Chen Zhen, Mayer Lawrence M, Weston Donald P, Bock Michael J, Jumars Peter A
Darling Marine Center, University of Maine, Walpole 04573, USA.
Environ Toxicol Chem. 2002 Jun;21(6):1243-8.
Digestive systems of deposit and suspension feeders can be exposed to high concentrations of copper (Cu) by ingestion of contaminated sediments. We assessed a potential impact of this Cu exposure on digestive enzyme activities in a wide range of benthic organisms by monitoring enzyme activities in their gut fluids during in vitro titrations with dissolved Cu, which mimics Cu solubilization from sediments. Increasing Cu inhibited digestive protease activities at threshold values, which varied widely among organisms, from 8 microM for an echinoderm to 0.4 M for an echiuran. More Cu was required to inhibit proteases in guts containing higher amino acid concentrations because strong Cu-binding sites on amino acids prevent Cu interaction with the enzymatically active sites. Threshold Cu concentrations were similar for proteases, esterases, lipases, and alpha- and beta-glucosidases, suggesting the same inhibition mechanism. Copper was less effective at inhibiting enzymes at lower pH, suggesting that protons can compete with Cu ion for binding to enzymatically active sites or that enzyme conformation is less vulnerable to Cu inhibition at lower pH. These results lead to the counterintuitive conclusion that deposit feeders with low enzyme activity, low amino acid concentration, and high pH values are most vulnerable to harm from sedimentary Cu by this mechanism, although they solubilize less sedimentary Cu than their counterparts with high enzyme activity, high amino acid concentrations, and low gut pH. In general, digestive systems of echinoderms may therefore be more susceptible to Cu contamination than those of polychaetes, with various other phyla showing intermediate susceptibilities. If threshold Cu values are converted to solid-phase sedimentary Cu concentrations, the thresholds are at least consistent with Cu loadings that have been observed to lead to biological impacts in the field.
沉积食性和悬浮物食性生物的消化系统可能会因摄入受污染的沉积物而接触到高浓度的铜(Cu)。我们通过在体外滴定溶解铜的过程中监测它们肠道液中的酶活性,评估了这种铜暴露对多种底栖生物消化酶活性的潜在影响,该过程模拟了沉积物中铜的溶解。铜浓度增加会在阈值时抑制消化蛋白酶活性,这些阈值在不同生物之间差异很大,从棘皮动物的8微摩尔到螠虫的0.4摩尔不等。抑制含有较高氨基酸浓度肠道中的蛋白酶需要更多的铜,因为氨基酸上的强铜结合位点会阻止铜与酶活性位点相互作用。蛋白酶、酯酶、脂肪酶以及α-和β-葡萄糖苷酶的阈值铜浓度相似,表明抑制机制相同。在较低pH值下,铜抑制酶的效果较差,这表明质子可以与铜离子竞争结合酶活性位点,或者在较低pH值下酶的构象对铜抑制的敏感性较低。这些结果得出了一个与直觉相反的结论,即酶活性低、氨基酸浓度低且pH值高的沉积食性生物通过这种机制最容易受到沉积铜的伤害,尽管它们比酶活性高、氨基酸浓度高且肠道pH值低的同类生物溶解的沉积铜更少。因此,一般来说,棘皮动物的消化系统可能比多毛纲动物更容易受到铜污染,其他各种门类则表现出中等敏感性。如果将阈值铜值转换为固相沉积铜浓度,这些阈值至少与在野外观察到的导致生物影响的铜负荷一致。