Axtell C D, Cox C, Myers G J, Davidson P W, Choi A L, Cernichiari E, Sloane-Reeves J, Shamlaye C F, Clarkson T W
Department of Biostatistics, University of Rochester School of Medicine and Dentistry, Rochester, New York 14642, USA.
Environ Res. 2000 Oct;84(2):71-80. doi: 10.1006/enrs.2000.4082.
Studies to date of the developmental effects of pre- and postnatal methylmercury exposure from fish consumption in the Seychelles Islands, using linear regression models for analysis, have not shown adverse effects on neurodevelopmental test scores. In this study we evaluated whether nonlinear effects of methylmercury exposure were present, using scores on six tests administered to cohort children in the Seychelles Child Development Study at 66 months of age. Prenatal exposure was determined by measuring mercury in a segment of maternal scalp hair representing growth during pregnancy. Postnatal exposure was measured in a segment of the child's hair taken at 66-months of age. Generalized additive models (GAMs), which make no assumptions about the functional form of the relationship between exposure and test score, were used in the analysis. GAMs similar to the original linear regression models were used to reanalyze the six primary developmental endpoints from the 66-month test battery. Small nonlinearities were identified in the relationships between prenatal exposure and the Preschool Language Scale (PLS) Total score and Child Behavior Check List (CBCL) and between postnatal exposure and the McCarthy General Cognitive Index (GCI) test scores. The effects are best described graphically but can be summarized by computing the change in the predicted test score from 0 to either 10 or 15 ppm and then above this point. For the PLS the trend involved a decline of 0.8 points between 0 and 10 ppm followed by an increase (representing improvement) of 1.3 points above 10 ppm. For the CBCL there was an increase of 1 point from 0 to 15 ppm, and then a decline (improvement) of 4 points above 15 ppm. The GCI increased by 1.8 points through 10 ppm and then declined 3.2 points (representing worse performance) above 10 ppm. These results are not entirely consistent. Two of the trends involve what appear to be beneficial effects of prenatal exposure. The one possibly adverse trend involves postnatal exposure. In every case the trend changes direction, so that an effect in one direction is followed by an effect in the opposite direction. Because of the descriptive nature of GAMs it is difficult to provide a precise level of statistical significance for the estimated trends. Certainly above 10 ppm there is less data and trends above this level are estimated less precisely. Overall there was no clear evidence for consistent (across the entire range of exposure levels) adverse effects of exposure on the six developmental outcomes. Further nonlinear modeling of these data may be appropriate, but there is also the risk of fitting complex models without a clear biological rationale.
迄今为止,在塞舌尔群岛开展的关于食用鱼类导致的产前和产后甲基汞暴露对发育影响的研究,使用线性回归模型进行分析,尚未显示对神经发育测试分数有不良影响。在本研究中,我们利用塞舌尔儿童发育研究中对队列儿童在66个月大时进行的六项测试的分数,评估甲基汞暴露是否存在非线性效应。通过测量代表孕期生长的母亲一段头皮头发中的汞来确定产前暴露。产后暴露则通过测量儿童66个月大时的一段头发来测定。分析中使用了广义相加模型(GAM),该模型对暴露与测试分数之间关系的函数形式不做任何假设。与原始线性回归模型类似的GAM被用于重新分析66个月测试组中的六个主要发育终点。在产前暴露与学前语言量表(PLS)总分及儿童行为检查表(CBCL)之间的关系以及产后暴露与麦卡锡一般认知指数(GCI)测试分数之间的关系中发现了小的非线性。这些效应最好用图形来描述,但可以通过计算预测测试分数从0到10或15 ppm然后高于此点的变化来总结。对于PLS,趋势是在0到10 ppm之间下降0.8分,然后在高于10 ppm时上升(代表改善)1.3分。对于CBCL,从0到15 ppm增加1分,然后在高于15 ppm时下降(改善)4分。GCI在10 ppm之前增加1.8分,然后在高于10 ppm时下降3.2分(代表表现更差)。这些结果并不完全一致。其中两个趋势涉及产前暴露似乎有有益影响。唯一可能不利的趋势涉及产后暴露。在每种情况下,趋势都会改变方向,即一个方向的效应之后是相反方向的效应。由于GAM的描述性质,很难为估计的趋势提供精确的统计显著性水平。当然,高于10 ppm的数据较少,高于此水平的趋势估计得不太精确。总体而言,没有明确证据表明暴露在六个发育结果上存在一致的(在整个暴露水平范围内)不良影响。对这些数据进行进一步的非线性建模可能是合适的,但也存在在没有明确生物学原理的情况下拟合复杂模型的风险。