铁和锰的氧化和还原

W. Ghiorse
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引用次数: 0

摘要

微生物对铁和锰的氧化和还原对土壤科学家具有广泛的重要性(Alexander, 1977;Paul & Clark, 1989)。事实上,了解土壤和沉积物中铁和锰转化微生物的分布、丰度、特性和活性,可以极大地促进对各种农业和环境问题的研究,如铁和锰对植物的可利用性、金属积累、金属和农药的毒性和流动性、井堵塞和湿地排水系统。对铁和锰转化微生物生物学的了解可以为这些微生物的金属动员和固定化活动的未来应用提供条件,以实现经济和环境效益(Ehrlich & Brierley, 1990)。除了形态上可识别的“铁细菌”外,人们对自然界中发生的铁锰转化生物知之甚少。对它们在自然系统中的功能或控制它们在原地活动的因素所知就更少了。另一方面,已经分离出了几种模式生物,并对其进行了分类鉴定(例如,氧化亚铁硫杆菌、二甲细螺旋体、腐坏希瓦氏菌和金属还原地杆菌)。, 1993))。在某些情况下,已经研究了它们的铁和锰转化能力的生化机制。(评论见giorse 1984, 1988;Ehrlich, 1987,1990;Lovley, 1987, 1991;纳尔逊等人。1988年、1989年;Myers & Nealson, 1990;埃利希等人。, 1991;尼尔森和迈尔斯,1992)。一个持续存在的问题是难以区分非生物和生物介导的转化,特别是在土壤等环境中,微生物活动可能改变微环境的氧化还原化学,导致铁和锰通过直接或间接机制发生氧化还原变化(Ehrlich, 1990)。这些问题也适用于微生物培养基,在某些情况下,微生物培养基可能会因生长引起的pH或Eh或代谢产物的变化而改变,这些变化会导致铁和锰的化学氧化或还原。考虑到这些可能性
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Iron and Manganese Oxidation and Reduction
Microbial oxidation and reduction of Fe and Mn are of wide-ranging importance to soil scientists (Alexander, 1977; Paul & Clark, 1989). Indeed, knowledge of the distribution, abundance, identity, and activity of Feand Mn-transforming microbes in soils and sediments can greatly enhance studies on such diverse agricultural and environmental problems as Fe and Mn availability to plants, metal accumulation, toxicity and mobility of metals and pesticides, and clogging in wells and wetland drainage systems. Knowledge of the biology of Feand Mn-transforming microorganisms may allow for future applications in which the metal mobilization and immobilization activities of these microorganisms are exploited for economic and environmental benefit (Ehrlich & Brierley, 1990). Except for the morphologically recognizable "iron bacteria," relatively little is known of the occurrence of Fe-Mn-transforming organisms in nature. Even less is known of their function in natural systems or the factors controlling their in situ activities. On the other hand, several model organisms have been isolated and characterized taxonomically (e.g., Thiobacillus ferrooxidans, Leptothrix discophora, Shewanella putrefaciens, and Geobacter metallireducens (Lovley et aI., 1993)). In some cases, the biochemical mechanisms underlying their Feand Mn-transforming abilities have been investigated. (For reviews, see Ghiorse 1984, 1988; Ehrlich, 1987, 1990; Lovley, 1987, 1991; Nealson et aI., 1988, 1989; Myers & Nealson, 1990; Ehrlich et aI., 1991; Nealson & Myers, 1992). A persistent problem has been the difficulty of distinguishing abiotic from biologically mediated (biotic) transformations, especially in environments like soil where microbial activity may alter the redox chemistry of the microenvironment, causing Fe and Mn redox changes to occur by direct or indirect mechanism (Ehrlich, 1990). These problems also apply to microbial growth media which, in some instances, may be altered by growthinduced changes in pH or Eh or metabolic products that cause chemical oxidation or reduction of Fe and Mn. These possibilities are taken into
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