Zimmerman Andrew R, Kang Dong-Hee, Ahn Mi-Youn, Hyun Seunghun, Banks M Katherine
Department of Geological Sciences, University of Florida, 241 Williamson Hall, P.O. Box 112120, Gainesville, FL 32611, USA.
Chemosphere. 2008 Jan;70(6):1044-51. doi: 10.1016/j.chemosphere.2007.07.075. Epub 2007 Sep 12.
Cyanide is commonly found as ferrocyanide Fe(II)(CN)(6) and in the more mobile form, ferricyanide Fe(III)(CN)(6) in contaminated soils and sediments. Although soil minerals may influence ferrocyanide speciation, and thus mobility, the possible influence of soil enzymes has not been examined. In a series of experiments conducted under a range of soil-like conditions, laccase, a phenoloxidase enzyme derived from the fungi Trametes versicolor, was found to exert a large influence on iron-cyanide speciation and mobility. In the presence of laccase, up to 93% of ferrocyanide (36-362ppm) was oxidized to ferricyanide within 4h. No significant effect of pH (3.6 and 6.2) or initial ferrocyanide concentration on the extent or rate of oxidation was found and ferrocyanide oxidation did not occur in the absence of laccase. Relative to iron-cyanide-mineral systems without laccase, ferrocyanide adsorption to aluminum hydroxide and montmorillonite decreased in the presence of laccase and was similar to or somewhat greater than that of ferricyanide without laccase. Laccase-catalyzed conversion of ferrocyanide to ferricyanide was extensive though up to 33% of the enzyme was mineral-bound. These results demonstrate that soil enzymes can play a major role in ferrocyanide speciation and mobility. Biotic soil components must be considered as highly effective oxidation catalysts that may alter the mobility of metals and metal complexes in soil. Immobilized enzymes should also be considered for use in soil metal remediation efforts.
氰化物在受污染的土壤和沉积物中通常以亚铁氰化物Fe(II)(CN)(6)的形式存在,且以更具流动性的铁氰化物Fe(III)(CN)(6)形式存在。尽管土壤矿物质可能影响亚铁氰化物的形态,进而影响其流动性,但土壤酶的潜在影响尚未得到研究。在一系列类似土壤条件下进行的实验中,发现漆酶(一种源自云芝的酚氧化酶)对铁氰化物的形态和流动性有很大影响。在漆酶存在的情况下,4小时内高达93%的亚铁氰化物(36 - 362ppm)被氧化为铁氰化物。未发现pH值(3.6和6.2)或初始亚铁氰化物浓度对氧化程度或速率有显著影响,且在没有漆酶的情况下不会发生亚铁氰化物氧化。相对于没有漆酶的铁氰化物 - 矿物体系,在漆酶存在下,亚铁氰化物在氢氧化铝和蒙脱石上的吸附减少,且与没有漆酶时铁氰化物的吸附相似或略高。漆酶催化的亚铁氰化物向铁氰化物的转化很广泛,尽管高达33%的酶与矿物结合。这些结果表明,土壤酶在亚铁氰化物的形态和流动性方面可能起主要作用。必须将生物土壤成分视为可能改变土壤中金属和金属络合物流动性的高效氧化催化剂。在土壤金属修复工作中也应考虑使用固定化酶。