Heavy metals in maternal and cord blood in Beijing and their efficiency of placental transfer
Graphical abstract
Introduction
Heavy metals are ubiquitous environmental pollutants, which results from industrial pollution, human activities, and natural combustion (Al-Saleh et al., 2011, Amaya et al., 2013). Dietary intake is the most common source of heavy metals for the general population (Amaya et al., 2013). Itai-Itai disease, which occurs in Japan, first brought global public attention to the problem of cadmium (Cd)-contaminated rice (Nogawa and Kido, 1993). In the US, several million people are suffering in arsenic (As) exposure of drinking water (Ayotte et al., 2011). The As concentration in these drinking water is above the US Environmental Protection Agency standard for As in drinking water systems (10 μg/L). Recently, low As exposure levels were reported to be associated with the risk of hyperuricemia in men and with the prevalence of gout in women (Kuo et al., 2015). However, for some heavy metals, such as vanadium (V) and stibium (Sb), their safe and adequate limit of intake is not known for humans (Imtiaz et al., 2015). To date, the adverse effect of heavy metals on human is gradually acknowledged because of their known and potential toxic properties.
Epidemiological evidence has demonstrated that some heavy metals exposure can dramatically affect adult fertility (Al-Saleh et al., 2008, Amaya et al., 2013, Kuo et al., 2015, Jin et al., 2016). Maternal blood lead (Pb) levels of approximately 100 μg/L would increase the risks of pregnancy hypertension and spontaneous abortion in pregnant women, and reduce neurobehavioral development in offspring (Bellinger, 2005). A recent study reported that Cd concentration in maternal blood was inversely associated with the birth weight of offspring in Bangladesh (Menai et al., 2012). Jin et al., (2014) conducted that high Cd level in pregnant women’ blood would increase the risk of neural tube defects in newborns.
The placenta is an important selective barrier to toxic compounds during pregnancy (Al-Saleh et al., 2011), however, some heavy metals can interfere with placental transport systems (Zhang et al., 2004) and then cross through the placenta (Osman et al., 2000). Because of differences between the fetus and adult in many biochemical pathways, the fetus is highly sensitive to chemicals or drugs, even at a very low exposure concentration (Wells et al., 2010). Therefore, there is a growing concern about the adverse effect on the fertility or fetal development even that the exposure level of heavy metals was much lower than international guidelines (Greet et al., 2006, Holmes et al., 2009, Al-Saleh et al., 2011). Furthermore, Mattison (2010) suggested that there were no thresholds for the effects of environmental exposure in utero or during early childhood.
To evaluate of the exposure of heavy metals exposure during pregnancy, maternal and/or cord samples was mainly used (Butler Walker et al., 2006, Amaya et al., 2013, Jin et al., 2014, Jin et al., 2016). Cord blood mercury levels are usually higher than that of maternal blood (Gundacker et al., 2010). Cord blood Pb levels are equal to or lower than maternal blood Pb levels (Ask et al., 2002, Al-Saleh et al., 2011), while cord blood Cd levels are always much lower than maternal blood Cd levels (Kantola et al., 2000, Al-Saleh et al., 2011). Currently, little is known about the features and mechanisms involved in heavy metal toxicokinetics through the placenta.
In this study, we conducted a pilot study of 156 pairs of maternal and cord blood samples that collected in Beijing, China. We aimed to characterize the occurrence, distribution, and placental transport of 10 heavy metals, including Pb, Cd, As, titanium (Ti), V, chrome (Cr), manganese (Mn), nickel (Ni), stannum (Sn), and Sb. Moreover, the association between each heavy metal and birth weight/length of newborns was investigated.
Section snippets
Subjects
All maternal and cord blood that was analyzed in this study was collected by staff at Beijing Obstetrics and Gynecology Hospital, Capital Medical University, China. These samples were obtained from 987 female volunteers who were hospitalized between November 2015 and December 2016 for parturition. The experimental protocol was approved by the Research Ethics Committee at all participating institutions, and informed consent of all participating subjects was obtained. General criteria for
Participants' characteristics
General characteristics of the 156 pairs of mothers and newborns are shown in Table 2. The age of the mothers ranged from 22 to 45 years, and 31 (20%) were older than 35 years. Of the 156 mothers, 122 (78%) had their first pregnancy. Of the 156 newborns, 17 (11%) were small for gestational age infants (gestational weeks, < 37), while the remaining 139 (89%) newborns were born following a normal number of weeks of pregnancy (37–41 weeks). Seventy-seven (49%) newborns were boys and 79 (51%) were
Conclusions
The present study showed widespread exposure to heavy metals in pregnant women in Beijing. Our results provide informative baseline biomonitoring data of heavy metal exposure in non-occupationally exposed pregnant women in Beijing. Moreover, the PTE data that were obtained in this study can help to evaluate the fetus's status in terms of heavy metal exposure at an earlier stage using maternal blood during pregnancy. Despite the finding that health risk assessment showed no potential concern for
Acknowledgment
This work was supported by the National Natural Science Foundation of China (No. 21677170) and the Strategic Priority Research Program of the Chinese Academy of Sciences (No. XDB14010300).
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These authors contributed equally to this work.