Research Article Volume 122 | Issue 10 | October 2014
Environ Health Perspect; DOI:10.1289/ehp.1307756
Associations between Arsenic Species in Exfoliated Urothelial Cells and Prevalence of Diabetes among Residents of Chihuahua, Mexico
Jenna M. Currier,1 María C. Ishida,2 Carmen González-Horta,2 Blanca Sánchez-Ramírez,2 Lourdes Ballinas-Casarrubias,2 Daniela S. Gutiérrez-Torres,2 Roberto Hernández Cerón,3 Damián Viniegra Morales,3 Francisco A. Baeza Terrazas,3 Luz M. Del Razo,4 Gonzalo G. García-Vargas,5 R. Jesse Saunders,6 Zuzana Drobná,6 Rebecca C. Fry,7 Tomáš Matoušek,8 John B. Buse,9 Michelle A. Mendez,6,10,11 Dana Loomis,12 and Miroslav Stýblo1,6
Background: A growing number of studies link chronic exposure to inorganic arsenic (iAs) with the risk of diabetes. Many of these studies assessed iAs exposure by measuring arsenic (As) species in urine. However, this approach has been criticized because of uncertainties associated with renal function and urine dilution in diabetic individuals.
Objectives: Our goal was to examine associations between the prevalence of diabetes and concentrations of As species in exfoliated urothelial cells (EUC) as an alternative to the measures of As in urine.
Methods: We measured concentrations of trivalent and pentavalent iAs methyl-As (MAs) and dimethyl-As (DMAs) species in EUC from 374 residents of Chihuahua, Mexico, who were exposed to iAs in drinking water. We used fasting plasma glucose, glucose tolerance tests, and self-reported diabetes diagnoses or medication to identify diabetic participants. Associations between As species in EUC and diabetes were estimated using logistic and linear regression, adjusting for age, sex, and body mass index.
Results: Interquartile-range increases in trivalent, but not pentavalent, As species in EUC were positively and significantly associated with diabetes, with ORs of 1.57 (95% CI: 1.19, 2.07) for iAsIII, 1.63 (1.24, 2.15) for MAsIII, and 1.31 (0.96, 1.84) for DMAsIII. DMAs/MAs and DMAs/iAs ratios were negatively associated with diabetes (OR = 0.62; 95% CI: 0.47, 0.83 and OR = 0.72; 95% CI: 0.55, 0.96, respectively).
Conclusions: Our data suggest that uncertainties associated with measures of As species in urine may be avoided by using As species in EUC as markers of iAs exposure and metabolism. Our results provide additional support to previous findings suggesting that trivalent As species may be responsible for associations between diabetes and chronic iAs exposure.
Citation: Currier JM, Ishida MC, González-Horta C, Sánchez-Ramírez B, Ballinas-Casarrubias L, Gutiérrez-Torres DS, Hernández Cerón R, Viniegra Morales D, Baeza Terrazas FA, Del Razo LM, García-Vargas GG, Saunders RJ, Drobná Z, Fry RC, Matoušek T, Buse JB, Mendez MA, Loomis D, Stýblo M. 2014. Associations between arsenic species in exfoliated urothelial cells and prevalence of diabetes among residents of Chihuahua, Mexico. Environ Health Perspect 122:1088–1094; http://dx.doi.org/10.1289/ehp.1307756
Address correspondence to M. Stýblo, Department of Nutrition, CB# 7461, 135 Dauer Dr., Room 2302, University of North Carolina at Chapel Hill, Chapel Hill, NC 27599-7461 USA. Telephone: (919) 966-5721. E-mail: firstname.lastname@example.org
This work was funded by the National Institutes of Health (grants R01ES015326 and 3R01ES015326-03S1 to M.S.). Support was also provided by the UNC Nutrition Obesity Research Center (grant DK056350) and the Center for Environmental Health and Susceptibility (grant P30ES010126) and also by the Ministry of Education, Youth and Sports of the Czech Republic (project no. LH12040) and the Academy of Sciences of the Czech Republic institutional fund RVO (68081715 to T.M.).
The authors declare they have no actual or potential competing financial interests.
Received: 18 October 2013
Accepted: 26 June 2014
Advance Publication: 27 June 2014
Final Publication: 1 October 2014
- Supplemental Material (1.1 MB) PDF
Arsenic (As), and specifically its inorganic forms (iAs) [arsenite (iAsIII) and arsenate (iAsV)], are naturally occurring drinking-water contaminants. Epidemiologic evidence (James et al. 2013; Kuo et al. 2013; Maull et al. 2012; Pan et al. 2013; Wang et al. 2014), including a prospective study (Kim et al. 2013), has linked chronic iAs exposure with the risk of diabetes mellitus. Several mechanisms by which iAs exposure can disrupt glucose homeostasis have been proposed (Maull et al. 2012). Trivalent iAsIII and the trivalent methylated arsenicals that are produced in the course of iAs metabolism—methylarsonite (MAsIII) and dimethylarsinite (DMAsIII)—play key roles in these mechanisms (Douillet et al. 2013; Fu et al. 2010; Paul et al. 2007, 2008). However, assessing the association between these arsenicals and risk of diabetes in population studies has been a major challenge. This is because iAsIII—and particularly MAsIII and DMAsIII—are unstable in human urine, which has been traditionally used in assessing iAs exposure and metabolism (Del Razo et al. 2011; Gong et al. 2001). An additional challenge is associated with quantification of iAs metabolites in urine, specifically with using urinary creatinine as a factor to adjust for variation in urine dilution. Urinary creatinine concentration is influenced by various factors, including age, sex, health status, ethnicity, body mass index (BMI), fat-free mass, and time of collection (Barr et al. 2005; Boeniger et al. 1993; Mahalingaiah et al. 2008). In addition, adjusting for creatinine may be inappropriate for individuals with compromised renal function, including people with diabetes (Jerums et al. 2010). More importantly, iAs exposure may lead to an increased excretion of creatinine (Nermell et al. 2008). Thus, the analysis of iAs metabolites in body fluids other than urine, such as in cells or tissues, may provide a better measure of iAs exposure.
We have previously demonstrated the feasibility of As analysis in human cells, including exfoliated urothelial cells (EUC). In 2008, we used hydride generation (HG)–cryotrapping (CT)–atomic absorption spectrometry (AAS) to measure concentrations of total iAs (iAsIII + V), MAs (MAsIII + V), and DMAs (DMAsIII + V) in EUC isolated from the urine of residents of the Zimapan region in Mexico (Hernández-Zavala et al. 2008b). Because of small sample sizes, we could not perform the oxidation state-specific analysis to distinguish between AsIII and AsV species. However, we were able to detect and quantify both AsIII and AsV species in cultured human urothelial cells treated in vitro with iAs. We have shown that both MAsIII and DMAsIII are stable in these cells when stored at –80°C (Currier et al. 2011a, 2011b). To increase the feasibility of the analysis of MAsIII and DMAsIII in the small numbers of EUC that are typically available from a spot urine sample, we have recently replaced AAS in the HG-CT-AAS system with inductively coupled plasma–mass spectrometry (ICP-MS). The newly developed HG-CT-ICP-MS was reported to be suitable for the oxidation state-specific analysis of As in EUC, providing superior detection limits and high reproducibility (Matoušek et al. 2013).
The goal of the present study was to determine concentrations of AsIII and AsV species in EUC from individuals exposed to iAs in drinking water and to examine the association between As species in EUC and the prevalence of diabetes.
Materials and Methods
The Chihuahua cohort. All procedures involving human subjects were approved by institutional review boards at the University of North Carolina at Chapel Hill (UNC) and Cinvestav-IPN (Centro de Investigación y de Estudios Avanzados del Instituto Politécnico Nacional, Mexico City, Mexico). Individuals participating in the present study were among 1,163 men and women recruited for the Chihuahua cohort (Mexico); all study participants provided informed consent. This cohort was established between 2008 and 2013 to study chronic diseases associated with iAs exposure in drinking water. Only adults (≥ 18 years of age) with ≥ 5 years of uninterrupted residency in the study area were recruited. Pregnant women and participants who reported kidney or urinary tract infection were excluded because these conditions could affect the urinary pattern of iAs metabolites. Individuals with a potential for occupational exposure to As were also excluded. Data on residency, occupation, drinking-water sources and consumption, smoking, use of alcohol, drugs, or medication, and medical history were gathered at the time of enrollment using a questionnaire. Specific questions were asked about previous diagnosis of diabetes and the use of antidiabetic drugs. Samples of household tap water were collected for As analysis. The participants were then transported to Universidad Autónoma de Chihuahua to undergo a medical examination. Body weight and height were recorded and used to calculate BMI. A single spot urine sample was collected in sterile plastic cups and placed immediately on ice. Aliquots of urine samples were frozen and stored at –80°C for speciation analysis of As; the rest was used for EUC isolation. A single sample of fasting venous blood was drawn, followed by a standard oral glucose tolerance test (OGTT) in which a sample of venous blood was drawn 2 hr after an oral load of 75 g glucose. All blood samples were placed on ice immediately after collection. Plasma was isolated from the fasting and 2-hr blood by centrifugation at 4°C and frozen at –80°C.
Isolation of EUC. EUC were isolated from individuals recruited between March 2011 and August 2012. A total of 466 individuals underwent medical examination during this period; 428 provided urine for EUC isolation. EUCs were isolated from freshly collected urine (100 mL/participant) by centrifugation at 4°C. The cell pellet was washed with ice-cold phosphate-buffered saline (PBS) and again centrifuged. Cells were then resuspended in PBS, counted, and checked for the presence of bacteria, yeast, and red or white blood cells using a microscope. Only EUC free of microbial contamination and with < 5% of the total cell count represented by red or white blood cells (from a total of 374 participants) were used in the present study. All cells other than bacteria, yeast, and red or white blood cells were assumed, but not confirmed, to be EUC. EUC were stored at –80°C and shipped along with the urine samples on dry ice to UNC once per month for As speciation analysis.
Diagnosis of diabetes. Glucose levels in fasting and 2-hr plasma samples were measured using a Prestige 24i Chemistry Analyzer (Tokyo Boeki). The analyzer was calibrated before analysis, and reference human sera with normal and elevated glucose levels (Serodos and Serodos PLUS; Human Diagnostics Worldwide) were used for quality control. Study participants with fasting plasma glucose (FPG) ≥ 126 mg/dL or 2-hr plasma glucose (2HPG) ≥ 200 mg/dL, or with a self-reported doctor’s diagnosis or self-reported use of antidiabetic medication were classified as diabetic.
Analyses of As in household water and urine. Concentrations of As in acid-digested water samples were determined at Cinvestav-IPN using HG-CT-AAS (Del Razo et al. 2011). Urine samples were analyzed at UNC after storage at –80°C for up to approximately 1 month, which is known to result in oxidation of MAsIII and DMAsIII (Del Razo et al. 2011). Thus, only analysis of total iAs (iAsIII + V), MAs (MAsIII + V), and DMAs (DMAsIII + V) was performed using HG-CT-AAS (Hernández-Zavala et al. 2008a). A certified standard reference material (SRM), Arsenic Species in Frozen Human Urine (SRM 2669; National Institute of Standards and Technology) was used with every shipment to assure accuracy. The concentrations of As species measured by HG-CT-AAS in SRM 2669 ranged from 86.7% to 106.4% of the certified values: 90.3–106.4% for iAs, 86.7–96.4% for MAs, and 88.2–99.0% for DMAs. The limits of detection (LODs) using 200 μL urine per sample were 0.05 ng As/mL for MAs or DMAs and 0.1 ng As/mL for iAs. The creatinine concentration in urine was determined by a colorimetric assay (Cayman Chemical Company); specific gravity was measured using a digital Atago PAL refractometer (Atago USA). It should be noted that the HG-CT-AAS cannot detect organic As species commonly found in seafood (e.g., arsenobetaine), and thus accounts for As species associated mainly with iAs exposure.
Analyses of As species in EUCs. AsIII and AsV species in EUCs were analyzed at UNC using HG-CT-ICP-MS (Matoušek et al. 2013). Briefly, cell pellets were lysed in ice-cold deionized water. The trivalent species (AsIII, MAsIII, and DMAsIII) were measured in an aliquot of cell lysate directly, without pretreatment. Another aliquot was treated with 2% cysteine and analyzed for total iAs (iAsIII + V), MAs (MAsIII + V), and DMAs (DMAsIII + V). The concentrations of iAsV, MAsV, and DMAsV were determined as a difference between AsIII + V values obtained for cysteine-treated aliquots and AsIII values from untreated sample aliquots. For AsIII species concentrations below LOD, the values of LOD divided by the square root of 2 were used when calculating the corresponding AsV values. Calibration curves were generated using cysteine-treated pentavalent As standards (at least 98% pure) as previously described (Hernández-Zavala et al. 2008a). The instrumental LODs for As species analyzed by HG-CT-ICP-MS ranged from 0.04 to 2.0 pg As. The analyses of As species in EUC were performed by a researcher who was unaware of the diabetes status of the individual study participant or of the As concentrations in the corresponding urine and water samples.
Statistical analysis. Continuous variables were described using means and SDs or medians and interquartile ranges (IQRs; for nonnormally distributed variables). Categorical variables were described using frequencies. For As species concentrations below LOD, the values of LOD divided by the square root of 2 were used for statistical analysis, including regression and descriptive analyses and to determine IQRs. The statistical significance of differences in characteristics of study participants with versus without diabetes was assessed using Student’s t-tests or one-way analyses of variance (ANOVA). Associations between As species in EUC and urine were estimated using linear regression models with log-transformed (log10) variables as well as with Spearman correlations. Associations of diabetes with concentrations of As species in EUC and urine were estimated using logistic regression to estimate odds ratios (ORs) and 95% confidence intervals (CIs). To control for potential confounding, sex (as a categorical variable) and age and BMI (as continuous variables) were included a priori as covariates. We also used linear regression models adjusted for age, sex, and BMI to estimate associations of log10-transformed FPG and 2HPG concentrations with concentrations of iAs metabolites and the sum of speciated As in urine. Age, sex, and BMI were included as covariates in these models. The linearity of the associations between As species and FPG/2HPG was assessed graphically and by linear regression using log10-transformed values. Slopes were significantly nonzero for all As species except pentavalent species in EUC. Unless otherwise specified, ORs, regression coefficients, and CIs are reported for a 1-IQR increment of exposure to facilitate comparison because of the different concentration ranges of As in EUCs and urine. Analyses of urinary metabolites of iAs were conducted both with and without urinary creatinine concentration or specific gravity adjustment. All statistical analyses were performed in Epi Info 7, version 1.0.6 (Centers for Disease Control and Prevention) and graphical representations were generated using GraphPad Instat software package (GraphPad Software Inc.). Statistical significance was considered at the level of p < 0.05.
Basic characteristics of the study population. The EUC samples free of microbial contamination and containing < 5% of red or white blood cells were obtained from a total of 374 participants (252 women and 122 men). More than 17% of these participants (17.5% of women and 18% of men) were classified as diabetic (Table 1) based on the FPG or 2HPG value or on their self-reported diabetes diagnosis or medication. Eleven participants who reported a previous diabetes diagnosis and/or taking antidiabetic medication (25.5% of those classified as diabetic) had FPG and 2HPG values in the normal or prediabetic range (i.e., FPG < 126 and 2HPG < 200 mg glucose/dL). Approximately 29% of the participants were overweight and 41% were obese. The average age and BMI were significantly higher among diabetic compared with nondiabetic individuals. No statistically significant differences between diabetic and nondiabetic individuals were found in the average EUC count, As concentration in drinking water, or sum of As species in urine (expressed either as nanograms of As per milliliter or nanograms of As per milligram creatinine). The average specific gravity of urine from diabetic individuals was significantly higher than in nondiabetic individuals, but the difference between the two groups in the sum of As species in urine adjusted for specific gravity was not statistically significant. The average sum of As species was higher in EUC from nondiabetic compared with diabetic participants; again, this difference was not statistically significant. Notably, basic characteristics of participants included in the present study and those of the entire Chihuahua cohort were very similar; however, the average age of the cohort was somewhat lower (see Supplemental Material, Table S1).
Arsenic species in EUC and urine. The speciation analysis of As was performed in all 374 samples of EUC and in the corresponding urine samples (Table 2). Concentrations of all AsIII and AsV species were above LOD in 94% of EUC samples. In urine, concentrations of iAs and MAs were below LOD in 15 (4%) and 2 (0.5%) samples, respectively. DMAs was detected and quantified in all urine samples. There were marked differences in As speciation profiles in EUC and in urine (Figure 1). The ratios of DMAs/MAs and MAs/iAs were lower in EUC compared with urine. In urine, total DMAs (i.e., DMAsIII + V) was the predominant species, accounting on average for 76% of all As species, with only 9% and 15% represented by iAs and MAs, respectively. In contrast, iAsIII and iAsV were the major As species in EUC, representing on average 37% and 29% of speciated As. DMAs accounted for approximately 22% (2.4% for DMAsIII and 19.2% for DMAsV) and MAs for approximately 14% (MAsIII for 7.9% and MAsV for 5.6%) of speciated As in EUC. In spite of the differences in As speciation profiles, statistically significant positive associations were found between the concentrations of individual As species in urine (not adjusted for creatinine) and EUC (see Supplemental Material, Figure S1). Notably, adjusting for creatinine had little or no effect on these associations (see Supplemental Material, Table S2).
EUC counts and As speciation in EUC and urine according to sex. We found statistically significant differences in the numbers of EUC obtained from males and females. Cell counts in urine from males ranged from 450 to 2,128,000 cells/100 mL, compared with 1,800 to 9,717,000 cells/100 mL in samples from females. The mean EUC count (± SE) was 10 times higher in urine from women compared with men (529,258 ± 52,218/100 mL vs. 53,328 ± 18,782/100 mL). On average, EUC from females contained significantly less total speciated As ± SD than EUC from males: 40 ± 163 pg/10,000 cells versus 309 ± 542 pg/10,000 cells (see Supplemental Material, Figure S2B). For both males and females, statistically significant negative associations were found between the cell count and the concentration of total speciated As in EUC (see Supplemental Material, Figure S2). This association was stronger for males than females: β = –0.70 (95% CI: –0.82, –0.58; r2 = 0.54) versus β = –0.35 (95% CI: –0.46, –0.23; r2 = 0.12). Sex-related differences were also found in the composition of As species in both EUC and urine (Figure 2). iAsIII and MAsIII represented on average 43% and 10% of total speciated As in EUC from females, but only 18% and 4% in EUC from males (Figure 2A). On the other hand, the pentavalent As species—iAsV, MAsV, and DMAsV—accounted for greater proportions of As in EUC from males. Taken together, iAs species (iAsIII and iAsV) represented a smaller portion and DMAs species (DMAsIII and DMAsV) a greater portion of total speciated As in EUC from males compared with EUC from females. On average, males excreted significantly more As in urine as MAsIII + V (17%) than did females (14%), but the percentage of DMAsIII + V was smaller (73% vs. 78%) (Figure 2B). The DMAs/MAs ratio was smaller in male compared with female urines: 4.7 ± 1.84 versus 7.0 ± 6.16 (p < 0.0001).
Figure 2 – Differences in the composition of As species in EUC (A) and urine (B) collected from male and female study participants. Data shown are mean + SD (n = 252 for women; n = 122 for men).
*p < 0.05 based on one-way ANOVA with Bonferroni’s posttest.
Associations of diabetes with As species in EUC and urine: logistic regression analysis. The logistic regression analysis was performed using two models. Model 1 included all diabetic individuals as classified by FPG, 2HPG, or self-reported diagnosis or medication (n = 66). For model 2, only individuals with FPG ≥ 126 mg/dL or 2HPG ≥ 200 mg/dL were considered diabetic (n = 55); 11 individuals who reported diabetes diagnosis or medication but had both FPG < 126 mg/dL and 2HPG < 200 mg/dL were excluded. Both models were adjusted for age, sex, and BMI. Using either model, we found diabetes to be significantly associated with iAsIII and MAsIII concentrations in EUC—more strongly in model 2, with ORs for each IQR of 1.75 (95% CI: 1.29, 2.39) and 2.02 (95% CI: 1.48, 2.77), respectively (Figure 3; see also Supplemental Material, Table S3 for numeric data). In both models diabetes was negatively associated with the ratios of DMAs/MAs and DMAs/iAs in EUCs. Here again, the associations were stronger in model 2: OR = 0.53 (95% CI: 0.38, 0.73) and OR = 0.65 (95% CI: 0.48, 0.89), respectively. Diabetes was also positively associated with DMAsIII and with sum of As species in EUC, but these associations were statistically significant only for model 2 (OR = 1.49, 95% CI: 1.04, 2.13 and OR = 1.41, 95% CI: 1.01, 1.97, respectively). Diabetes was also positively associated with total iAsIII + V and MAsIII + V. A marginally significant association was found with iAsV, but not with other AsV species. Notably, adjusting for cell count as a covariate in sensitivity analyses had no significant impact on the associations between As species in EUC and diabetes (data not shown). For example, ORs for model 2 were 1.81 (95% CI: 1.33, 2.48) for iAsIII, 1.93 (95% CI: 1.42, 2.62) for MAsIII, and 1.42 (95% CI: 1.02, 1.97) for DMAsIII, thus practically matching the values obtained without the adjustment (see above).
Figure 3 – Association of diabetes with As species in EUC. In model 1, diabetes was classified by either FPG ≥ 126 mg/dL, 2HPG ≥ 200 mg/dL, or self-report of doctor diagnosis or use of medication for treatment of diabetes; in model 2, diabetes was classified only by FPG ≥ 126 mg/dL or 2HPG ≥ 200 mg/dL. ORs (95% CIs) are standardized to an increment of 1 IQR and adjusted for age, sex, and BMI. IQRs for each As species and species ratio are shown in Table 2. See Supplemental Material, Table S3, for numeric data.
*p < 0.05.
In urine, total iAs, MAs, and DMAs and DMAs/MAs ratio were all positively associated with diabetes; however, these associations were statistically significant only for the DMAs/MAs ratio in model 1 (OR = 1.37, 95% CI: 1.03, 1.84) and total DMAs in model 2 (OR = 1.34, 95% CI: 1.02, 1.76) (Figure 4; see also Supplemental Material, Table S3 for numeric data). When adjusted for creatinine, total iAs, MAs, DMAs, and sum of As species in model 2 were all significantly associated with diabetes. In contrast, after adjusting for specific gravity all OR values were close to zero. Unlike creatinine, specific gravity itself was positively associated with diabetes: model 1, OR = 1.32 (95% CI: 1.01, 1.71); model 2, OR = 1.42 (95% CI: 1.07, 1.89).
Figure 4 – Association of diabetes with As species in urine, urine creatinine, and specific gravity. Arsenic species are either unadjusted (A) or adjusted for creatinine (B) or specific gravity (C). In model 1, diabetes was classified by either FPG ≥ 126 mg/dL, 2HPG ≥ 200 mg/dL, or self-report of doctor diagnosis or use of medication for treatment of diabetes; in model 2, diabetes was classified only by FPG ≥ 126 mg/dL or 2HPG ≥ 200 mg/dL. ORs (95% CIs) are standardized to an increment of 1 IQR and adjusted for age, sex, and BMI. IQRs for each As species and species ratio are indicated in Table 2. See Supplemental Material, Table S3, for numeric data.
*p < 0.05.
Associations of diabetes with As species in EUC and urine: linear regression analysis. Linear regression analysis using logarithmically (log10) transformed FPG and 2HPG values was performed to further characterize associations between diabetes and As species in EUC and urine (Table 3). Both FPG and 2HPG were positively associated with the trivalent As species (iAsIII, MAsIII, DMAsIII) and with the sum of AsIII + V species in EUC (p < 0.01), but not significantly associated with the pentavalent As species in EUC. The ratios of DMAs/MAs and DMAs/iAs in EUCs were negatively associated with FPG and 2HPG (p ≤ 0.04). Statistically significant (p = 0.04) and marginally significant (p = 0.08) positive associations were found between the MAs/iAs ratio and FPG and 2HPG, respectively. FPG and 2HPG also were significantly associated with each of the AsIII + V species in urine, regardless of adjustment for creatinine or specific gravity. Here again, specific gravity, but not creatinine, was positively associated with both FPG and 2HPG concentrations (p < 0.01). Both FPG and 2HPG were also positively associated with the urinary DMAs/MAs ratio.
The evidence linking chronic iAs exposure to diabetes was reviewed by a 2011 National Toxicology Program (NTP) workshop. This review concluded that existing data provide limited to sufficient support for an association of diabetes with high iAs exposures in drinking water (Maull et al. 2012). The workshop also discussed methods accounting for urine dilution when urinary As is used as an indicator of iAs exposure. Because of uncertainties associated with effects of iAs exposure or disease on urinary creatinine levels, the workshop review recommended that both raw and adjusted values should be reported (Maull et al. 2012). We followed this recommendation in the present study. We found all AsIII + V species in urine to be positively associated with diabetes classified by FPG or 2HPG. When adjusting for creatinine, these associations were statistically significant in model 2; without the adjustment, significant association was found only with urinary DMAsIII + V (Figure 4; see also Supplemental Material, Table S3). Because of the uncertainty associated with urinary creatinine, adjusting for specific gravity has been recommended as an alternative method (Nermell et al. 2008). However, adjusting for specific gravity may bias associations with diabetes because urine of diabetic individuals, compared with healthy subjects, contains higher levels of albumin and glucose, resulting in higher specific gravity (Chadha et al. 2001; Voinescu et al. 2002). Indeed, we found a statistically significant positive association between diabetes and specific gravity and no associations between diabetes and urinary As species after adjusting for specific gravity.
The main goal of the present study was to examine associations between prevalent diabetes and As species in EUC as an alternative marker of iAs exposure and metabolism. Because cells provide a reducing environment, the toxic trivalent arsenicals are relatively stable even in samples stored for weeks (Currier et al. 2011a, 2011b). Our results show that As species profiles in EUC do not reflect those in urine. Specifically, iAs species are the major species in EUC but represent only a small percentage of As found in urine, whereas DMAs (i.e., DMAsIII + V) is the major urinary metabolite. High iAs levels in EUC could be explained by formation of iAs-containing intracytoplasmic and intramitochondrial inclusions. These inclusions have recently been found in EUC from leukemia patients treated with arsenic trioxide (Wedel et al. 2013) and in bladder epithelium of mice exposed to iAs in drinking water (Dodmane et al. 2014). We also found that the concentrations and proportions of As species in EUC significantly differ between men and women. EUC from male donors contained approximately 10-fold more total speciated As than EUC from female donors; however, iAsIII and MAsIII accounted for smaller fractions of As in male compared with female EUC. These differences can probably be explained by different cell counts and cell types present in urine from males and females. The vesical trigone area of an adult female bladder is particularly susceptible to squamous metaplasia (Fortin et al. 2010; Tyler 1962), a noncancerous change in the epithelial lining that is ultimately responsible for greater numbers of cells in urine from females. Urine from females may also contain vaginal epithelial cells. However, the routine microscopy used in our study to examine EUC suspensions cannot reliably distinguish between epithelial cells of urothelial or squamous origin. Because of the relatively small numbers of cells collected from spot urines, we could not apply more sophisticated techniques (e.g., immunocytochemistry) to characterize the types and origin of EUC. Thus, for the purpose of this study we defined all cells isolated from the bacteria- and yeast-free urine containing < 5% of red or white blood cells as EUC.
We have previously reported that trivalent As species, particularly MAsIII and DMAsIII, inhibit insulin-dependent glucose uptake by adipocytes (Paul et al. 2007) and glucose stimulated insulin secretion by isolated pancreatic islets (Douillet et al. 2013). Our recent study in the Zimapan and Lagunera regions of Mexico (Del Razo et al. 2011) indicated an association between the prevalence of diabetes and DMAsIII concentration in urine. In the present study, we found positive associations of diabetes with iAsIII, MAsIII, and DMAsIII concentrations in EUC, thus providing additional evidence that trivalent metabolites of iAs play important roles in the diabetogenic effects of iAs exposure. Notably, DMAs/MAs and DMAs/iAs ratios in EUC were inversely associated with diabetes. Although never before measured in EUC, the ratios of As species in urine have often been used in population studies to evaluate the body capacity to methylate iAs. Low DMAs/MAs and high MAs/iAs ratios in urine, as possible indicators of low methylation capacity, have been linked to increased risks of cancer and cardiovascular disease in populations chronically exposed to iAs exposure (Tseng 2007). In contrast, our study in Zimapan and Lagunera (Del Razo et al. 2011) and the present study show that in the case of diabetes, a high DMAs/MAs ratio in urine may be a risk factor.
Our findings provide additional evidence for the association between diabetes and chronic exposure to iAs and for the role of the trivalent metabolites of iAs in the diabetogenic effects of this exposure. We also show that the speciation analysis of As in EUC—which facilitates assessment of trivalent species and avoids the need for dilution adjustments—can be used as an alternative to analysis of urinary As species. It should be noted, however, that in this study, the results obtained using the measures of AsIII species in EUC were consistent with the results using measures of AsIII + V species in urine after adjusting for creatinine. The associations between diabetes and As species in both EUC and urine were stronger when diabetes was classified only by FPG ≥ 126 or 2HPG ≥ 200 mg/dL, disregarding self-reported diagnosis or medication. This is consistent with a recent report from an American Indian cohort (Gribble et al. 2012) where an association between iAs exposure and diabetes was observed only among participants with poor diabetes control as indicated by elevated levels of glycated hemoglobin. Thus, using clinical indicators as compared with existing diabetes diagnosis may be required to better characterize the association of iAs exposure with prevalent or incident diabetes. The cross-sectional design, which cannot provide information on causality of the observed associations, and a modest sample size are the main limitations of the present study. Prospective studies in larger populations exposed to iAs, including the Chihuahua cohort, are needed to determine whether trivalent As species in EUC can be used to identify individuals or subpopulations who are at risk of developing diabetes as a result of chronic exposure to iAs.
Barr DB, Wilder LC, Caudill SP, Gonzalez AJ, Needham LL, Pirkle JL. 2005. Urinary creatinine concentrations in the U.S. population: implications for urinary biologic monitoring measurements. Environ Health Perspect 113:192–200; doi: 10.1289/ehp.7337.
Currier JM, Svoboda M, de Moraes DP, Matoušek T, Dědina J, Stýblo M. 2011a. Direct analysis of methylated trivalent arsenicals in mouse liver by hydride generation-cryotrapping-atomic absorption spectrometry. Chem Res Toxicol 24:478–480.
Del Razo M, García-Vargas GG, Valenzuela OL, Hernandez-Castellanos E, Sánchez-Peňa LC, Drobná Z, et al. 2011. Exposure to arsenic in drinking water is associated with increased prevalence of diabetes: a cross-sectional study in the Zimapan and Lagunera regions in Mexico. Environ Health 10:73; doi: 10.1186/1476-069X-10-73.
Dodmane PR, Arnold LL, Muirhead DE, Suzuki S, Yokohira M, Pennington KL, et al. 2014. Characterization of intracellular inclusions in the urothelium of mice exposed to inorganic arsenic. Toxicol Sci 137:36–46.
Douillet C, Currier J, Saunders RJ, Bodnar WM, Matoušek T, Stýblo M. 2013. Methylated trivalent arsenicals are potent inhibitors of glucose stimulated insulin secretion by murine pancreatic islets. Toxicol Appl Pharmacol 267:11–15.
Fu J, Woods CG, Yehuda-Shnaidman E, Zhang Q, Wong V, Collins S, et al. 2010. Low-level arsenic impairs glucose-stimulated insulin secretion in pancreatic beta cells: involvement of cellular adaptive response to oxidative stress. Environ Health Perspect 118:864–870; doi: 10.1289/ehp.0901608.
Hernández-Zavala A, Matoušek T, Drobna Z, Paul DS, Walton F, Adair BM, et al. 2008a. Speciation analysis of arsenic in biological matrices by automated hydride generation-cryotrapping-atomic absorption spectrometry with multiple microflame quartz tube atomizer (multiatomizer). J Anal At Spectrom 23:342–351.
Hernández-Zavala A, Valenzuela OL, Matoušek T, Drobna Z, Dědina J, Garcia-Vargas GG, et al. 2008b. Speciation of arsenic in exfoliated urinary bladder epithelial cells from individuals exposed to arsenic in drinking water. Environ Health Perspect 116:1656–1660; doi: 10.1289/ehp.11503.
James KA, Marshall JA, Hokanson JE, Meliker JR, Zerbe GO, Byers TE. 2013. A case-cohort study examining lifetime exposure to inorganic arsenic in drinking water and diabetes mellitus. Environ Res 123:33–38.
Mahalingaiah S, Meeker JD, Pearson KR, Calafat AM, Ye X, Petrozza J, et al. 2008. Temporal variability and predictors of urinary bisphenol A concentrations in men and women. Environ Health Perspect 116:173–178; doi: 10.1289/ehp.10605.
Matoušek T, Currier JM, Trojánková N, Saunders RJ, Ishida MC, González-Horta C, et al. 2013. Selective hydride generation- cryotrapping- ICP-MS for arsenic speciation analysis at picogram levels: analysis of river and sea water reference materials and human bladder epithelial cells. J Anal At Spectrom 28:1456–1465.
Maull EA, Ahsan H, Edwards J, Longnecker MP, Navas-Acien A, Pi J, et al. 2012. Evaluation of the association between arsenic and diabetes: a National Toxicology Program Workshop Review. Environ Health Perspect 120:1658–1670; doi: 10.1289/ehp.1104579.
Pan WC, Seow WJ, Kile ML, Hoffman EB, Quamruzzaman Q, Rahman M, et al. 2013. Association of low to moderate levels of arsenic exposure with risk of type 2 diabetes in Bangladesh. Am J Epidemiol 178:1563–1570.
Paul DS, Devesa V, Hernández-Zavala A, Adair BM, Walton FS, Drobna B, et al. 2008. Environmental arsenic as a disruptor of insulin signaling. In: Metal Ions in Biology and Medicine, Vol 10 (Collery PH, Maynard I, Theophanides T, Khassanova L, Callery T, Libbey J, eds). Paris:Eurotext, 1–7.
Paul DS, Harmon AW, Devesa V, Thomas DJ, Stýblo M. 2007. Molecular mechanisms of the diabetogenic effects of arsenic: inhibition of insulin signaling by arsenite and methylarsonous acid. Environ Health Perspect 115:734–742; doi: 10.1289/ehp.9867.
Wedel WR, Muirhead DE, Arnold LL, Dodmane PR, Lele SM, Maness-Harris L, et al. 2013. Urothelial cell intracytoplasmic inclusions after treatment of promyelocytic leukemia with arsenic trioxide. Toxicol Sci 134:271–275.
ISEE 2015 Abstracts Now AvailableEHP is pleased to present the abstracts for the 2015 annual conference of the International Society for Environmental Epidemiology (ISEE), “Addressing Environmental Health Inequalities,” being held 30 August–3 September 2015 in São Paulo, Brazil.
CEHN September 2015 Article of the Month“Relation of Prenatal Methylmercury Exposure from Environmental Sources to Childhood IQ” (DOI:10.1289/ehp.1408554) has been selected by the Children’s Environmental Health Network (CEHN) as its September 2015 Article of the Month. These CEHN summaries discuss the potential policy implications of current children’s environmental health research.
New Editor-in-ChiefWe are pleased to announce that Sally Perreault Darney has been selected as the new Editor-in-Chief of EHP. Sally comes to EHP from the U.S. Environmental Protection Agency, where she most recently co-led a large research project focused on assessing health disparities in vulnerable groups and providing healthy environments for children. Learn more about Sally and her vision for the journal in the September issue of EHP.
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Recent Advance Publications
Prenatal Ambient Air Pollution, Placental Mitochondrial DNA Content, and Birth Weight in the INMA (Spain) and ENVIRONAGE (Belgium) Birth Cohorts
Endocrine-Disrupting Chemicals and Oil and Natural Gas Operations: Potential Environmental Contamination and Recommendations to Assess Complex Environmental Mixtures
Bisphenol A, Bisphenol S, and 4-Hydroxyphenyl 4-Isoprooxyphenylsulfone (BPSIP) in Urine and Blood of Cashiers
Prenatal Phthalate Exposures and Childhood Fat Mass in a New York City Cohort
Effects of in Utero Exposure to Arsenic during the Second Half of Gestation on Reproductive End Points and Metabolic Parameters in Female CD-1 Mice