U.S. Geological Survey, Western Ecological Research Center, Davis Field Station, University of California-Davis, Davis, California 95616, USA.
Environ Sci Technol. 2011 Jun 15;45(12):5418-25. doi: 10.1021/es200647g. Epub 2011 May 18.
Toxicological risk of methylmercury exposure to juvenile birds is complex due to the highly transient nature of mercury concentrations as chicks age. We examined total mercury and methylmercury concentrations in blood, liver, kidney, muscle, and feathers of 111 Forster's tern (Sterna forsteri), 69 black-necked stilt (Himantopus mexicanus), and 43 American avocet (Recurvirostra americana) chicks as they aged from hatching through postfledging at wetlands that had either low or high mercury contamination in San Francisco Bay, California. For each waterbird species, internal tissue, and wetland, total mercury and methylmercury concentrations changed rapidly as chicks aged and exhibited a quadratic, U-shaped pattern from hatching through postfledging. Mercury concentrations were highest immediately after hatching, due to maternally deposited mercury in eggs, then rapidly declined as chicks aged and diluted their mercury body burden through growth in size and mercury depuration into growing feathers. Mercury concentrations then increased during fledging when mass gain and feather growth slowed, while chicks continued to acquire dietary mercury. In contrast to mercury in internal tissues, mercury concentrations in chick feathers were highly variable and declined linearly with age. For 58 recaptured Forster's tern chicks, the proportional change in blood mercury concentration was negatively related to the proportional change in body mass, but not to the amount of feathers or wing length. Thus, mercury concentrations declined more in chicks that gained more mass between sampling events. The U-shaped pattern of mercury concentrations from hatching to fledging indicates that juvenile birds may be at highest risk to methylmercury toxicity shortly after hatching when maternally deposited mercury concentrations are still high and again after fledging when opportunities for mass dilution and mercury excretion into feathers are limited.
由于幼鸟体内汞浓度的高度瞬时变化,甲基汞暴露对幼鸟的毒理学风险较为复杂。我们研究了在加利福尼亚州旧金山湾低汞和高汞污染湿地中,111 只蛎鹬(Sterna forsteri)、69 只黑颈长脚鹬(Himantopus mexicanus)和 43 只美洲鹈鹕(Recurvirostra americana)雏鸟从孵化到离巢这段时间内血液、肝脏、肾脏、肌肉和羽毛中的总汞和甲基汞浓度。对于每种水鸟物种、内部组织和湿地,总汞和甲基汞浓度随着雏鸟的生长而迅速变化,并在孵化到离巢期间呈现出二次、U 形模式。由于卵中母体沉积的汞,雏鸟刚孵化出来时体内的汞浓度最高,然后随着雏鸟的生长,其体重增加,体内的汞含量被稀释,通过生长和向生长中的羽毛中排出汞来降低体内的汞含量。然后,在离巢期间,当体重增加和羽毛生长减缓时,汞浓度会增加,而雏鸟仍在通过饮食摄入汞。与内部组织中的汞不同,雏鸟羽毛中的汞浓度变化很大,且随着年龄的增长呈线性下降。对于 58 只重新捕获的蛎鹬雏鸟,血液中汞浓度的比例变化与体重的比例变化呈负相关,但与羽毛量或翼展长度无关。因此,在两次采样之间体重增加较多的雏鸟体内的汞浓度下降幅度更大。从孵化到离巢期间汞浓度的 U 形模式表明,幼鸟在刚孵化时可能面临最高的甲基汞毒性风险,此时母体沉积的汞浓度仍然很高,在离巢后再次面临风险,此时体重稀释和将汞排入羽毛的机会有限。