生物冶金中耐盐浸矿微生物的研究进展

耐盐浸矿微生物是指在发挥矿物浸出功能时对所处的含盐环境具有一定耐受能力的一类浸矿微生物。耐盐浸矿微生物因其可以适应不同浓度的氯化钠等盐,因而在淡水资源缺乏地区的生物冶金中具有广泛的应用价值。本文从耐盐浸矿微生物的种类、耐盐机制及其在矿物生物浸出中的应用现状进行了系统性综述,为耐盐浸矿微生物的研究和应用提供参考。     

基于基因芯片对微生物基因功能与群落结构分析的硫化矿生物浸出分析

生物冶金技术因具有流程短、成本低、环境友好, 且特别适合处理低品位、复杂、难处理的矿产资源等优点,已经成为研究热点。然而由于缺少高效菌种以及不能对浸矿体系微生物进行定量分析, 难以对浸矿工艺参数和微生物种群进行优化调控, 从而导致硫化矿生物浸出速度慢、浸出率低。随着基因芯片、菌种保存技术的发展, 这些难题在逐一被解决。对近年来针对硫化矿浸出过程微生物的基因功能与群落结构分析的研究进行了概述, 将帮助我们更好地了解基因组学与生物冶金技术结合的重要作用。     

基于基因芯片对微生物基因功能与群落结构分析的硫化矿生物浸出分析

生物冶金技术因具有流程短、成本低、环境友好, 且特别适合处理低品位、复杂、难处理的矿产资源等优点,已经成为研究热点。然而由于缺少高效菌种以及不能对浸矿体系微生物进行定量分析, 难以对浸矿工艺参数和微生物种群进行优化调控, 从而导致硫化矿生物浸出速度慢、浸出率低。随着基因芯片、菌种保存技术的发展, 这些难题在逐一被解决。对近年来针对硫化矿浸出过程微生物的基因功能与群落结构分析的研究进行了概述, 将帮助我们更好地了解基因组学与生物冶金技术结合的重要作用。     

国内某低品位难选铜矿的生物浸出研究

目的:微生物湿法冶金技术是一种有效回收难处理常规选矿方法难以处理的复杂矿中金属的方法,本研究旨在利用该工艺处理国内某低品位(0.67%)难选铜矿,提高铜的回收率。方法:首先,从某矿山富集得到中温富集物,其次,对该矿石进行生物浸出,同时优化浸出过程工艺参数。结果:所富集得到的中温富集物最适生长温度为30℃,最适pH值为1.9。在摇瓶中浸出难选铜矿时,最佳摇床转速为180 r/min,最优充气强度为360 mL/min,10天内难选铜矿中铜的浸出率可以达到92%。结论:该中温富集物具有较好地浸出难选铜矿的能力。     

金属矿物细菌浸出现状

金属矿床开采过程中,总有大量不够开采品位的废石被舍弃。这些废石虽然金属含量极低,伹数量巨大,是不可忽视的金属资源。用细菌浸出法可以回收其中的有用金属。世界许多国家对细菌浸出十分重视,已用于铜、铀的露天矿废石堆、地下采空区和废矿井,成为这两种金属的重要来源之一。据统计,现在全     

镉锌超积累植物伴矿景天焚烧飞灰的重金属浸出特性及安全处置

为探究超积累植物伴矿景天焚烧灰浸出回收有价金属的可行性,以800℃流化床焚烧旋风灰为材料,研究盐酸、硝酸、氯化铵以及不同浓度、液固比和浸出时间对飞灰中重金属浸出规律的影响,同时评价浸出残渣的安全性.结果 表明:浸提剂种类、浓度及液固比是影响浸出的重要参数,浸出时间的影响较小,酸性浸提剂浸出能力明显强于氯化铵盐溶液浸出;...     

嗜酸嗜热浸矿微生物

随着人们对浸矿菌的研究不断加深,嗜热嗜酸菌的浸矿潜力及在微生物冶金中的作用和地位得到认识,利用嗜热菌对矿石进行高效浸出已成为微生物冶金领域的研究重点。嗜热微生物包括中度嗜热微生物和极端嗜热微生物,主要栖息于热泉、工厂高温废水排放区以及火山口等高温环境中。本综述总结了嗜热浸矿微生物种类,分析了嗜中温菌和极端嗜热菌等嗜酸菌种的生长习性、利用的能源物质、浸矿能力等,并进一步介绍了嗜热嗜酸微生物在高温生物冶金中的发展及应用。     

嗜热微生物及在高温生物冶金过程中的应用

嗜热微生物包括中度嗜热微生物和极端嗜热微生物,主要栖息于热泉、火山口、海底热液喷口、高温反应器以及工厂高温废水排放区等自然或人为产生的高温环境中。它们可以生活在40-80°C、甚至更高的温度中,其中有些具备嗜酸性及特殊的代谢类型,在高温生物冶金过程中具有应用潜力。高温生物冶金较传统中温生物冶金更具优势,其能浸出某些难处理矿、解决浸矿过程的钝化问题,以及提高浸出效率等,目前已引起了生物冶金工业的重视。本文概述了应用于生物冶金的主要嗜热微生物的生理特点、耐热机制以及对铁、铜和砷等离子的耐受机制,进一步介绍了嗜热微生物在高温生物冶金中的发展及应用。     

金的微生物浸出和回收

金是最稳定的元素之一。它常和银,铜以及其他微量元素结合。在化合物中,常见一价和三价金。金的三价化合物较稳定。在碱性条件下,一价金离子可与含有氧和硫的配位基形成可溶于水的复合物,该复合物在岩石圈的表面层易流动。在一定的条件下,金的溶解、迁移和沉淀是由微生物的作用产生的。金在自然界的复杂循环过程中,微生物起着重要的作用。由于微生物和金有密切的关系,在黄金工业中,人们有可能多方面的利用微生物。例如:加拿大温哥华基因探针有限公司研制了探测金矿的微生物探测器^[1];加拿大、南非和美国巳用微生物预处理难浸含砷命矿,提高了金的浸出率^[2]。本文仅就国外用微生物从矿石中直接浸出和从溶液中回收金的研究现状作一简要介绍。     

异养微生物在金属生物淋滤技术中的应用

生物淋滤技术主要应用于低品位矿石金属选矿、煤气脱硫、废弃物中金属回收和污染介质中金属离子毒性的去除等方面。作为生物淋滤技术中的主体微生物之一,异养微生物可通过其产生的酸性代谢物还原、酸化及络合,提取或者溶解非硫化矿、固体废弃物、污水污泥及土壤中的金属,有助于解决目前的资源短缺问题,还可对污染环境治理提供技术支持,具有重要的理论意义和实践价值。应用于异养微生物淋滤技术中的常见微生物包括细菌(以假单胞菌为主)和真菌(以曲霉菌和青霉菌应用最为广泛)。淋滤过程涉及酸解、络合、还原及碱化等。目前,异养微生物淋滤技术主要应用于生物冶金、固体废弃物处理、污水处理和污染土壤修复等。本文分析了异养微生物金属淋滤过程中的问题,并提出了未来研究的发展方向。     

Microbial leaching of metals from solid industrial wastes

Biotechnological applications for metal recovery have played a greater role in recovery of valuable metals from low grade sulfide minerals from the beginning of the middle era till the end of the twentieth century. With depletion of ore/minerals and implementation of stricter environmental rules, microbiological applications for metal recovery have been shifted towards solid industrial wastes. Due to certain restrictions in conventional processes, use of microbes has garnered increased attention. The process is environmentally-friendly, economical and cost-effective. The major microorganisms in recovery of heavy metals are acidophiles that thrive at acidic pH ranging from 2.0–4.0. These microbes aid in dissolving metals by secreting inorganic and organic acids into aqueous media. Some of the well-known acidophilic bacteria such as Acidithiobacillus ferrooxidans, Acidithiobacillus thiooxidans, Leptospirillum ferrooxidans and Sulfolobus spp. are well-studied for bioleaching activity, whereas, fungal species like Penicillium spp. and Aspergillus niger have been thoroughly studied for the same process. This mini-review focuses on the acidophilic microbial diversity and application of those microorganisms toward solid industrial wastes.     

Treatment of metal-contaminated wastes: why select a biological process?

Nature has demonstrated some subtle and intricate mechanisms for selectively controlling the mobility of metal pollutants in the environment. However, the application of this science to technology has been disappointing. A small number of pilot-plant studies have been carried out to investigate the potential of microorganisms (primarily bacteria) to remove metals from liquid wastes but only one system in the past 15 years has been commercialized. In order to explain this lack of application, it is important to understand the effectiveness, robustness and reliability of biological processes involving metals and their ability to compete with proven physicochemical technologies.     

Bio-Acidification and Leaching of Metals,Nitrogen, and Phosphorus from Soil and Sludge Mixtures

Soil and wastewater treatment sludge are commonly brought together in mixtures for a variety of beneficial purposes. The mixtures contain bioacidifying (i.e., sulfur-oxidizing) microorganisms that can easily be activated through providing the appropriate substrate and environmental conditions. In this study, contaminated soil and sludge mixtures were subjected to controlled bio-acidification and the impacts of the process on the partitioning of heavy metals, nitrogen, and phosphorus were examined. Three successive bio-acidification cycles resulted in significant leaching of metals from sludge. The leaching results, expressed as fraction of total mass of metals in the sludge, averaged 67% for Cr, 96% for Ni, 24% for Zn; 16% for Cu; 23% for Cd; and 96% for Pb. Bio-acidification of the sludge also converted 28 to 45% of the organic nitrogen into ammonia and increased the soluble orthophosphates fraction of total phosphorus by approximately 18 to 20%. Bio-acidification also resulted in significant metals leaching from the contaminated soils in the soil/sludge mixtures. Soil/sludge mixtures were prepared using six soil particle sizes (less than 0.075?mm to 2.38?mm) contaminated with 22,500?mg/kg Zn, 14,000?mg/kg Pb, 1500?mg/kg Cr, 9500?mg/kg Cu, 1000?mg/kg Ni, and 1000?mg/kg Cd. The addition of metals to the soil inhibited the sulfur-oxidizing microorganisms, preventing bio-acidification in the mixtures containing 4 to 50?g soil in 130?ml sludge, and considerably slowing bio-acidification in the mixtures containing 1 to 3?g soil. Using a mixture that contained 2-g soil samples, three successive bio-acidification cycles resulted in significant cumulative metals leaching results. The leaching results, expressed as percentage of the mass of metals added to the soil, were in the range of 56 to 98% for Cr, 77 to 95% for Zn, 33 to 66% for Ni, 64 to 82% for Cu, and 10 to 33% for Pb, with the higher results in each range belonging to the larger size soil particles. On the other hand, only Cr was leached in neutralized soil samples. The results confirmed the potential for inhibition of the sulfur-oxidizing microorganisms and bio-acidification in contaminated soil/sludge mixtures, and the significant impacts of bio-acidification on the mobility of metals, nitrogen, and phosphorus. In addition, the results confirmed the potential for using controlled bioacidification for removing heavy metals from contaminated soil using the indigenous sulfur oxidizing microorganisms in sludge.     

有机肥连续施用对菜田重金属行为的影响——基于地球化学模型研究

2017年起,农业部连续多年出台化肥减量增效行动工作方案,要求适当增加有机肥投入,发展循环农业。但连续施用的有机肥进入土壤后,会对土壤pH、有机质和重金属含量等产生影响,改变土壤重金属行为。科学评估有机肥料施用的影响至关重要。仅通过总含量评估重金属污染风险被认为是片面的,不同化学提取剂提取的重金属含量不能完全代表实际污染状况。地球化学模型具有良好的适用性,比传统的提取方法能够更全面地解释重金属的行为。在集约化农业种植区黄淮海平原,多次施用不同比例的粪源有机肥于旱地菜田,并引入地球化学模型,结合pH依赖性浸出试验,明确连续施肥对菜田土壤重金属行为的主要影响机制。研究发现,有机肥中的铜锌含量远高于土壤中的含量,施用后,它们在土壤中的淋溶浓度随着施用比例增加而显著增加,最多可超过十倍以上,并且活性大大增加,与施肥后溶解性有机物含量的升高呈正相关。不同处理条件下的土壤重金属浸出趋势相似：在中性pH下浸出浓度最低,然后逐渐向强酸和强碱增加,呈现出V型变化。地球化学模型LeachXS展示出较好的模拟结果,其模拟值与实测浓度具有良好的相关性(71.02%)。模拟结果显示,有机肥的施用不会明显改变重金...     

The Cement Industry as a Scavenger in Industrial Ecology and the Management of Hazardous Substances

The cement industry uses a variety of secondary materials and fuels, thus fulfilling the role of "scavenger" in industrial ecology (IE). The use of wastes in cement production has been advocated to reduce cement production costs and to achieve the degradation and immobilization of hazardous compounds. In dealing with hazardous elements contained in the wastes, this development has side effects such as relatively significant stack emissions of heavy metals and leaching of hazardous compounds during the life cycle of cement-derived products. Emissions and leaching potential may be substantially lowered by reducing levels of hazardous elements in wastes before they are included in cement production and by selectively capturing mercury from stack gases. An analogy to metabolic functions of selective uptake, sequestration, and selective excretion is presented.     

Effect of copper and tri- and hexavalent chromium on the work of an activated sludge.

The effect of metals (Cu2+, Cr3+, Cr6+) on the work of an activated sludge grown in crude oil refining or synthetic wastes was examined. The activated sludge method was found to be applicable for the purification of wastes carrying up to 0.8 mgCu2+/1,15mgCr3+/1, or 20mgCr6+/1. Higher concentrations of these metals inhibited the work of the activated sludge which was evident in inferior purification and reduced intensity of respiration of the activated sludge microorganisms.     

Organoheterotrophe Laugung resistenter Materialien

Leaching processes can be classified in chemolithotrophic and organoheterotrophic mechanisms. In the case of chemolithotrophic leaching sulphide minerals, elemental sulphur, ferrous iron and a number of different reduced metals will be oxidized in a solution containing sulphuric acid of bacterial and/or chemical origin. Organoheterotrophic leaching however is connected with the accumulation of microbial metabolites such as organic acids, proteins, peptides and polysaccharides, which are capable to disintegrate ores, minerals or industrial wastes through dissolution, formation of complexes or chelates. Whereas at the present time chemolithotrophic leaching processes are in operation in industrial scale for the winning of copper, uranium and some other special metals, organoheterotrophic processes, their problems and technical applications are still under study. Therefore problems of organoheterotrophic leaching of chemical high resistant materials such as phosphorus furnace slag and zircon from the Baltic shield have been investigated with regard to possible technical applications for the winning of rare earth elements (REE) and other precious metals. Using a strain of Acetobacter methanolicus which is able to accumulate large amounts of gluconic acid on the basis of glucose or glucose containing by-products, leaching effects up to 90% of REE could be realized in the case of phosphorus furnace slag and up to 45% in the case of zircon.     

A review of biotechnology processes applied for manganese recovery from wastes

The global consumption of manganese is rising due to its growing industrial requirement while the natural reserves of manganese are diminishing at an alarming rate. Consequently, recovery of manganese from metal containing wastes has become highly crucial. Bioleaching of metal from wastes using microbes provides an adequate advantage over the traditional method of recovery. A molecular level understanding of microbial catalyzed manganese recovery is essential for the exploitation of novel microorganisms for similar applications. In current scenario, the application of bioleaching concentrates on cost effective and eco-friendly recovery of precious metals from mining and industrial wastes. This review encompasses the modern improvements in biomining, highlights the comprehensive factors that emphasize the selection of manganese recovery technique, shed insights into spectacular progress in developing molecular based technologies and also identifies the applicability of different models in metal bioremediation which will not only aid in pollution abatement but also in the prevention of occupational health disorder.     

Biosorption of toxic metals from aqueous solutions by bacteria strains isolated from metal-polluted soils

The use of biological materials for effective removal and recovery of heavy metals from contaminated wastewaters has emerged as a potential alternative method to conventional treatment techniques. The aim of this paper was the laboratory study of biosorption of toxic metals from aqueous solution by the application of microorganisms (Bacillus laterosporus or Bacillus licheniformis), isolated from polluted (metal-laden) soil. Microorganisms have a high surface area-to-volume ratio, because of their small size and therefore, they can provide a large contact interface, which would interact with metals from the surrounding environment. Microbial metal accumulation has received much attention during recent years, due to the potential use of microorganisms for treatment of metal-polluted water or wastewater streams. Two toxic metals were selected as typical examples: a cation (cadmium) and an oxyanion (hexavalent chromium, and promising results were obtained, under optimized conditions.