Study population
The population of the current study was derived from the 2011-2016 NHANES. The protocol of NHANES study was described previously [23-25]. Briefly, NHANES employs a complex, multistage probability sampling strategy among the civilian, noninstitutionalized U.S. population to investigate a nationally representative sample. Starting in 2011, a sample design was implemented in NHANES to oversample non-Hispanic Asians (NHA), in addition to the ongoing oversample of Hispanics, non-Hispanic blacks, older adults, and low-income whites/others. All participants completed household surveys conducted by trained study staff, which include questions about demographics and health history. The study protocol also includes standardized medical examinations, collection of a blood sample, and other in-person testing at mobile examination centers. Informed consent was obtained from all NHANES participants.
During 2011-2012, 2013-2014 and 2015-2016 NHANES cycles, 29, 902 participants were investigated. For the present study we included participants (n=16, 513) ≥ 20 years of age, both males and females, and all racial and ethnic groups, except those categorized as “other” (i.e., Pacific Islanders, Native Americans/Alaskan Natives, and multiracial individuals). The “other” race group was excluded because of its small sample size and the heterogeneous nature of the group. Furthermore, we excluded participants with missing blood pressure levels (n=1, 319) and data of covariates (n=1, 037), including sex, education, annual household income, serum cotinine level and alcohol consumption. The associations of metals levels in blood and urine with blood pressure levels and hypertension were estimated separately. Thus, participants without data of blood Pb, Cd and Hg levels were excluded, which resulted in 7, 913 participants available for analyses based on blood metals (Figure 1). NHANES 2011-2016 examined a one-third sample of the study population of urinary As, Pb, Cd and Hg levels, leaving 3, 954 participants eligible for analyses based on urinary metals (Figure 1).
Exposure assessment
Whole blood Pb, Cd, total Hg levels were examined at the Environmental Health Sciences Laboratory of the Center for Disease Control and Prevention (CDC) National Center for Environmental Health (NCEH), using inductively coupled plasma mass spectrometry (ICP-MS). The limit of detection (LOD) was 0.25 µg/dL for Pb, 0.16 µg/L for Cd, and 0.16 µg/L for total Hg in NHANES 2011-2012. In NHANES 2013-2016, the LOD values were 0.07 µg/dL for Pb, 0.10 µg/L for Cd and 0.28 µg/L for total Hg. The detection rates of blood metals for participants included were as follow: blood Pb (99.63%), blood Cd (90.53%) and blood Hg (92.01%). In addition, Hg species levels in blood, including inorganic Hg, ethyl Hg and MeHg, are measured using a triple spike isotope dilution method which employs gas chromatography to separate the species followed by introduction into an ICP-MS for detection. The LOD values for inorganic Hg, ethyl Hg and MeHg were 0.27 µg/L, 0.16 µg/L and 0.12 µg/L respectively in these three NHANES cycles. The percentage of study participants with these Hg species levels over LOD was 25.7% for inorganic Hg, 2.3% for ethyl Hg and 87.8% for MeHg. Therefore, only MeHg was considered in final analyses.
Urinary total As, Pb, Cd and Hg levels were also examined using ICP-MS. The LOD was 1.25 µg/L for As, 0.0800 µg/L for Pb, 0.0560µg/L for Cd and 0.05 ng/ml for Hg in NHANES 2011-2012. In NHANES 2013-2016, the LOD for these metals were as follow: As, 0.26 µg/L; Pb, 0.036 µg/L, Cd, 0.030 µg/L; Hg, 0.13 ng/ml. The detection rates were 91.79% for Cd, 98.84% for As, 98.28% for Pb, and 73.19% for Hg among participants included. As species levels in urine, including arsenous acid, arsenic acid, arsenobetaine, arsenocholine, DMA and monomethylarsonic acid, are determined by using high performance liquid chromatography to separate the species coupled to an ICP-MS to detect the As species. The LOD values of As species were 0.48 µg/L for arsenous acid, 0.87 µg/L for arsenic acid, 1.19 µg/L for arsenobetaine, 0.28 µg/L for arsenocholine, 1.8 µg/L for DMA, 0.89 µg/L for monomethylarsonic acid in NHANES 2011-2012. In NHANES 2013-2016, the LOD for these As species were as follow: arsenous acid, 0.12 µg/L; arsenic acid, 0.79 µg/L; arsenobetaine, 1.16 µg/L; arsenocholine, 0.11 µg/L; DMA, 1.91 µg/L; monomethylarsonic acid, 0.20 µg/L; The percentage of study participants with arsenous acid, arsenic acid, arsenobetaine, arsenocholine, DMA and monomethylarsonic acid levels over LOD values was 50.2%, 2.2%, 49.3%, 13.9%, 74.8% and 51.8% respectively. Finally, DMA was included in current study due to low detection rate for other As species. Furthermore, urinary metal concentrations were corrected using the concentration of urinary creatinine concentration to account for the effect of urinary dilution.
For samples with metals levels below LOD, NHANES use “fill values” (LOD divided by the square root of 2). Detailed information about laboratory procedures have been described previously, including sample collection, storing and handling of specimens, quality control, and instrument and equipment used for the chemical analyses [26-34].
Blood pressure and hypertension
The blood pressure was measured consecutively three times after resting quietly in a seated position for 5 minutes. If a blood pressure measurement is interrupted or incomplete, a fourth attempt may be made. Mean SBP and DBP levels were computed discarding the first reading, except when only reading was eligible. Hypertension was defined as a mean SBP ≥ 130 mmHg, or a mean DBP ≥ 80 mmHg, or a self-reported antihypertension medication use currently, according to the 2017 ACC/AHA Guideline for High Blood Pressure in adults [35].
Covariates
Variables including age, sex, race/ethnicity, education, household income, body mass index (BMI), alcohol consumption and smoking (based on the serum cotinine concentration) were considered as potential confounders for the associations of metals levels with blood pressure and hypertension. Age was categorized into ≥20 to ≤39 years, 40 to 59 years and over 60 years. Race/ethnicity was self-reported as non-Hispanic white (NHA), non-Hispanic black (NHB), Mexican American (MA), other Hispanic (OH), non-Hispanic Asian (NHA). Education was classified as < high school, high school graduate/general education development, some college/associate in art degree and ≥ college graduate. Household income was grouped into < $20,000, $20,000 – < $55,000, $55,000 – < $75,000 and ≥ $75,000. Serum cotinine level was ln-transformed due to skew distribution. Alcohol consumption was classified as never drinker, ever drinker and current drinker. BMI was calculated as participant’s weight in kilograms divided by the square of the participant’s height in meters (kg/m2). Previous study have demonstrated that fish was the major contributor to dietary Hg and As intake [12]. Omega-3 fatty acids may negatively confound or modify the association of As and Hg with hypertension because these fatty acids are derived from fish consumption and are known to have cardio-protective properties [12, 36]. The omega-3 fatty acid intake data was from two 24-hour recall and calculated as the sum of eicosapentaenoic acid (EPA; 20:5 n-3) and docosahexaenoic acid (DHA; 22:6 n-3). The omega-3 fatty acid data was then categorized into four groups according to quartile values which were determined based on the whole study sample.
Statistical analysis
Demographic characteristics, lifestyle factors, blood pressure and hypertension prevalence were described across racial/ethnic groups. Geometric means (GM) and their confidence intervals of metals concentrations in urine and blood were also described among racial/ethnic categories. Metals levels in urine and blood were categorized into 3 groups for analyses according to the tertile cutoff values which were based on weighted distribution in the whole study sample.
To explore the associations of metals exposure and blood pressure and prevalence of hypertension among NHA, we categorized racial/ethnic groups into other racial/ethnic groups (including NHW, NHB, MA and OH; hereafter these groups simply referred to non-Asian American or non-NHA) and Asian American, due to concentrations of As, Pb, Cd and Hg either in urine or blood in Asian American higher than those in non-Asian American. To account for the influence of antihypertensive medications on blood pressure, the censored normal regression model was employed to analysis the association of metals levels in blood or urine with SBP and DBP levels [37]. The relationship between metal levels in urine or blood and prevalence of hypertension were also explored using multivariable logistic regression model to estimate odds ratio (OR) and confidence interval (CI). All models were adjusted for age, gender, education, annual household income, serum cotinine level, alcohol consumption and BMI. For Hg, MeHg, As and DMA, omega-3 fatty acid intake was adjusted additionally. The dose-response trend of p value was calculated by using the median values in each tertile of metal level as continuous variables.
Since the NHANES study was performed with a complex survey design, all the statistical analyses accounted for the sampling weight, clusters and strata. All statistical analyses were used SAS version 9.4 (SAS Institute, Cary, NC), except for the associations of metals levels and blood pressure levels using the command of “cnreg” of Stata 13.0 (STATA Corp, College Station, Texas, USA). All the statistical analyses were two tailed, and the p values < 0.05 were considered statistically significant.