- Open Access
Prenatal exposure to heavy metal mixtures and anthropometric birth outcomes: a cross-sectional study
Environmental Health volume 21, Article number: 139 (2022)
Numerous studies have suggested significant associations between prenatal exposure to heavy metals and newborn anthropometric measures. However, little is known about the effect of various heavy metal mixtures at relatively low concentrations. Hence, this study aimed to investigate associations between prenatal exposures to a wide range of individual heavy metals and heavy metal mixtures with anthropometric measures of newborns.
We recruited 975 mother–term infant pairs from two major hospitals in Israel. Associations between eight heavy metals (arsenic, cadmium, chromium, mercury, nickel, lead, selenium, and thallium) detected in maternal urine samples on the day of delivery with weight, length, and head circumference at birth were estimated using linear and Bayesian kernel machine regression (BKMR) models.
Most heavy metals examined in our study were observed in lower concentrations than in other studies, except for selenium. In the linear as well as the BKMR models, birth weight and length were negatively associated with levels of chromium. Birth weight was found to be negatively associated with thallium and positively associated with nickel.
By using a large sample size and advanced statistical models, we could examine the association between prenatal exposure to metals in relatively low concentrations and anthropometric measures of newborns. Chromium was suggested to be the most influential metal in the mixture, and its associations with birth weight and length were found negative. Head circumference was neither associated with any of the metals, yet the levels of metals detected in our sample were relatively low. The suggested associations should be further investigated and could shed light on complex biochemical processes involved in intrauterine fetal development.
Heavy metals are naturally occurring elements with a high atomic weight and density at least five times greater than water. Some of these heavy metals are essential nutrients in the body, and a deficiency in one of them can result in diseases . On the other hand, over-consumption and exposure to high levels of heavy metals have been associated with adverse health outcomes [2,3,4]. Over-exposure of both mother and fetus to heavy metals during pregnancy has been associated with preterm birth and reduced birth size [6,7,8].
While the mechanisms underlying the effect of over-exposure to heavy metals on the development of newborns remain the subject of ongoing studies [9, 10], some heavy metals, including cadmium (Cd), mercury (Hg), lead (Pb), and selenium (Se), have been found to cross the placental barrier  and accumulate in the fetal blood circulation. The associations between prenatal exposure to these metals and adverse birth outcomes have been widely studied and raised possible associations with shorter birth length , low birth weight , and small head circumference . Prenatal exposure to other metals, such as arsenic (As), thallium (Tl), nickel (Ni), and chromium (Cr), has been less extensively studied but was also found to be associated with various adverse birth outcomes [15,16,17]. Prenatal assessment of heavy metal exposures during pregnancy is challenging and is usually conducted by analysis of maternal blood, assuming exposure traces found in it are highly correlated with human cord blood levels, as previously shown by Kot et al. (2021)  and Li et al. (2018) . The latter examined the efficiency of placental transfer of several metals and suggested that while Cr and As accumulated in the blood cord easily, the accumulation of others including Ni is less prominent. Maternal exposure can also be monitored by examination of metal traces in urine. Although very few studies have examined the correlation between metal traces found in maternal urine and cord blood , a relatively high correlation between metals found in urine and maternal blood was reporeted . Thus, Ashrap et al. (2021) suggested measuring metals in either urine or maternal blood may be an equally good approach to evaluate associations with intrauterine exposures .
In recent years, many epidemiologic studies have examined the associations between heavy metals measured in maternal urine and various adverse health outcomes among newborns, including low birth weight , low birth size , and various congenital abnormalities . While these findings alone may be associated with morbidity in early childhood  and adulthood , they may have resulted from a complicated sequence of intrauterine events  that could be associated with many other future complications, including behavioral changes in early childhood , obesity during late childhood  and various endocrine disruptions . Hence, it is crucial to investigate any associations between prenatal exposure to various heavy metals and measurable and sensitive birth outcomes. Until now, most studies conducted in this field have focused on populations exposed to relatively high levels of heavy metals [31, 32], rather than levels similar to the average background of exposure, where no exceptional exposures occur.
In the current study, we examine the association between prenatal exposure to a mixture of heavy metals (as measured in maternal urine) and newborn anthropometric measures. We investigated the concentrations of eight heavy metals (As, Cd, Cr, Hg, Ni, Pb, Se, and Tl) in maternal urine samples and examined their association with anthropometric measures, both individually and by using a modeling approach that accounts for possible non-linear associations, as well as any interactions between the metals .
Beginning in 2016, pregnant women and their newborns were recruited in delivery rooms of two hospitals in Israel: (1) Rambam Medical Center – the largest hospital in the Northern District of Israel, which accounts for around 5500 births annually, and (2) Shamir Medical Center – located in the Central region of Israel and which accounts for around 8000 deliveries annually. Women were considered eligible if they were Hebrew-speaking, aged 18 years or older, and pregnant with a singleton. Exclusion criteria included: (1) preterm birth (< 37 weeks of gestational age); (2) pregnancies considered by the medical staff to have a high risk of complications (e.g., autoimmune diseases, hypertension, diabetes) ; (3) minor or major congenital malformations as defined by the United States Centers for Disease Control and Prevention (CDC) and the European network of population-based registries for the epidemiological surveillance of congenital anomalies (EUROCAT) [35, 36]. A specialized study coordinator in each hospital obtained written informed consent from each woman before her participation and completed a questionnaire covering variables including sociodemographic characteristics, tobacco exposure, health status, pregnancy, and obstetric history. A total of 975 mother–newborns pairs were recruited from the hospitals: 509 from Rambam Medical Center and 466 from Shamir Medical Center. Maternal urine samples were collected from all participants on the day of delivery, and newborns’ anthropometric measures were taken by specialized neonatologists.
Urinary metals and creatinine
Each participant was asked to provide a single urine sample. The samples were frozen at − 80 °C immediately after receiving them and then transported at − 20 °C for further analysis at the Central Public Health Laboratory of the Israeli Ministry of Health (Abu-Kabir). We measured levels of As, Cd, Cr, Hg, Ni, Pb, Se, and Tl using inductively coupled plasma mass spectrometry (ICP-MS), on an Agilent 7800 × ICP-MS instrument equipped with an Integrated Sample Introducing System (ISIS) and High Matrix Introducing mode (HMI). The procedure involved acid dilution of urine and direct injection into the ICP-MS instrument, followed by helium dilution in the HMI instrument. The method followed standard quality assurance and quality control procedures. Urinary metal concentrations were quantified using internal standard calibration procedures and certified analytical standards. Quality control was performed by analyzing aliquots of control material in each series (every ten samples), and accuracy was validated by the successful annual participation in the international proficiency test (G-EQUAS) for all parameters. Urine creatinine was measured using a well-established colorimetric method at the Central Teratology Laboratory at the Shamir Medical Center. It was used to standardize the metal concentration detected in the urine samples by a simple adjustment and a covariate in statistical models, as previously suggested by O'Brien et al. [37, 38].
Newborns’ health and anthropometric measures
As part of a routine physical examination by trained neonatologists performed upon all infants following birth, birth weight, length, and head circumference were measured. The data were documented under an anonymized number for each mother–child pair. A total of 975 weight and head circumference measurements were conducted, as well as 887 length measurements. Each measurement was repeated three times for reliability, and mean values were computed. All results were documented in the newborns' medical records.
Using the comprehensive data collected from each mother via the questionnaires and data gathered from maternal medical registries, we were able to adjust our final models to account for possible confounders, including maternal age (continuous, in years), newborn’s gender, parity (nulliparous vs. multiparous), tobacco exposure during pregnancy (yes vs. no), socioeconomic status (SES) (standardized score), geographic area and creatinine concentration as measured in maternal urine. The maternal standardized SES index was individually calculated by matching maternally reported home address zip codes and the geographical distribution of SES as reported yearly by the Central Bureau of Statistics , using a geographical information system (GIS).
As gestational age could function as a mediator affecting the pathway between exposure and outcome , and therefore potentially lead to over- or under-estimation of the true effects , this variable was not included in the analysis.
Information on cigarette, cigar, or pipe smoking and the degree to which women were exposed to environmental tobacco smoke during pregnancy was self-reported by participants. Women were considered smoke-exposed if they reported either being an active smoker or were exposed to environmental tobacco smoke for 1 h or more per week during at least one-half of their pregnancy.
Distributional plots and descriptive statistics were examined for all variables by the recruitment center (Rambam and Shamir). Mean values and standard deviations (SDs) were used to describe continuous variables, and independent t-tests were used to compare differences between groups. Median values, interquartile ranges (IQRs), and Mann–Whitney U tests helped describe and compare maternal urinary metal concentrations between groups. We used frequencies and chi-square tests to present and compare categorical variables between groups. All metal concentrations were modeled as natural log-transformed and standardized for IQR to achieve a standard scale and account for the positive skewness detected. The mean values of repeated anthropometric measurements were calculated and then standardized to the mean and SD of the study population.
For further analysis, statistical significance was two-sided and set at p < 0.05. All statistical processes were performed using R (version 4.1.1; R Foundation for Statistical Computing) and the data.table, ggplot2, dplyr, lubridate, and bkmr packages.
Multivariate linear regression
First, we evaluated the associations between exposure to individual metals during pregnancy and standardized anthropometric measures using multivariate linear regression models adjusted for maternal age, parity, newborn’s gender, tobacco exposure, SES, geographic area and creatinine concentration as measured in maternal urine. The standardized birth weight of newborns was also included as an independent variable in models that examined the association between exposure with birth length and head circumference. First, models were adjusted for covariates without considering interactions among the metals. Then, two- and three-way interactions of metal concentrations were included in the models. The results are presented as mean differences in SD of anthropometric measures (with 95% confidence intervals, CI) per IQR change in the log-transformed urine metal concentrations.
Bayesian kernel machine regression (BKMR)
Alongside the single pollution models, possible effects of joint exposures were examined. To examine potential interactions between metals on and their associations with the standardized birth weight, length, and head circumference, Bayesian kernel machine regression (BKMR) models were run. This novel non-parametric method enables a Bayesian variable selection framework to conduct analyses of mixtures without any prior assumption of linearity of the associations  and has been widely used in prenatal exposure studies [42,43,44]. Each model (Eq. 1) accounted for an anthropometric outcome, Yi, an independent exposure–response function, h(), as well as covariates (Xi) and their corresponding coefficients (β).
In our study, BKMR models were fit using the Markov chain Monte Carlo algorithm, with 25,000 iterations using the Gaussian kernel . All metals were entered into the model as one group, and the posterior inclusion probabilities (PIP) representing the contribution of each metal to the overall association were computed and reported.
For PIP, a minimal threshold of 0.50 was previously suggested  to determine whether a single exposure is important and has any substantial association with the estimates calculated via the models. Dose–response relationships were assessed jointly for all metals and individually for each metal by fixing other exposure agents at their median values. Further exposure–response relationships between the metals were explored as mean changes in the anthropometric measurements were calculated for IQR changes in the log concentration of each metal, while the concentrations of the other metals were fixed at their 25th, 50th, and 75th percentiles. To further examine the possible bivariate metal–response associations, we visualized the anthropometric measures as functions of two exposures while concentrations of one metal change and the second were fixed at their 10th, 50th, and 90th percentiles.
Among 975 mother–newborn pairs recruited for the study (Table 1), the mean maternal age (SD) was 32.347 (4.580) years, and the mean (SD) gestational age at delivery was 39.472 (1.338) weeks; 509 newborns (52.2%) were male, and 466 (47.8%) were female. The mean birth weight (SD) was 3287.693 (441.475) g, the mean length at birth was 49.557 (2.203) cm, and the mean head circumference was 34.611 (1.272) cm. The overall metal concentrations, corrected for creatinine (μg/g creatinine), detected in maternal urine samples are shown in Table 2. Correlations between metals were tested, and Spearman’s coefficients are shown in Fig. 1.
Multivariate linear regression analysis
The linear regression results are shown in Fig. 2. When adjusting for covariates, a 1-IQR increase in log Cr concentration [μg/g creatinine] was associated with an average decrease of 0.120 SD (95% CI: -0.202 to -0.037; P = 0.004) in birth weight, as well as an average decrease in birth length of 0.133 SD (95% CI: -0.215 to -0.05; P = 0.002). A 1-IQR increase in log Tl concentration [μg/g creatinine] was also associated with an average decrease in birth weight, of 0.081 SD (95% CI: -0.158 to -0.004; P = 0.040). Head circumference was not significantly associated with any of the exposures. Neither two-way nor three-way significant interactions among the metals were detected for birth weight, length, and head circumference.
BKMR was implemented to obtain estimates of the joint exposure–response function of all metals examined in our study. We first examined the overall mixture dose–response relationship with weight, length, and head circumference at birth (Fig. 3). The results suggest a negative association for weight and head circumference and a U-shaped association for length, yet all credible intervals obtained overlapped the null association. Then, the association of each creatinine-corrected metal (IQR-centered log concentrations) in the mixture was examined with weight, length, and head circumference at birth when all other metals were fixed at their median. Models were adjusted for the covariates mentioned above and are shown in Fig. 4. The PIP values of the birth weight model are shown in Table 3 and were above 0.5 for Cr, Tl, and Ni (0.757, 0.618, and 0.646, respectively); the other metals had PIPs between 0.30 and 0.49, suggesting the probability these metals had any substantial association with newborn weight was low, thus should be considered as if their influence on the predicted outcome was low. Similar to the findings obtained from the linear model of birth weight, an inverse association was found between Cr and Tl concentrations with birth weight, while Cr was the only metal that obtained a 95% credible interval that did not overlap zero. Positive linear associations were detected between Hg as well as Ni, Pb, and Se and birth weight, while As and Cd were negatively associated with birth weight. To further investigate possible effect modifications by metals, based on the non-linear associations detected, we estimated the associations of a 1-IQR increase in each metal while the other seven metals were fixed at their 25th, 50th, and 75th percentiles (Fig. 5). A possible interaction was suggested if the estimates obtained for each metal varied while the concentrations of other metals remained unchanged. When examining the estimates of birth weight, no significant interaction among the metals was detected. For further investigation, we visualized two metals interactions plots in Figure S1 [see Additional File 1]. We denoted positive interactions as interactions in which higher levels of one exposure increased the slope of the association between the outcome and the other exposure. Hence, a positive interaction would attenuate a negative association with the outcome but would potentiate a positive association with the outcome, and vice versa for negative interactions. As shown in Figure S1 [see Additional File 1], there was a suggestion of a positive interaction between As and Cr that attenuated the negative associations between the metal and birth weight.
Only two PIP values calculated for the metals in the length model were higher than 0.50 (Table 3): 0.772 for Cr and 0.524 for Hg. Length at birth appeared to be (Fig. 4) a decreasing function of Cr and an increasing function of Hg, yet only Cr function yielded a 95% credible interval that did not overlap zero. Further analysis (Fig. 5) did not show any susceptibility for interactions among the metals. An examination of the slopes obtained from the two-metal interaction plots (Figure S2 [see Additional File 1]) suggested a negative interaction between Cr and both Hg and Ni that potentiate the negative associations between the metals and attenuated the positive association between them and birth length.
Calculated PIPs for the head circumference model (Table 3) were lower than 0.5 for all metals. Although visualization of the univariate exposure–response chart (Fig. 4) did suggest a negative association of Cr and Tl with head circumference, but the credible intervals of both functions did overlap zero, suggesting a non-significant association. As shown in Fig. 5, the estimates obtained from the interaction models for each metal remained unchanged, suggesting no significant interactions among the metals. These findings were supported by the bivariate metal-response functions (Figure S3 [see Additional File 1]).
Using modeling approaches that account for linear as well as non-linear relations, we examined the association between eight metals detected in maternal urine at delivery and anthropometric measures of the newborns. Our findings suggested Cr had the most prominent negative association with weight and length. An inverse association between Tl and birth length was detected, while a positive association between Ni and birth weight was suggested.
The combined effect of all metals is shown and suggests a negative association for weight and head circumference and a U-shaped association for length. Although the trends can be visualized, the estimates are close to zero, and the credible intervals overlap the null association, suggesting the trends are insignificant. The joint effects, reflected by the crude trends may be influenced by biological and chemical interactions between the metals. Thus different associations can mask each other and should be further studied among larger sample sizes with higher exposure levels.
Our analysis suggested a negative association between increasing levels of Cr and a newborn's weight and length. Evidence of negative associations between Tl and Ni with birth weight and Hg with length was also detected. The reduction in birth weight associated with increased Cr levels was supported by both the linear and BKMR models, as the latter also suggested a positive interaction between Cr and both As and Se that attenuated the negative associations between the metal and birth weight. These interactions may explain the inconsistencies compared with other studies conducted in this field. Several studies have reported a possible decrease in newborn birth size and weight associated with increasing levels of Cr in maternal urine samples at birth  and during pregnancy . However, other studies did not support these findings [49, 50], although none accounted for possible associations between the outcomes and mixtures of metals. There is increasing evidence to suggest that Cr in maternal blood is associated with placental insufficiency , increasing placental oxidative stress, and possible lower birth weight and pregnancy complications . Besides this indirect mechanism, Saxena et al.  suggest that Cr can cross the placenta, accumulate in the fetal tissues, and could directly induce DNA damage  and affect intrauterine growth .
Although Se was non significantly associated with birthweight, the proximity of its calculated PIP to 0.5 and the possible interaction with Cr could not be neglected. Its possible association with the increase in birth weight is consistent with a study conducted by Solé-Navais et al. (2020) . In their study, increased prenatal levels of Se detected in the blood of Norwegian pregnant women were found to be significantly and positively associated with birth weight. Monangi et al. (2021)  suggested that increasing levels of Se in maternal blood were associated with longer gestation and hence could contribute to the increase in birth weight. The mechanism underlying the involvement of Se in gestational duration is not fully understood. Still, it could be explained by its role in the suppression of mediators involved in the activation of labor in human fetal membranes and the myometrium . The authors of another study , suggested Se could form chemical bonds, reduce the effect of teratogenic metals, and promote fetal growth. In our study, high concentrations of Se did appear to attenuate the reduction of birth weight associated with Cr. However, the mechanisms underlying this possible interaction and its association with anthropometric measures are beyond the scope of this study and should be further investigated.
Similar to Cr, increasing levels of Tl were significantly associated with lower birth weight, as shown in the linear models and supported by the BKMR models. These results are consistent with the findings of several studies [59,60,61], where Tl was found to be associated with decreased birth weight. It was previously suggested that Tl, as with Cr, can increase the placental as well as the fetal oxidative stress  and is thus associated with intrauterine growth restriction . Prenatal exposure to Tl has been found to be associated with a decrease in maternal and fetal thyroid activity , which could be directly and indirectly related to developmental impairments . However, while we found Tl levels were negatively and significantly associated with a newborn’s weight, they were not found to be associated with length or head circumference.
As shown in Table S2 [see Additional File 1], compared with other studies conducted in this field, the medians of most of the metal/creatinine concentrations (μg/g) detected in our study (Table 2) were lower [23, 60, 65,66,67,68,69,70], except for Se, which showed higher levels compared with other studies (geometric mean = 38.68 μg/g; median = 38.35 μg/g; IQR: 30.64–48.42 μg/g). However, this was similar to the amounts detected among pregnant women in the US  by Kim et al. (2019); geometric mean = 35.4 μg/g (IQR: 18.0–57.4 μg/g). The relatively low concentrations of metals detected in urine samples from our study population enabled us to examine possible associations between anthropometric measures at birth and prenatal exposure to metals at levels similar to the background averages.
Previous studies that examined the association of Ni with fetal growth have been inconclusive; however, several studies [71, 72] have reported positive associations between Ni and fetal development. The positive association between Ni concentration and fetal growth could be attributed to some of the nutritional benefits of Ni. As it has a biological function in metabolic pathways in which vitamin B12 is important , Ni could potentially affect the stages in fetal growth when consumption of B12 is enhanced . The possible association between Ni, weight, and length was also observed by Howe et al. (2022)  and thus contributed the validity of our findings.
The association of maternal urine Hg concentrations with anthropometric measures of newborns has been investigated [58, 66]. While some studies did suggest an inverse association between prenatal exposure to Hg and anthropometric measurements at birth , most studies did not offer any significant association [58, 66] and were conducted among women exposed to median Hg levels five to six-fold higher than those observed in our study. In general, Hg levels detected in our study were lower than those seen among the US population  and significantly lower than the upper limit suggested  for pregnant women by the World Health Organization (WHO) (5–7 μg/g creatinine). In our study, Increasing levels of Hg were found to be positively but non-significantly associated with length. Yet, the Hg levels detected among participants in our study were low and had a narrow range (IQR = 0.08 to 0.38 μg/g creatinine) compared with other studies. Therefore, the associations with anthropometric measures should be considered carefully and studied further among populations with greater variances.
As Pb and Cd levels exceeded the limit of detection (LOD) in less than 70% of participants in our study and had a prominently lower range and mean compared with other studies [78,79,80], it is difficult to relate the dose–response relationships observed for these metals with changes in the anthropometric measures.
Previous literature on the association between As exposure and anthropometric measures of the newborn is relatively limited, and reports have had mixed findings: while some failed to reject the null hypothesis [81, 82], others reported an inverse association between increasing concentrations of As and birth weight , as well as birth size . In our study, although non-significant, the association between As concentration in maternal urine and newborn weight was inverse and consistent with previous studies [30, 83]. As concentrations were not found to be associated with head circumference, similar to previous studies [85, 86]. The PIP value calculated for As suggested it did not influence the estimates calculated for the outcome. However, the findings in other studies were inconsistent; while Shih et al. (2020)  reported a positive association, other studies reported inverse [31, 87, 88] associations between As levels in maternal blood or urine and the head circumference of the newborn. Although we were failed to reject the null hypothesis, the inconsistency with previous studies highlights the need for further research.
None of the metals was found to be significantly associated with head circumference in any of the models run. Using the BKMR models for head circumference, the PIPs detected were less than 0.50 for all metals, and single exposure associations appeared insignificant. Various associations between metals and head circumference were previously shown by Rahman et al. (2021) , who examined associations between metals detected in maternal erythrocytes and newborn anthropometric measures. An infant’s head circumference was previously found to be associated with many prenatal and environmental factors, including the newborn’s gender and gestational age  and maternal nutrition . However, it is predominantly determined by inheritance  and pathways involving many genes and transcription factors ; therefore alternations in head circumference characterize many genetic disorders [92, 93] and have been extensively studied. As many of the metals included in this study were previously found to act as genetic modifiers [94,95,96], suppressing or enhancing fetal expression of genes, it is not unreasonable to assume that interactions between these metals themselves , or with proteins , including transcription factors, could lead to various alterations in newborns’ phenotypes. Recent studies have suggested that metals could also interact with epigenetic processes that may be crucial to intrauterine development , especially in the context of metal mixtures. Investigating the biochemical mechanisms that contribute to genomic–metal interactions should be a key area for future research and might require the collection of samples such as placental tissue and cord blood.
The current study had several strengths: the large sample size, the examination of multiple metals, the use of classic as well as advanced mixture modeling analysis, and the heterogeneous population recruited from two different geographical areas and hospitals. However, there were also several limitations. Since maternal education and income data was not collected, individual zip code-based SES was used. As our study included only term newborns, any association between prenatal maternal exposure to metals and preterm deliveries could not be examined [56, 78, 87]. The metal concentrations observed in our study were relatively low; this enabled us to examine the possible effect of daily exposures. On the other hand, it limited the scope of outcomes associated with high concentrations and wide variances. Although metals could be measured in urine and were corrected to maternal hydration condition, they had a variety of half-lives, with some concentrations reflecting exposure that had occurred in the past few days (e.g., As, Ni, Pb, Se, and Tl), and others reflecting exposures over past weeks and months (e.g., Cd, Cr, and Hg) [99,100,101,102]. Thus, our findings cannot reflect any association between duration and prenatal timing of exposure with any of the anthropometric measures. It is worth mentioning that metals measured in urine did not reflect the existence of many possible potent forms in the human body, e.g., methyl-Hg , selenomethionine , and lead–protein complexes .
Using a large sample size and multi-metal mixture data, we delineated a potential association between prenatal maternal exposure to heavy metals and newborns’ weight, length, and head circumference. Our findings suggested that Cr was the most influential metal in predicting weight and length, as it was also negatively associated with both. An inverse association between Tl and birth length was detected, while a positive association between Ni and birth weight was suggested. Although some findings were not consistent with those of other studies, the levels of heavy metals observed in our study were relatively low, with low variances. Hence some associations detected might be spurious and should be further investigated in future epidemiologic studies as well as in vitro and in vivo biochemical studies.
Availability of data and materials
The datasets generated and analyzed during the current study are not publicly available due to ethical restrictions but are available from the corresponding author upon reasonable request.
Appropriate for Gestational Age
Bayesian Kernel Machine Regression
Center for Disease Control and Prevention
European network of population-based registries for the epidemiological surveillance of congenital anomalies
Geographic Information System
High Matrix Introducing Mode
Inductively Coupled Plasma Mass Spectrometry
Integrated Sample Introducing System
Large for Gestational Age
Limits of quantification
Posterior Inclusion Probability
Small for Gestational Age
Standardized Sociodemographic Status
Organization WH, Agency IAE, Nations F and AO of the U. Trace elements in human nutrition and health. World Health Organization; 1996. Accessed 2 Mar 2020. https://apps.who.int/iris/handle/10665/37931
Tchounwou PB, Yedjou CG, Patlolla AK, Sutton DJ. Heavy Metals Toxicity and the Environment. EXS. 2012;101:133–64. https://doi.org/10.1007/978-3-7643-8340-4_6.
Jan AT, Azam M, Siddiqui K, Ali A, Choi I, Haq Q, Mohd R. Heavy Metals and Human Health: Mechanistic Insight into Toxicity and Counter Defense System of Antioxidants. Int J Mol Sci. 2015;16(12):29592–630. https://doi.org/10.3390/ijms161226183.
Balali-Mood M, Naseri K, Tahergorabi Z, Khazdair MR, Sadeghi M. Toxic mechanisms of five heavy metals: mercury, lead, chromium, cadmium, and arsenic. Front Pharmacol. 2021;12:643972. https://doi.org/10.3389/fphar.2021.643972.
Zheng G, Zhong H, Guo Z, et al. Levels of heavy metals and trace elements in umbilical cord blood and the risk of adverse pregnancy outcomes: a population-based study. Biol Trace Elem Res. 2014;160(3):437–44. https://doi.org/10.1007/s12011-014-0057-x.
Kippler M, Tofail F, Gardner R, et al. Maternal cadmium exposure during pregnancy and size at birth: a prospective cohort study. Environ Health Perspect. 2012;120(2):284–9. https://doi.org/10.1289/ehp.1103711.
Howe CG, Claus Henn B, Eckel SP, et al. Prenatal metal mixtures and birth weight for gestational age in a predominately lower-income Hispanic pregnancy cohort in Los Angeles. Environ Health Perspect. 2020;128(11):117001. https://doi.org/10.1289/EHP7201.
Lee MS, Eum KD, Golam M, et al. Umbilical Cord Blood Metal Mixtures and Birth Size in Bangladeshi Children. Environ Health Perspect. 2021;129(5):EHP7502, 057006. https://doi.org/10.1289/EHP7502.
Arai Y, Ohgane J, Yagi S, et al. Epigenetic assessment of environmental chemicals detected in maternal peripheral and cord blood samples. J Reprod Dev. 2011;57(4):507–17. https://doi.org/10.1262/jrd.11-034A.
Hanna CW, Bloom MS, Robinson WP, et al. DNA methylation changes in whole blood is associated with exposure to the environmental contaminants, mercury, lead, cadmium and bisphenol A, in women undergoing ovarian stimulation for IVF. Hum Reprod. 2012;27(5):1401–10. https://doi.org/10.1093/humrep/des038.
Chen Z, Myers R, Wei T, et al. Placental transfer and concentrations of cadmium, mercury, lead, and selenium in mothers, newborns, and young children. J Expo Sci Environ Epidemiol. 2014;24(5):537–44. https://doi.org/10.1038/jes.2014.26.
Zhang YL, Zhao YC, Wang JX, et al. Effect of Environmental Exposure to Cadmium on Pregnancy Outcome and Fetal Growth: A Study on Healthy Pregnant Women in China. J Environ Sci Health Part A. 2004;39(9):2507–15. https://doi.org/10.1081/ESE-200026331.
Gustin K, Barman M, Stråvik M, et al. Low-level maternal exposure to cadmium, lead, and mercury and birth outcomes in a Swedish prospective birth-cohort. Environ Pollut. 2020;265:114986. https://doi.org/10.1016/j.envpol.2020.114986.
Rahman ML, Oken E, Hivert MF, et al. Early pregnancy exposure to metal mixture and birth outcomes – A prospective study in Project Viva. Environ Int. 2021;156:106714. https://doi.org/10.1016/j.envint.2021.106714.
McDermott S, Salzberg DC, Anderson AP, Shaw T, Lead J. Systematic Review of Chromium and Nickel Exposure During Pregnancy and Impact on Child Outcomes. J Toxicol Environ Health A. 2015;78(21–22):1348–68. https://doi.org/10.1080/15287394.2015.1090939.
Qi J, Lai Y, Liang C, et al. Prenatal thallium exposure and poor growth in early childhood: a prospective birth cohort study. Environ Int. 2019;123:224–30. https://doi.org/10.1016/j.envint.2018.12.005.
Shih YH, Scannell Bryan M, Argos M. Association between prenatal arsenic exposure, birth outcomes, and pregnancy complications: An observational study within the National Children’s Study cohort. Environ Res. 2020;183:109182. https://doi.org/10.1016/j.envres.2020.109182.
Kot K, Łanocha-Arendarczyk N, Kupnicka P, et al. Selected Metal Concentration in Maternal and Cord Blood. Int J Environ Res Public Health. 2021;18(23):12407. https://doi.org/10.3390/ijerph182312407.
Li A, Zhuang T, Shi J, Liang Y, Song M. Heavy metals in maternal and cord blood in Beijing and their efficiency of placental transfer. J Environ Sci. 2019;80:99–106. https://doi.org/10.1016/j.jes.2018.11.004.
Bocca B, Ruggieri F, Pino A, et al. Human biomonitoring to evaluate exposure to toxic and essential trace elements during pregnancy. Part A. concentrations in maternal blood, urine and cord blood. Environ Res. 2019;177:108599. https://doi.org/10.1016/j.envres.2019.108599.
Ashrap P, Watkins DJ, Mukherjee B, et al. Predictors of urinary and blood Metal(loid) concentrations among pregnant women in Northern Puerto Rico. Environ Res. 2020;183:109178. https://doi.org/10.1016/j.envres.2020.109178.
Ashrap P, Watkins DJ, Mukherjee B, et al. Performance of urine, blood, and integrated metal biomarkers in relation to birth outcomes in a mixture setting. Environ Res. 2021;200:111435. https://doi.org/10.1016/j.envres.2021.111435.
Wai K, Mar O, Kosaka S, Umemura M, Watanabe C. Prenatal heavy metal exposure and adverse birth outcomes in Myanmar: a birth-cohort study. Int J Environ Res Public Health. 2017;14(11):1339. https://doi.org/10.3390/ijerph14111339.
Karakis I, Landau D, Yitshak-Sade M, et al. Exposure to metals and congenital anomalies: a biomonitoring study of pregnant Bedouin-Arab women. Sci Total Environ. 2015;517:106–12. https://doi.org/10.1016/j.scitotenv.2015.02.056.
McIntire DD, Bloom SL, Casey BM, Leveno KJ. Birth weight in relation to morbidity and mortality among newborn infants. N Engl J Med. 1999;340(16):1234–8. https://doi.org/10.1056/NEJM199904223401603.
Risnes KR, Vatten LJ, Baker JL, et al. Birthweight and mortality in adulthood: a systematic review and meta-analysis. Int J Epidemiol. 2011;40(3):647–61. https://doi.org/10.1093/ije/dyq267.
Punshon T, Li Z, Jackson BP, et al. Placental metal concentrations in relation to placental growth, efficiency and birth weight. Environ Int. 2019;126:533–42. https://doi.org/10.1016/j.envint.2019.01.063.
Cowell W, Colicino E, Levin-Schwartz Y, et al. Prenatal metal mixtures and sex-specific infant negative affectivity. Environ Epidemiol. 2021;5(2):e147. https://doi.org/10.1097/EE9.0000000000000147.
Gardner RM, Kippler M, Tofail F, et al. Environmental exposure to metals and children’s growth to age 5 years: a prospective cohort study. Am J Epidemiol. 2013;177(12):1356–67. https://doi.org/10.1093/aje/kws437.
Sun X, Liu W, Zhang B, et al. Maternal heavy metal exposure, thyroid hormones, and birth outcomes: a prospective cohort study. J Clin Endocrinol Metab. 2019;104(11):5043–52. https://doi.org/10.1210/jc.2018-02492.
Gilbert-Diamond D, Emond JA, Baker ER, Korrick SA, Karagas MR. Relation between in utero arsenic exposure and birth outcomes in a cohort of mothers and their newborns from new Hampshire. Environ Health Perspect. 2016;124(8):1299–307. https://doi.org/10.1289/ehp.1510065.
Fang X, Qu J, Huan S, et al. Associations of urine metals and metal mixtures during pregnancy with cord serum vitamin D Levels: a prospective cohort study with repeated measurements of maternal urinary metal concentrations. Environ Int. 2021;155:106660. https://doi.org/10.1016/j.envint.2021.106660.
Bobb JF, Valeri L, Claus Henn B, et al. Bayesian kernel machine regression for estimating the health effects of multi-pollutant mixtures. Biostatistics. 2015;16(3):493–508. https://doi.org/10.1093/biostatistics/kxu058.
Holness N. High-Risk Pregnancy. Nurs Clin North Am. 2018;53(2):241–51. https://doi.org/10.1016/j.cnur.2018.01.010.
World Health Organization, Centers for Disease Control and Prevention (U.S.), International Clearinghouse for Birth Defects Monitoring Systems. Birth Defects Surveillance: A Manual for Programme Managers. 2nd ed. World Health Organization; 2020. Accessed 5 June 2022. https://apps.who.int/iris/handle/10665/337425
Khoshnood B, Greenlees R, Loane M, Dolk H, on behalf of the EUROCAT Project Management Committee and a EUROCAT Working Group. Paper 2: EUROCAT public health indicators for congenital anomalies in Europe. Birt Defects Res A Clin Mol Teratol. 2011;91(S1):S16–22. https://doi.org/10.1002/bdra.20776.
O’Brien KM, Upson K, Cook NR, Weinberg CR. Environmental Chemicals in Urine and Blood: Improving Methods for Creatinine and Lipid Adjustment. Environ Health Perspect. 2016;124(2):220–7. https://doi.org/10.1289/ehp.1509693.
O’Brien KM, Upson K, Buckley JP. Lipid and creatinine adjustment to evaluate health effects of environmental exposures. Curr Environ Health Rep. 2017;4(1):44–50. https://doi.org/10.1007/s40572-017-0122-7.
Characterization and Classification of Geographical Units by the Socio-Economic Level of the Population 2017. The National Central Bureau of Statistics. Jerusalem, Israel. 2020.
Ananth CV, Brandt JS. A principled approach to mediation analysis in perinatal epidemiology. Am J Obstet Gynecol. 2022;226(1):24-32.e6. https://doi.org/10.1016/j.ajog.2021.10.028.
VanderWeele TJ, Mumford SL, Schisterman EF. Conditioning on intermediates in perinatal epidemiology. Epidemiology. 2012;23(1):1–9. https://doi.org/10.1097/EDE.0b013e31823aca5d.
Signes-Pastor AJ, Doherty BT, Romano ME, et al. Prenatal exposure to metal mixture and sex-specific birth outcomes in the New Hampshire Birth Cohort Study. Environ Epidemiol. 2019;3(5):e068. https://doi.org/10.1097/EE9.0000000000000068.
Chen X, Wei L, Huang H, et al. Assessment of individual and mixture effects of element exposure measured in umbilical cord blood on birth weight in Bangladesh. Environ Res Commun. 2021;3(10):105001. https://doi.org/10.1088/2515-7620/ac23a8.
Lee KS, Kim KN, Ahn YD, et al. Prenatal and postnatal exposures to four metals mixture and IQ in 6-year-old children: a prospective cohort study in South Korea. Environ Int. 2021;157:106798. https://doi.org/10.1016/j.envint.2021.106798.
Bobb JF, Claus Henn B, Valeri L, Coull BA. Statistical software for analyzing the health effects of multiple concurrent exposures via Bayesian kernel machine regression. Environ Health. 2018;17(1):67. https://doi.org/10.1186/s12940-018-0413-y.
Coker E, Chevrier J, Rauch S, et al. Association between prenatal exposure to multiple insecticides and child body weight and body composition in the VHEMBE South African birth cohort. Environ Int. 2018;113:122–32. https://doi.org/10.1016/j.envint.2018.01.016.
Xia W, Hu J, Zhang B, et al. A case-control study of maternal exposure to chromium and infant low birth weight in China. Chemosphere. 2016;144:1484–9. https://doi.org/10.1016/j.chemosphere.2015.10.006.
Peng Y, Hu J, Li Y, et al. Exposure to chromium during pregnancy and longitudinally assessed fetal growth: Findings from a prospective cohort. Environ Int. 2018;121:375–82. https://doi.org/10.1016/j.envint.2018.09.003.
Guo Y, Huo X, Li Y, et al. Monitoring of lead, cadmium, chromium and nickel in placenta from an e-waste recycling town in China. Sci Total Environ. 2010;408(16):3113–7. https://doi.org/10.1016/j.scitotenv.2010.04.018.
Cabrera-Rodríguez R, Luzardo OP, González-Antuña A, et al. Occurrence of 44 elements in human cord blood and their association with growth indicators in newborns. Environ Int. 2018;116:43–51. https://doi.org/10.1016/j.envint.2018.03.048.
Banu SK, Stanley JA, Taylor RJ, et al. Sexually dimorphic impact of chromium accumulation on human placental oxidative stress and apoptosis. Toxicol Sci. 2018;161(2):375–87. https://doi.org/10.1093/toxsci/kfx224.
Schoots MH, Gordijn SJ, Scherjon SA, van Goor H, Hillebrands JL. Oxidative stress in placental pathology. Placenta. 2018;69:153–61. https://doi.org/10.1016/j.placenta.2018.03.003.
Saxena DK, Murthy RC, Jain VK, Chandra SV. Fetoplacental-maternal uptake of hexavalent chromium administered orally in rats and mice. Bull Environ Contam Toxicol. 1990;45(3):430–5. https://doi.org/10.1007/BF01701168.
Wise SS, Holmes AL, Wise, Sr. JP. Hexavalent Chromium-Induced DNA Damage and Repair Mechanisms. Rev Environ Health. 2008;23(1). https://doi.org/10.1515/REVEH.2008.23.1.39
Solé-Navais P, Brantsæter AL, Caspersen IH, et al. Maternal dietary selenium intake during pregnancy is associated with higher birth weight and lower risk of small for gestational age births in the Norwegian Mother, Father and child cohort study. Nutrients. 2020;13(1):23. https://doi.org/10.3390/nu13010023.
Monangi N, Xu H, Khanam R, et al. Association of maternal prenatal selenium concentration and preterm birth: a multicountry meta-analysis. BMJ Glob Health. 2021;6(9):e005856. https://doi.org/10.1136/bmjgh-2021-005856.
Kalansuriya DM, Lim R, Lappas M. In vitro selenium supplementation suppresses key mediators involved in myometrial activation and rupture of fetal membranes. Metallomics. 2020;12(6):935–51. https://doi.org/10.1039/d0mt00063a.
Sun H, Chen W, Wang D, Jin Y, Chen X, Xu Y. The effects of prenatal exposure to low-level cadmium, lead and selenium on birth outcomes. Chemosphere. 2014;108:33–9. https://doi.org/10.1016/j.chemosphere.2014.02.080.
Hu X, Zheng T, Cheng Y, et al. Distributions of heavy metals in maternal and cord blood and the association with infant birth weight in China. J Reprod Med. 2015;60(1–2):21–9.
Xia W, Du X, Zheng T, et al. A case-control study of prenatal thallium exposure and low birth weight in China. Environ Health Perspect. 2016;124(1):164–9. https://doi.org/10.1289/ehp.1409202.
Zhou H, Sun X, Wang Y, et al. The mediating role of placental weight change in the association between prenatal exposure to thallium and birth weight: a prospective birth cohort study. Front Public Health. 2021;9:679406. https://doi.org/10.3389/fpubh.2021.679406.
Puttabyatappa M, Banker M, Zeng L, et al. Maternal exposure to environmental disruptors and sexually dimorphic changes in maternal and neonatal oxidative stress. J Clin Endocrinol Metab. 2020;105(2):492–505. https://doi.org/10.1210/clinem/dgz063.
Biri A, Bozkurt N, Turp A, Kavutcu M, Himmetoglu Ö, Durak İ. Role of oxidative stress in intrauterine growth restriction. Gynecol Obstet Invest. 2007;64(4):187–92. https://doi.org/10.1159/000106488.
Yorita Christensen KL. Metals in blood and urine, and thyroid function among adults in the United States 2007–2008. Int J Hyg Environ Health. 2013;216(6):624–32. https://doi.org/10.1016/j.ijheh.2012.08.005.
Fort M, Cosín-Tomás M, Grimalt JO, Querol X, Casas M, Sunyer J. Assessment of exposure to trace metals in a cohort of pregnant women from an urban center by urine analysis in the first and third trimesters of pregnancy. Environ Sci Pollut Res. 2014;21(15):9234–41. https://doi.org/10.1007/s11356-014-2827-6.
Bashore C, Geer L, He X, et al. Maternal mercury exposure, season of conception and adverse birth outcomes in an urban immigrant community in Brooklyn, New York, U.S.A. Int J Environ Res Public Health. 2014;11(8):8414–42. https://doi.org/10.3390/ijerph110808414.
Xiao T, Guha J, Liu CQ, et al. Potential health risk in areas of high natural concentrations of thallium and importance of urine screening. Appl Geochem. 2007;22(5):919–29. https://doi.org/10.1016/j.apgeochem.2007.02.008.
Wang X, Qi L, Peng Y, et al. Urinary concentrations of environmental metals and associating factors in pregnant women. Environ Sci Pollut Res. 2019;26(13):13464–75. https://doi.org/10.1007/s11356-019-04731-z.
Kim SS, Meeker JD, Keil AP, et al. Exposure to 17 trace metals in pregnancy and associations with urinary oxidative stress biomarkers. Environ Res. 2019;179:108854. https://doi.org/10.1016/j.envres.2019.108854.
Barregard L, Ellingsen DG, Berlinger B, Weinbruch S, Harari F, Sallsten G. Normal variability of 22 elements in 24-hour urine samples – Results from a biobank from healthy non-smoking adults. Int J Hyg Environ Health. 2021;233:113693. https://doi.org/10.1016/j.ijheh.2021.113693.
Howe CG, Nozadi SS, Garcia E, et al. Prenatal metal(loid) mixtures and birth weight for gestational age: a pooled analysis of three cohorts participating in the ECHO program. Environ Int. 2022;161:107102. https://doi.org/10.1016/j.envint.2022.107102.
Jalali LM, Koski KG. Amniotic fluid minerals, trace elements, and prenatal supplement use in humans emerge as determinants of fetal growth. J Trace Elem Med Biol. 2018;50:139–45. https://doi.org/10.1016/j.jtemb.2018.06.012.
Nielsen FH, Uthus EO, Poellot RA, Shuler TR. Dietary vitamin B12, sulfur amino acids, and odd-chain fatty acids affect the response of rats to nickel deprivation. Biol Trace Elem Res. 1993;37(1):1–15. https://doi.org/10.1007/BF02789397.
Rogne T, Tielemans MJ, Chong MFF, et al. Associations of Maternal Vitamin B12 Concentration in Pregnancy With the Risks of Preterm Birth and Low Birth Weight: A Systematic Review and Meta-Analysis of Individual Participant Data. Am J Epidemiol. Published online January 20, 2017:amjepid;kww212v1. https://doi.org/10.1093/aje/kww212
Vigeh M, Nishioka E, Ohtani K, et al. Prenatal mercury exposure and birth weight. Reprod Toxicol. 2018;76:78–83. https://doi.org/10.1016/j.reprotox.2018.01.002.
Third National Report on Human Exposure to Environmental Chemicals (No. NCEH Pub. No. 05-0570), 2005. Department of Health and Human Services Centers for Disease Control and Prevention (CDC), Atlanta, Georgia 30341-3724.
Assessment of prenatal exposure to mercury: human biomonitoring survey. Published online 2018. Accessed 26 Jan 2022. https://www.euro.who.int/en/health-topics/environment-and-health/chemical-safety/publications/2018/assessment-of-prenatal-exposure-to-mercury-human-biomonitoring-survey-2018
Zhang B, Xia W, Li Y, et al. Prenatal exposure to lead in relation to risk of preterm low birth weight: a matched case-control study in China. Reprod Toxicol Elmsford N. 2015;57:190–5. https://doi.org/10.1016/j.reprotox.2015.06.051.
Nozadi SS, Li L, Luo L, et al. Prenatal Metal Exposures and Infants’ Developmental Outcomes in a Navajo Population. Int J Environ Res Public Health. 2021;19(1):425. https://doi.org/10.3390/ijerph19010425.
Amegah AK, Sewor C, Jaakkola JJK. Cadmium exposure and risk of adverse pregnancy and birth outcomes: a systematic review and dose–response meta-analysis of cohort and cohort-based case–control studies. J Expo Sci Environ Epidemiol. 2021;31(2):299–317. https://doi.org/10.1038/s41370-021-00289-6.
Davis MA, Higgins J, Li Z, et al. Preliminary analysis of in utero low-level arsenic exposure and fetal growth using biometric measurements extracted from fetal ultrasound reports. Environ Health. 2015;14(1):12. https://doi.org/10.1186/1476-069X-14-12.
Fano-Sizgorich D, Vásquez-Velásquez C, Yucra S, et al. Total urinary arsenic and inorganic arsenic concentrations and birth outcomes in pregnant women of Tacna, Peru: a cross-sectional Study. Expo Health. 2021;13(1):133–40. https://doi.org/10.1007/s12403-020-00377-2.
Guan H, Piao F, Zhang X, et al. Prenatal Exposure to Arsenic and Its Effects on Fetal Development in the General Population of Dalian. Biol Trace Elem Res. 2012;149(1):10–5. https://doi.org/10.1007/s12011-012-9396-7.
Mullin AM, Amarasiriwardena C, Cantoral-Preciado A, et al. Maternal blood arsenic levels and associations with birth weight-for-gestational age. Environ Res. 2019;177:108603. https://doi.org/10.1016/j.envres.2019.108603.
Bermúdez L, García-Vicent C, López J, Torró MI, Lurbe E. Assessment of ten trace elements in umbilical cord blood and maternal blood: association with birth weight. J Transl Med. 2015;13:291. https://doi.org/10.1186/s12967-015-0654-2.
Bloom MS, Neamtiu IA, Surdu S, et al. Low level arsenic contaminated water consumption and birth outcomes in Romania-An exploratory study. Reprod Toxicol Elmsford N. 2016;59:8–16. https://doi.org/10.1016/j.reprotox.2015.10.012.
Rahman ML, Kile ML, Rodrigues EG, et al. Prenatal arsenic exposure, child marriage, and pregnancy weight gain: associations with preterm birth in Bangladesh. Environ Int. 2018;112:23–32. https://doi.org/10.1016/j.envint.2017.12.004.
Liao KW, Chang CH, Tsai MS, et al. Associations between urinary total arsenic levels, fetal development, and neonatal birth outcomes: a cohort study in Taiwan. Sci Total Environ. 2018;612:1373–9. https://doi.org/10.1016/j.scitotenv.2017.08.312.
Yokoyama Y, Sugimoto M, Ooki S. Analysis of factors affecting birthweight, birth length and head circumference: study of Japanese triplets. Twin Res Hum Genet. 2005;8(6):657–63. https://doi.org/10.1375/twin.8.6.657.
Smit DJA, Luciano M, Bartels M, et al. Heritability of head size in Dutch and Australian twin families at ages 0–50 years. Twin Res Hum Genet. 2010;13(4):370–80. https://doi.org/10.1375/twin.13.4.370.
Yang XL, Zhang SY, Zhang H, et al. Three Novel Loci for Infant Head Circumference Identified by a Joint Association Analysis. Front Genet. 2019;10:947. https://doi.org/10.3389/fgene.2019.00947.
Jayaraman D, Bae BI, Walsh CA. The Genetics of primary microcephaly. Annu Rev Genomics Hum Genet. 2018;19(1):177–200. https://doi.org/10.1146/annurev-genom-083117-021441.
Williams CA, Dagli A, Battaglia A. Genetic disorders associated with macrocephaly. Am J Med Genet A. 2008;146A(15):2023–37. https://doi.org/10.1002/ajmg.a.32434.
Smeester L, Martin EM, Cable P, et al. Toxic metals in amniotic fluid and altered gene expression in cell-free fetal RNA. Prenat Diagn. 2017;37(13):1364–6. https://doi.org/10.1002/pd.5183.
Montes-Castro N, Alvarado-Cruz I, Torres-Sánchez L, et al. Prenatal exposure to metals modified DNA methylation and the expression of antioxidant- and DNA defense-related genes in newborns in an urban area. J Trace Elem Med Biol. 2019;55:110–20. https://doi.org/10.1016/j.jtemb.2019.06.014.
Bozack AK, Rifas-Shiman SL, Coull BA, et al. Prenatal metal exposure, cord blood DNA methylation and persistence in childhood: an epigenome-wide association study of 12 metals. Clin Epigenetics. 2021;13(1):208. https://doi.org/10.1186/s13148-021-01198-z.
Wang M, Xia W, Liu H, et al. Urinary metabolomics reveals novel interactions between metal exposure and amino acid metabolic stress during pregnancy. Toxicol Res. 2018;7(6):1164–72. https://doi.org/10.1039/C8TX00042E.
Küpers LK, Monnereau C, Sharp GC, et al. Meta-analysis of epigenome-wide association studies in neonates reveals widespread differential DNA methylation associated with birthweight. Nat Commun. 2019;10(1):1893. https://doi.org/10.1038/s41467-019-09671-3.
Paustenbach DJ, Panko JM, Fredrick MM, Finley BL, Proctor DM. Urinary chromium as a biological marker of environmental exposure: what are the limitations? Regul Toxicol Pharmacol. 1997;26(1):S23–34. https://doi.org/10.1006/rtph.1997.1135.
Hawkes WC, Alkan FZ, Oehler L. Absorption, Distribution and Excretion of Selenium from Beef and Rice in Healthy North American Men. J Nutr. 2003;133(11):3434–42. https://doi.org/10.1093/jn/133.11.3434.
Keil DE, Berger-Ritchie J, McMillin GA. Testing for toxic elements: a focus on arsenic, cadmium, lead, and mercury. Lab Med. 2011;42(12):735–42. https://doi.org/10.1309/LMYKGU05BEPE7IAW.
Nordberg G, Fowler BA, Nordberg M. Handbook on the Toxicology of Metals. 4th edition. Elsevier/Academic Press; Amsterdam. 2015.
Park JD, Zheng W. Human exposure and health effects of inorganic and elemental mercury. J Prev Med Pub Health. 2012;45(6):344–52. https://doi.org/10.3961/jpmph.2012.45.6.344.
Mehdi Y, Hornick JL, Istasse L, Dufrasne I. Selenium in the environment, metabolism and involvement in body functions. Molecules. 2013;18(3):3292–311. https://doi.org/10.3390/molecules18033292.
de Souza ID, de Andrade AS, Dalmolin RJS. Lead-interacting proteins and their implication in lead poisoning. Crit Rev Toxicol. 2018;48(5):375–86. https://doi.org/10.1080/10408444.2018.1429387.
The authors wish to thank our colleagues from Rambam and Shamir hospitals, the medical, nursing, and recruitment staff, and the newborns and families participating in the study.
The research reported in this publication was supported by grant support from the Israeli Ministry of Environmental Protection (No.161–1-1/2016–1). The content of this paper is solely the responsibility of the authors. It does not necessarily represent the official views of the Israeli Ministry of Environmental Protection, as it had no other involvement in the study or submission.
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All study procedures were approved by the Institutional Review Boards at Rambam Medical Center and Shamir Medical Center. All participants signed a written informed consent to participate in the study.
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Additional file 1: Table S1.
Urinary Metal Concentrations (n=975) corrected for creatinine levels (μg/g) Stratified by recruitment center: Shamir and Rambam. Figure S1. Bivariate Exposure-Response Functions for z-standardized weight model (n = 975). Figure S2. Bivariate Exposure-Response Functions for z-standardized length model (n = 887). Figure S3. Bivariate Exposure-Response Functions for z-standardized head circumference model (n = 975). Table S2. BKMR Posterior Inclusion Probabilities (PIP) obtained for each metal from models of anthropometric measures including gestational age as an independent variable.
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Michael, T., Kohn, E., Daniel, S. et al. Prenatal exposure to heavy metal mixtures and anthropometric birth outcomes: a cross-sectional study. Environ Health 21, 139 (2022). https://doi.org/10.1186/s12940-022-00950-z
- Anthropometric Measures
- Prenatal Exposure