Restauración de suelos contaminados por medio de procesos microbiológicos y enzimáticos

L. Gianfreda, M. Mora, M. C. Diez
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引用次数: 11

Abstract

In the last years, a high number of highly toxic compounds have been released into theenvironment because of several industrial and/or agricultural activities. Typical organicchemicals include pesticides, fuels, solvents, alkanes, polycyclic aromatic hydrocarbons(PAHs), nitrogen and phosphorus compounds, explosives, and dyes while inorganiccontaminants are mainly represented by toxic heavy metals.Contamination of soil, surface and ground water by organic pollutants is a problem ofgreat environmental concern in several countries. Furthermore, a complex pollution includingmore than one pollutant and also toxic metals may accumulate in the environment thusbeing a point of major concern for both a toxicological risk assessment of contaminatedfield sites and to study the feasibility of bioremediation technologies to remediatecontaminated soils.Intrinsic biodegradation is one of the natural attenuation phenomena, which may occurat the contaminated soil and contribute to its remediation (Figure 1). Indeed, most of pollutingchemicals have been proven to be transformed by microbial organisms (Alexander, 1985;Cerniglia, 1992; Alexander, 1994). Their susceptibility to biodegradation may, however,change drastically, depending on several factors related to the chemical and physicalproperties of both the chemical and the environment in which they are present.Although much experimental evidence supports the capability of microorganisms tobiodegrade organic pollutants, several sites are still strongly contaminated, indicating ahigh persistence of these compounds under field conditions.Several strategies have been devised to remediate and restore polluted environments:physical and chemical methods and biological approaches, requiring the involvement ofbiological agents (Adriano et al., 1999; Alexander, 1985, 19994; Bollag and Liu, 1990; Bollagand Bollag, 1995; Bouwer and Zender, 1993; Cerniglia, 1992; Edgehill, 1999; Edgehill et al.,1991,Gevao et al., 2000;
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通过微生物和酶的过程修复受污染的土壤
在过去的几年里,由于一些工业和/或农业活动,大量剧毒化合物被释放到环境中。典型的有机化学品包括农药、燃料、溶剂、烷烃、多环芳烃(PAHs)、氮磷化合物、炸药、染料等,而无机污染物主要以有毒重金属为代表。有机污染物对土壤、地表水和地下水的污染是一些国家非常关注的环境问题。此外,包括一种以上污染物和有毒金属在内的复杂污染可能在环境中积累,因此对污染场地的毒理学风险评估和研究生物修复技术修复污染土壤的可行性都是一个主要关注的问题。内在生物降解是一种自然衰减现象,它可能发生在被污染的土壤中,并有助于其修复(图1)。事实上,大多数污染化学物质已被证明可以被微生物转化(Alexander, 1985;Cerniglia, 1992;亚历山大,1994)。然而,它们对生物降解的敏感性可能会发生巨大变化,这取决于与它们所处的化学品和环境的化学和物理性质有关的几个因素。尽管许多实验证据支持微生物生物降解有机污染物的能力,但一些地点仍然受到严重污染,表明这些化合物在野外条件下具有高持久性。已经制定了若干战略来修复和恢复被污染的环境:物理和化学方法以及需要生物制剂参与的生物方法(Adriano等人,1999年;亚历山大,1985,19994;Bollag and Liu, 1990;Bollagand Bollag, 1995;Bouwer and Zender, 1993;Cerniglia, 1992;Edgehill, 1999;Edgehill等,1991,Gevao等,2000;
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