Correlations between mercury concentrations in umbilical cord tissue and other biomarkers of fetal exposure to methylmercury in the Japanese population
Introduction
Fetuses are known to be a high-risk group for methylmercury (MeHg) exposure because of the high susceptibility of the developing brain itself (Choi, 1989; Sakamoto et al., 1993; World Health Organization (WHO), 1990). Moreover, MeHg easily crosses the blood–placenta barrier, accumulating more in the fetus than the mother (Choi, 1989; Sakamoto et al., 2002, Sakamoto et al., 2004; Stern and Smith, 2003; WHO, 1990). Therefore, the effect of MeHg exposure on pregnant women is an important issue for elucidation, especially in Japanese and some other populations that consume much fish and sea mammals (Grandjean, 1997, Grandjean, 2005; Myers et al., 1995a, Myers et al., 1995b, Myers et al., 2003; National Research Council (NRC), 2000; WHO, 1990).
The epidemic called “Minamata disease” is well known as the first instance on record of severe MeHg poisoning caused by manmade environmental pollution, which occurred mainly among fishermen and their families in and around Minamata City. It originated from the consumption of large amounts of fish and shellfish contaminated with MeHg discharged from a chemical plant (Irukayama and Kondo, 1966). The principal symptoms included neurological disorders such as sensory disorders, cerebellar ataxia, contraction of the visual field, hearing impairments, and disequilibrium (Takeuchi et al., 1962). The first patient was reported in 1953, and the number of patients rapidly increased after 1955. Up to the present, more than 2000 people have been certified to have Minamata disease. Furthermore, many fetuses exposed to MeHg through the placenta of the exposed mother showed severe cerebral-palsy-like symptoms, while their mothers had mild or no manifestation of the poisoning (Harada, 1978). Outbreaks of the typical fetal-type Minamata disease occurred during 1955–1959 when the mercury pollution appears to have been most severe, judging from the incidence of patients (Harada, 1978) and the MeHg concentration in the preserved umbilical cords of inhabitants of the area (Nishigaki and Harada, 1975). During the period, a deceased male birth ratio associated with increased male fetal death was observed in Minamata City pollution, indicating its severity and widespread distribution (Sakamoto et al., 2001). This landmark epidemic was the first to bring worldwide attention to the high risk of fetal exposure to MeHg.
Thereafter, large prospective cohort studies were conducted in the Seychelles (Myers et al., 1995a, Myers et al., 1995b, Myers et al., 2003) and the Faroe Islands (Grandjean, 1997, Grandjean, 1999, Grandjean, 2005), where fish or sea mammal consumption is high. Though the MeHg exposure level was similar in these studies, different conclusions were reached (NRC, 2000). The exposure level in the epidemic in Minamata is thought to have been much higher than in those studies. Therefore, the study of Minamata disease is still very important, and it will provide more obvious health effect information by using recently developed neurological test batteries. Fortunately, Japanese people have a custom of preserving a small piece of the dried umbilical cord tissue as a birth memento in a wooden or plastic box deep inside a chest of drawers. MeHg in the tissue will not be reduced by microorganisms, because it is completely dried. By measuring the Hg concentrations in this preserved dry cord sample, we can estimate the individual MeHg exposure level at birth. Grandjean et al. (2005) revealed that cord tissue Hg as well as cord blood Hg was useful as a predictor of the effect of fetal exposure to MeHg. However, the preserved cord tissues had often been treated with mercurochrome at the period when cut off at parturition. The mercurochrome can easily dissociate into Hg ions in the solution and the ions act as a disinfectant. Then the cord tissue treated with mercurochrome shows a very high Hg concentration when total mercury (THg) is measured. Accordingly, we need to measure not THg but MeHg in the preserved cord tissue in Japan, especially in the samples treated back in those days. Some studies (Akagi et al., 1998; Nishigaki and Harada, 1975) have revealed exposure of the fetus to MeHg in the Minamata area by measuring it in the preserved cord tissue. The present study investigates the relationships between THg and MeHg in cord tissue and the relationships between other biomarkers of fetal exposure to MeHg in the Japanese population to evaluate the significance of the Hg concentrations in cord tissue.
Section snippets
Subjects and sampling
In total, 116 healthy Japanese pregnant women without any special exposure to mercury, ranging in age from 19 to 41 yr (average 30.0±5.0), gave informed consent to take part in the present trial. The samples were collected in the Tsushima Islands in Nagasaki Prefecture (30 cases), Fukuoka City in Fukuoka Prefecture (68 cases) and Katsushika, a special ward of metropolitan Tokyo (18 cases). Blood samples from the mothers and umbilical cord were collected immediately after birth in 1996. Whole
Results
Table 1 presents the geometric means of THg in hair and THg and MeHg in cord tissue, maternal blood, and cord blood in three districts in Japan. There were significant differences among the districts in all the Hg concentrations (). The geometric means of Hg concentrations in all tissues were highest in Katsushika ward of metropolitan Tokyo, followed by Fukuoka City and the Tsushima Islands. All the data were combined, because similar correlations were observed among the Hg concentrations
Discussion
MeHg is one of the most risky substances for the fetal brain, and most of the human exposure to MeHg is through maternal fish consumption. MeHg easily passes through the placenta as a cysteine conjugate during intrauterine life (Aschner and Clarkson, 1987; Kajiwara et al., 1996). The National Research Council (NRC, 2000) recommended cord blood Hg as the best biomarker for fetal exposure to MeHg. In addition, cord tissue Hg concentration was revealed to be useful as a predictor of the effect of
Acknowledgments
A part of this work was supported by a grant for Comprehensive Research of Minamata Disease from the Ministry of Environment, Japan.
This study was approved by the Ethics Committee of the National Institute for Minamata Disease (No. 19-55-4 NIMD).
References (34)
- et al.
Methylmercury dose estimation from umbilical cord concentrations in patients with Minamata disease
Environ. Res.
(1998) - et al.
Health assessment for mercury exposure among schoolchildren residing near a gold processing and refining plant in Apokon, Tagum, Davao del Norte, Philippines
Sci. Total Environ.
(2000) The effects of methylmercury on the developing brain
Prog. Neurobiol.
(1989)- et al.
Comparative aspects of the brain growth spurt
Early Hum. Dev.
(1979) - et al.
Cognitive deficit in 7-year-old children with prenatal exposure to methylmercury
Neurotoxicol. Teratol.
(1997) - et al.
Prenatal methylmercury exposure from ocean fish consumption in the Seychelles child development study
Lancet
(2003) - et al.
Effects of methyl mercury in postnatal developing rats
Environ. Res.
(1993) - et al.
Declining Minamata male birth ratio associated with increased male fetal death due to heavy methylmercury pollution
Environ. Res.
(2001) - et al.
Declining risk of methylmercury exposure to infants during lactation
Environ. Res.
(2002) - et al.
Methyl mercury pharmacokinetics in man: a reevaluation
Toxicol. Appl. Pharmacol.
(1996)
Fish as a source of exposure to mercury and selenium
Sci. Total Environ.
Mercury 203 distribution in pregnant and nonpregnant rats following systemic infusions with thiol-containing amino acids
Teratology
Study of intrinsic flow properties at the normal pregnancy second trimester
Clin. Hemorheol. Microcirc.
Effects of hair treatment on hair mercury—the best biomarker of methylmercury exposure?
Environ. Health Prev. Med.
Mercury in the umbilical cord: implications for risk assessment for Minamata disease
Environ. Health Perspect.
Methylmercury exposure biomarkers as indicators of neurotoxicity in children aged 7 years
Am. J. Epidemiol.
Umbilical cord mercury concentration as biomarker of prenatal exposure to methylmercury
Environ. Health Perspect.
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