重金属污染土壤的湿地生物修复技术

生物修复技术是近年来发展起来的一种有前途的污染治理技术,重金属的湿地植物稳定技术和植物萃取技术等植物修复技术是一研究热点;同时,针对微生物对重金属的生物积累、生物转化及生物修复作一分析,重金属的生物修复生理机制及其提高富集效率的条件作一综述,以期推动国内这一国际热点领域的研究。     

Simplified heavy metal staining techniques demonstrated with Fast Plant leaf tissue

Fast Plant(Brassica rapa,Cruciferae)leaf tissuefixed in glutaraldehyde-acrolein and post-fixed in os-mium,was examined for response to several easily-prepared heavy metal stains.Lead and uranium,separately and in combination,gave typical resultsacross the spectrum of cell organellets.As a single stainfollowing osmium,bismuth produced images seeminglyequivalent to lead and uranium.Phosphotungstic acidproduced very good membrane delineation but produceda washed-out background image similar to that from leadstaining.Carbohydrate compounds were especiallyresponsive to ruthenium;the cytoplasm and the matrixof all organelles were also stained very well.Theprocedures were no more demanding than traditionalstaining methods and may be easily used in research andteaching.Fast Plant materials are a reliable,quick andeasy source of living material.     

Simplified heavy metal staining techniques demonstrated with Fast Plant leaf tissue

Fast Plant (Brassica rapa,Cruciferae)leaf tissue fixed in glutaradehyde-acrolein and post-fixed in osmium,was examined for response to several easilyprepared heavy metal stains.Lead and uranium,separately and in combination,gave typical results across the spectrum of cell orgeanelles.As s single stain following osmium,bismuth produced images seemingly equivalent to lead and uranium.Phosphotungstic acid produced very good membrane delineation but produced a washed-out background image similar to that from lead staining .Carbohydrate compounds were especially responsive to ruthenium;the cytoplasm and the matrix of all organelles were also stained very well.The procedures were no more demanding than traditional staining methods and may be easily used in research and teaching .Fast Plant materials are a reliable,quick nand easy source of living material.     

Studies on the accumulation of heavy metal elements in biological systems

Summary Cells of a Daucus carota suspension culture were entrapped in a matrix of calcium alginate. The immobilised cells, incubated in a buffer mixture of sucrose, nitrate, KCl, CaCl₂, 2-(N-morpholino)-ethane sulphonic acid at pH 5.5, hydroxylated digitoxigenin. When compared under the same incubation conditions, freely suspended cells biotransformed digitoxigenin at a faster rate. Periplogenin formation was maximal at pH 5.3 and temperatures of 26°–34°C. The hydroxylase activity of the entrapped cells adapted to the presence of 20 mM CaCl₂ over a 12 day incubation. The diffusion barrier established on entrapment of the cells could not be overcome by addition of detergents or methanol. Controlled addition of chloroform (at 1/4 and 1/2 saturation) did stimulate hydroxylation of digitoxigenin without adversely affecting cell viability. The rate of hydroxylation of digitoxigenin was linear over an immobilised cell concentration of 0–7 mg dry weight and a digitoxigenin concentration of 0–20 mg/L. Five consecutive batch bioconversions at a rate greater than 60% could be achieved before the biocatalyst was inactivated. The results are discussed in relation to improving the hydroxylation reaction by immobilised D. carota and other reactions performed by immobilised plant cells.     

Studies on thermoprotection induced by heavy metal ions in spring barley seedlings

Barley seedlings (Hordeum vulgare L., cv. Fatran) were pretreated with various concentrations of five heavy metal ions (Zn, Cu, Fe, Mg, Mn) for 3 d. When the subsequent heat shock was administered for 2 h, the heavy metal ions had thermoprotective effect against the sub-lethal (40 °C) and lethal (45 °C) temperature stresses, which were otherwise lethal to control (water grown) seedlings. The effectiveness of each of the heavy metal ions was different, the most effective being Cu. The level of protection provided by these heavy metal ions was dependent on both the time and the concentration that plants were exposed to them. The greatest differences were recorded in the thermotolerance mediated by applied metal ions in the shoot and root cells. Thermotolerance was exhibited by both the shoot and root of pretreated seedlings, even though the heavy metal stresses were applied solely to the roots.     

Studies of heavy metal sorption by Trenton Channel (Detroit River) sediments

Sediment resuspension plays a dominant physical role in downstream transport of sediment-bound, or in-place pollutants. During resuspension, however, numerous sorption reactions may alter contaminant phase distributions. Previous field resuspension studies on heavily contaminated sediments (Theis et al., 1988, J. Great Lakes Res. 14, 216) showed parallel trends in metal partitioning with pH and time for each of 7 metals (Cd, Co, Cr, Cu, Ni, Pb, Zn), when pH was < 7.5 during resuspension. To improve our ability to interpret follow-up laboratory partitioning experiments using sediments from the field sites, we conducted an evaluation of sediment sample storage as a potential factor leading to field-laboratory partitioning differences. Although metal sorption observed in the laboratory differed substantially from that observed in the field, sample storage effects, reported as holding time and changes in solid phase metal fractionation, gave minimal support for the hypothesis that sample storage caused the differences. It appears, rather, than our in vitro batch equilibrium systems incompletely replicated those attributes of a sediment-water system that are relevant to adsorption and desorption of heavy metals during a resuspension event. Accordingly, we conclude that a general improvement in the understanding of contaminant partitioning would result if future studies would assign greater importance to evaluating the effects of relevant physical phenomena on partitioning (e.g. particle interaction and shear stress), in addition to such widely studied chemical determinants as pH, time, and metal species.     

Retromobilization of heavy metal resistance genes in unpolluted and heavy metal polluted soil

Abstract: Retromobilization of the nonconjugative (Tra⁻Mob⁺) IncQ vector, pMOL155, and the non-mobilizable (Tra⁻Mob⁻) vector, pMOL149, by means of the IncP plasmids RP4 and pULB113 (RP4::Mu3A), was studied in plate matings and in soil microcosms, and compared with direct and triparental mobilization. Both vectors harbour the czc genes, originating from Alcaligenes eutrophus , which code for resistance to Co, Zn, and Cd. The donor of the czc genes was Escherichia coli which did not express these genes. The recipient, Alcaligenes eutrophus , expressed the czc genes very well. Retromobilization, direct and triparental mobilization of pMOL155 was observed in sterile soil. Both the addition of nutrients and heavy metals significantly enhanced the number of (retro)transconjugants. Retromobilization was also detected in nutrient amended nonsterile soil, but the presence of the autochthonous soil biota strongly reduced the number of retrotransconjugants and also prevented their increase upon application of heavy metals to the soil. Retromobilization of the czc genes, cloned in pMOL149, by using pULB113 was also observed, yet only in sterile, nutrient amended, heavy metal polluted soil.     

具超强汞富集能力基因工程菌生长情况的研究

对具超强汞富集能力的基因工程菌在重金属汞离子存在的水体中的生长状况进行了研究。实验所采用的基因工程菌由于外源基因的表达而对Hg^2 产生了一定的耐受力,而且这种耐受力经IPTG诱导后还能得到进一步的增强,耐受能力从Hg^2 浓度5mg／L提高到15mg／L。IPTG加入的时机对菌体的生长和耐受力的有效诱导是重要的。一般在OD600为0．5～0．8时加入,且加入后还应保证2h左右的诱导时间。实验结果还表明菌体在生长过程中对碳源的要求很低。     

Microbes in heavy metal remediation

Heavy metal contamination due to natural and anthropogenic sources is a global environmental concern. Release of heavy metal without proper treatment poses a significant threat to public health because of its persistence, biomagnification and accumulation in food chain. Non-biodegradability and sludge production are the two major constraints of metal treatment. Microbial metal bioremediation is an efficient strategy due to its low cost, high efficiency and ecofriendly nature. Recent advances have been made in understanding metal--microbe interaction and their application for metal accumulation/detoxification. This article summarizes the potentials of microbes in metal remediation.     

Microorganisms and heavy metal toxicity

The environmental and microbiological factors that can influence heavy metal toxicity are discussed with a view to understanding the mechanisms of microbial metal tolerance. It is apparent that metal toxicity can be heavily influenced by environmental conditions. Binding of metals to organic materials, precipitation, complexation, and ionic interactions are all important phenomena that must be considered carefully in laboratory and field studies. It is also obvious that microbes possess a range of tolerance mechanisms, most featuring some kind of detoxification. Many of these detoxification mechanisms occur widely in the microbial world and are not only specific to microbes growing in metal-contaminated environments.     

Phytochelatins and heavy metal tolerance

The induction and heavy metal binding properties of phytochelatins in heavy metal tolerant (Silene vulgaris) and sensitive (tomato) cell cultures, in water cultures of these plants and in Silene vulgaris grown on a medieval copper mining dump were investigated. Application of heavy metals to cell suspension cultures and whole plants of Silene vulgaris and tomato induces the formation of heavy metal–phytochelatin-complexes with Cu and Cd and the binding of Zn and Pb to lower molecular weight substances. The binding of heavy metal ions to phytochelatins seems to play only a transient role in the heavy metal detoxification, because the Cd- and Cu-complexes disappear in the roots of water cultures of Silene vulgaris between 7 and 14 days after heavy metal exposition. Free heavy metal ions were not detectable in the extracts of all investigated plants and cell cultures. Silene vulgaris plants grown under natural conditions on a mining dump synthesize low molecular weight heavy metal binding compounds only and show no complexation of heavy metal ions to phytochelatins. The induction of phytochelatins is a general answer of higher plants to heavy metal exposition, but only some of the heavy metal ions are able to form stable complexes with phytochelatins. The investigation of tolerant plants from the copper mining dump shows that phytochelatins are not responsible for the development of the heavy metal tolerant phenotypes.     

重金属生物吸附剂的应用研究现状

1　前言含重金属废水是对生态环境危害极大的一类污染源。进入环境中的重金属往往参与食物链循环并在生物体内积累 ,破坏生物体的正常生理代谢[1,2 ] 。如何消除重金属的危害并有效地回收废水中的贵重金属是当今环境保护工作中面临的一个非常突出的问题。重金属废水主要来源于电镀、采矿、冶炼、化工、纺织、印染、化纤等行业 ,传统含重金属废水的处理方法主要有沉淀法、化学氧化还原法、蒸发法、离子交换法、电化学处理法、膜技术分离法等 ,这些方法最突出的缺点在于处理低浓度 ( <1 0 0ｍｇ/ｌ)重金属废水时 ,操作繁琐、运行费用较高。近…     

Detection and quantification of ATP and heavy metal with electronical micro-circuits

In order to use whole eukaryotic cells as an active element in the detection and amplification of biological signals, for both in vitro and in vivo applications, we have undertaken a first approach to interface live cells and integrated circuit, and evaluate the possibility to develop a microbioreactor. An amplified photodiode system was designed and built as an electronical circuit in a way that it could easily be miniaturised. In parallel micro-chips with silicium chambers were used as microbioreactors to adhere cells. We showed here that this etched silicon chamber allows endothelial and CHO cells spreading, permitting determination of a number of cell properties {\it on line} providing appropriate integrated circuits are designed to perform the desired functions. The photodiode system reacting to the luminescent luciferase system permitted, through the use of appropriate software from a personal computer (PC) connected on line in vitro, the determination of ATP concentration, and using different luciferase transfected bacteria permitted the detection of constitutive or induced luminescence. This revised version was published online in July 2006 with corrections to the Cover Date.     

Efflux-mediated heavy metal resistance in prokaryotes

What makes a heavy metal resistant bacterium heavy metal resistant? The mechanisms of action, physiological functions, and distribution of metal-exporting proteins are outlined, namely: CBA efflux pumps driven by proteins of the resistance-nodulation-cell division superfamily, P-type ATPases, cation diffusion facilitator and chromate proteins, NreB- and CnrT-like resistance factors. The complement of efflux systems of 63 sequenced prokaryotes was compared with that of the heavy metal resistant bacterium Ralstonia metallidurans. This comparison shows that heavy metal resistance is the result of multiple layers of resistance systems with overlapping substrate specificities, but unique functions. Some of these systems are widespread and serve in the basic defense of the cell against superfluous heavy metals, but some are highly specialized and occur only in a few bacteria. Possession of the latter systems makes a bacterium heavy metal resistant.