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Protection of mesopore-adsorbed organic matter from enzymatic degradation

机译:保护中孔吸附的有机物免于酶降解

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Synthetic mesoporous alumina and silica minerals with uniform pore geometries, and their nonporous analogues were used to test the role of mineral mesopores (2-50 nm diameter) in protecting organic matter from enzymatic degradation in soils and sediments. Dihydroxyphenylalanine (L-DOPA), a model humic compound, was irreversibly sorbed to both mineral types. The surface area-normalized adsorption capacity was greater for the mesoporous minerals relative to their nonporous analogues. The degradation kinetics of free and mineral-sorbed L-DOPA by the enzyme laccase was monitored in a closed cell via oxygen electrode. Relative to freely dissolved L-DOPA, nonporous alumina-sorbed substrate was degraded, on average, 90% more slowly and to a lesser extent (93%), likely due to laccase adsorption to alumina. In contrast, relative to free L-DOPA, degradation of nonporous silica-sorbed L-DOPA was enhanced by 20% on average. In the case of mesoporous alumina and silica-sorbed L-DOPA, the enzyme activity was 3-40 times lower than that observed for externally sorbed substrate (i.e., L-DOPA sorbed to nonporous minerals). These results provide strong evidence to support the viability of the mesopore protection mechanism for sequestration and preservation of sedimentary organic matter and organic contaminants. Nanopore adsorption/desorption phenomena may aid in explaining the slow degradation of organic contaminants in certain soils and sediments and may have implications for environmental remediation and biotechnological applications.
机译:具有均匀孔几何结构的合成介孔氧化铝和二氧化硅矿物及其无孔类似物用于测试矿物介孔(直径2-50 nm)在保护有机物免受土壤和沉积物中酶促降解方面的作用。模范腐殖化合物二羟基苯丙氨酸(L-DOPA)不可逆地吸附到两种矿物类型。相对于无孔类似物,中孔矿物的表面积归一化吸附容量更大。酶漆酶通过氧电极监测了游离酶和矿物质吸附的L-DOPA的降解动力学。相对于自由溶解的L-DOPA,无孔氧化铝吸附的基质降解的平均速度要慢90%,而降解程度较小(93%),这可能是由于漆酶对氧化铝的吸附所致。相反,相对于游离的L-DOPA,无孔二氧化硅吸附的L-DOPA的降解平均提高了20%。在介孔氧化铝和二氧化硅吸附的L-DOPA的情况下,酶活性比外部吸附的底物(即L-DOPA吸附到无孔矿物上)的酶活性低3-40倍。这些结果提供了有力的证据来支持中孔保护机制用于隔离和保存沉积有机物和有机污染物的可行性。纳米孔吸附/解吸现象可能有助于解释某些土壤和沉积物中有机污染物的缓慢降解,并且可能对环境修复和生物技术应用产生影响。

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