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Distribution of metabolic characteristics among aerobic soil bacteria and implications for biotransformation of organic and metallic wastes .

机译:需氧土壤细菌代谢特性的分布及其对有机和金属废物生物转化的影响。

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摘要

Comingled organic and metallic pollutants challenge soil remediation efforts because of their distinct chemical and biological transformation behavior. Bioremediation of such wastes depends upon pollutant types, remediation endpoints, and microbial metabolism and habitat. This research examined relationships between habitat, cell physiology, and aerobic biotransformation of chromium and organics. It was hypothesized that the degree of soil attachment by culturable heterotrophic bacterial communities in the vadose zone correlates to chromium biosorption, reduction, and tolerance; cell surface properties; growth rate; and substrate affinity. Compared to weakly soil-associated communities, strongly-associated communities were expected to have slower growth and greater substrate affinity, hydrophobicity, and chromium tolerance. Community-level relationships were not expected to hold true at the population level, however. Instead, bacterial isolates were anticipated to exhibit cell surface properties and biotransformation behavior not necessarily linked to their original soil association or community. The research sought to identify the biotransformation potential of often-overlooked soil microorganisms and to assess their use in achieving low residual contaminant concentrations in comingled chromium wastes.;Serial elution was used to extract two variably-attached bacterial communities from noncontaminated vadose zone soil. Five microbial isolates were cultured from these consortia. Consortia and isolates were characterized with respect to: (1) cell surface hydrophobicity and charge, using solvent-, resin-, and titration-based tests; (2) the rate and extent of growth on yeast extract and salicylic acid, a model organic pollutant; (3) chromium toxicity under variable substrate conditions; (4) chromium reduction, measured via x-ray spectroscopy; and (5) the kinetics and extent of chromium biosorption.;As hypothesized, the easily-detached bacterial community (F1) was less hydrophobic than its counterpart (F3), but its isolates varied unpredictably in hydrophobicity. Furthermore, F1 exhibited faster Monod-type growth but lower affinity for yeast extract (micromax = 0.35 hr-1, Ks = 36.6 mg/L) than F3 (micromax = 0.30 hr-1, Ks = 12.2 mg/L), whereas its isolates showed growth variability. Salicylic acid generally produced non-Monod growth and increased apparent chromium toxicity. All isolates and consortia were able to sorb and reduce chromium, regardless of cell surface properties or original attachment. Chromium resistance was negatively correlated to substrate (yeast extract) affinity among isolates, positively correlated to the substrate affinity of consortia (as hypothesized), and independent of cell surface properties.
机译:混合的有机和金属污染物因其独特的化学和生物转化行为而对土壤修复工作提出了挑战。此类废物的生物修复取决于污染物的类型,修复终点以及微生物的代谢和栖息地。这项研究检查了栖息地,细胞生理以及铬和有机物的有氧生物转化之间的关系。假设渗流区内可培养的异养细菌群落对土壤的附着程度与铬的生物吸附,还原和耐受性有关。细胞表面特性;增长率;和底物亲和力。与弱土壤相关的群落相比,强相关的群落被期望具有较慢的生长和更大的底物亲和力,疏水性和铬耐受性。但是,社区一级的关系并不能在人口一级成立。取而代之的是,预期细菌分离株会表现出细胞表面特性和生物转化行为,而不一定与其原始土壤联系或群落有关。该研究旨在确定经常被忽视的土壤微生物的生物转化潜力,并评估其在实现混合铬废料中低残留污染物浓度方面的应用。;串行洗脱用于从无污染的渗滤带土壤中提取两个可变附着的细菌群落。从这些联合体培养了五个微生物分离株。财团和分离株的特征如下:(1)细胞表面疏水性和电荷,使用基于溶剂,树脂和滴定的测试; (2)在酵母提取物和水杨酸(一种典型的有机污染物)上的生长速率和程度; (3)可变底物条件下的铬毒性; (4)铬还原,通过X射线光谱法测量; (5)铬生物吸附的动力学和程度。如所假设的,易分离的细菌群落(F1)的疏水性低于其对应物(F3),但其分离物的疏水性发生了不可预测的变化。此外,与F3(micromax = 0.30 hr-1,Ks = 12.2 mg / L)相比,F1表现出更快的Monod型生长,但对酵母提取物的亲和力较低(micromax = 0.35 hr-1,Ks = 36.6 mg / L)。分离株显示出生长变异性。水杨酸通常会产生非Monod的生长并增加表观铬的毒性。所有分离物和社团都能够吸收和还原铬,而与细胞表面特性或原始附着无关。铬抗性与分离株之间的底物(酵母提取物)亲和力呈负相关,与联合体的底物亲和力呈正相关(如假设),并且与细胞表面特性无关。

著录项

  • 作者

    Zhang, Fangmei.;

  • 作者单位

    Case Western Reserve University.;

  • 授予单位 Case Western Reserve University.;
  • 学科 Biology Microbiology.;Engineering Environmental.
  • 学位 Ph.D.
  • 年度 2007
  • 页码 155 p.
  • 总页数 155
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

  • 入库时间 2022-08-17 11:39:09

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