Bergdahl I A, Schütz A, Ahlqwist M, Bengtsson C, Lapidus L, Lissner L, Hulten B
Department of Occupational and Environmental Medicine, Lund University, Sweden.
Environ Res. 1998 Apr;77(1):20-4. doi: 10.1006/enrs.1997.3820.
Methylmercury in serum (S-MeHg) was assessed from serum concentrations of total (S-TotHg) and inorganic mercury (S-InoHg), determined by cold vapor-atomic absorption spectrometry. The samples were collected from 135 women on two occasions, in 1968-1969 and 1980-1981. In a subgroup of 29 women, an association was found between S-MeHg and the amount of fish consumed in 1968-1969 (r = 0.38, P = 0.04). The association was stronger (r = 0.50; P = 0.006) when the individuals' mean S-MeHg from 1968-1969 and 1980-1981 were plotted vs fish consumption 1968-1969. In the group, as a whole, there was an association between S-InoHg and number of dental amalgam surfaces, in both 1968-1969 (r = 0.48, P = 0.0001) and 1980-1981 (r = 0.57, P < 0.0001). The S-InoHg increased by approximately 0.1 nmol/L per amalgam tooth surface, corresponding to an uptake of approximately 0.2 microgram/day per amalgam surface, but with considerable interindividual differences. The levels were lower in 1980-1981 than in 1968-1969 for both MeHg and InoHg. The medians and ranges (nmol/L) were for MeHg 1968-1969: 3.6 (0.3-11.9); MeHg 1980-1981, 2.0 (-0.4-8.7); InoHg 1968-1969, 3.3 (0.7-11.8); InoHg 1980-1981, 1.7 (0.1-11.8); TotHg 1968-1969, 7.2 (1.9-18.8); and TotHg 1980-1981, 3.9 (1.0-14.2). The decrease in S-MeHg is probably due to a decreased consumption of MeHg via contaminated fish. The decrease in S-InoHg may reflect a decrease in environmental exposure, but the possibility of contamination of the 1968-1969 samples at sampling and/or storage cannot be excluded.
血清甲基汞(S-MeHg)通过冷蒸气原子吸收光谱法测定血清总汞(S-TotHg)和无机汞(S-InoHg)的浓度来评估。在1968 - 1969年和1980 - 1981年分两次从135名女性中采集样本。在29名女性的亚组中,发现1968 - 1969年的S-MeHg与鱼类摄入量之间存在关联(r = 0.38,P = 0.04)。当绘制1968 - 1969年和1980 - 1981年个体的平均S-MeHg与1968 - 1969年鱼类消费量的关系图时,这种关联更强(r = 0.50;P = 0.006)。在整个组中,1968 - 1969年(r = 0.48,P = 0.0001)和1980 - 1981年(r = 0.57,P < 0.0001),S-InoHg与银汞合金补牙面数量之间均存在关联。每增加一个银汞合金补牙面,S-InoHg大约增加0.1 nmol/L,相当于每个银汞合金表面每天摄取约0.2微克,但个体差异较大。1980 - 1981年甲基汞和无机汞的水平均低于1968 - 1969年。1968 - 1969年甲基汞的中位数和范围(nmol/L)为:3.6(0.3 - 11.9);1980 - 1981年甲基汞为2.0(-0.4 - 8.7);1968 - 1969年无机汞为3.3(0.7 - 11.8);1980 - 1981年无机汞为1.7(0.1 - 11.8);1968 - 1969年总汞为7.2(1.9 - 18.8);1980 - 1981年总汞为3.9(1.0 - 14.2)。S-MeHg的下降可能是由于通过受污染鱼类摄入的甲基汞减少。S-InoHg的下降可能反映了环境暴露的减少,但不能排除1968 - 1969年样本在采样和/或储存过程中受到污染的可能性。