A New Klebsiella planticola Strain (Cd-1) Grows Anaerobically at High Cadmium Concentrations and Precipitates Cadmium Sulfide

Heavy metal resistance by bacteria is a topic of much importance to the bioremediation of contaminated soils and sediments. We report here the isolation of a highly cadmium-resistant Klebsiella planticola strain, Cd-1, from reducing salt marsh sediments. The strain grows in up to 15 mM CdCl₂ under a wide range of NaCl concentrations and at acidic or neutral pH. In growth medium amended with thiosulfate, it precipitated significant amounts of cadmium sulfide (CdS), as confirmed by x-absorption spectroscopy. In comparison with various other strains tested, Cd-1 is superior for precipitating CdS in cultures containing thiosulfate. Thus, our results suggest that Cd-1 is a good candidate for the accelerated bioremediation of systems contaminated by high levels of cadmium.     

Bioavailable cadmium during the bioremediation of phenanthrene-contaminated soils using the diffusive gradients in thin-film technique

AIMS: To study the impact of fungal bioremediation of phenanthrene on trace cadmium solid-solution fluxes and solution phase concentration. METHODS AND RESULTS: The bioremediation of phenanthrene in soils was performed using the fungus Penicillium frequentans. Metal behaviour was evaluated by the techniques of diffusive gradient in thin-films (DGT) and filtration. Fluxes of cadmium (Cd) show a significant (P < 0.002) increase after the start of bioremediation, indicating that the bioremediation process itself releases significant amount of Cd into solution from the soil solid-phase. Unlike DGT devices, the solution concentration from filtration shows a clear bimodal distribution. We postulate that the initial action of the fungi is most likely to breakdown the surface of the solid phase to smaller, 'solution-phase' material (<0.45 microm) leading to a peak in Cd concentration in solution. CONCLUSIONS: Phenanthrene removal from soils by bioremediation ironically results in the mobilization of another toxic pollutant (Cd). SIGNIFICANCE AND IMPACT OF THE STUDY: Bioremediation of organic pollutants in contaminated soil will likely lead to large increases in the mobilization of toxic metals, increasing metal bio-uptake and incorporation into the wider food chain. Bioremediation strategies need to account for this behaviour and further research is required both to understand the generality of this behaviour and the operative mechanisms.     

两株多环芳烃降解菌协同对菲-镉污染的去除特性北大核心

【目的】从污染土壤中分离筛选一株多环芳烃降解菌,并探究其与Pseudomonas aeruginosa B6-2构建的混菌体系对菲-镉复合污染的修复效能,以及微生物代谢特性对不同镉浓度赋存的响应特性,以期为复合污染的生物修复提供优良菌株资源及应用技术参考。【方法】采用富集驯化、筛选纯化方法得到一株多环芳烃降解菌,通过生理生化特征和16S rRNA基因序列分析进行鉴定。利用高效液相色谱法和电感耦合等离子体质谱法评估不同镉浓度赋存下各反应体系对菲和镉的去除效能;通过菌体细胞形态的扫描电镜观测及菌株代谢活性检测,探讨镉胁迫对菲生物降解过程的影响机制。【结果】筛选得到一株具有重金属耐受性和多环芳烃高效降解菌SZ-3,经鉴定为节杆菌属;降解菌协同体系(M)具有良好的菲降解效能和抗镉胁迫优势。镉胁迫浓度为0.5、10 mg/L时,M对菲和镉的去除率分别高于85%、80%;镉胁迫浓度为25、50 mg/L时,2种污染物的去除率均大于65%。扫描电镜分析表明,镉胁迫导致菌体表面粗糙且出现不同程度变形,菌体间黏附性和聚集性提高。反应周期内,邻苯二酚1,2-双加氧酶活性与电子传递体系活性随镉浓度增加而降低,两者变化与菲降解速率变化一致。【结论】Arthrobacter sp.SZ-3是一株PAHs高效降解菌,能与Pseudomonas aeruginosa B6-2协同高效修复菲-镉复合污染,随着初始镉胁迫浓度增加,混菌协同对目标污染物去除的优势显著。     

Interactions of bacteria with cadmium

Cadmium pollution arises mainly from contamination of minerals used in agriculture and from industrial processes. The usual situation is of large volumes of soil and water that are contaminated with low — but significant — concentrations of cadmium. Therefore, detoxification of the polluted water and soil involves the concentration of the metal, or binding it in a way that makes it biologically inert.Cadmium is one of the more toxic metals, that is also carcinogenic and teratogenic. Its effects are short term, even acute (diseases like Itai-itai), or long term. The long term effects are intensified due to the fact that cadmium accumulates in the body.This paper describes a study involving several hundred cadmium-resistant bacterial isolates. These bacteria could be divided into three groups—the largest group consisted of bacteria resistant to cadmium by effluxing it from the cells. The bacteria of the other two groups were capable of binding cadmium or of detoxifying it. We concentrated on one strain that could bind cadmium very efficiently, depending on the bacterial biomass and on the pH. This strain could effectively remove cadmium from contaminated water and soil.     

Bioremediation of multi-metal contaminated soil using biosurfactant — a novel approach

An unconventional nutrient medium, distillery spent wash (1:3) diluted) was used to produce di-rhamnolipid biosurfactant by Pseudomonas aeruginosa strain BS2. This research further assessed the potential of the biosurfactant as a washing agent for metal removal from multimetal contaminated soil (Cr-940 ppm; Pb-900 ppm; Cd-430 ppm; Ni-880 ppm; Cu-480 ppm). Out of the treatments of contaminated soil with tap water and rhamnolipid biosurfactant, the latter was found to be potent in mobilization of metal and decontamination of contaminated soil. Within 36 hours of leaching study, di-rhamnolipid as compared to tap water facilitated 13 folds higher removal of Cr from the heavy metal spiked soil whereas removal of Pb and Cu was 9–10 and 14 folds higher respectively. Leaching of Cd and Ni was 25 folds higher from the spiked soil. This shows that leaching behavior of biosurfactant was different for different metals. The use of wastewater for production of biosurfactant and its efficient use in metal removal make it a strong applicant for bioremediation.     

Effects of copper, cadmium and contaminated harbour sediments on recolonisation of soft-bottom communities

An extensive field experiment on benthic colonisation on polluted sediments was carried out at 50 m depth at three locations representative of the pollution gradient in the inner Oslofjord. The aim of the study was to investigate the effect of copper, cadmium and polluted harbour sediment on recolonisation of benthic fauna, and whether the response varied with a varying degree of background pollution. Copper and cadmium were added to the local sediments at the three locations, while the contaminated harbour sediment was taken from the hypoxic Oslo harbour and transplanted to well-oxygenated and less-polluted locations. Oslo harbour has a poor macrofauna, the sediments are heavily contaminated and the oxygen levels in the bottom waters are low. One of the aims of this experiment was to separate effects of contamination from effects of low oxygen. Sediments with high levels of copper (∼400-1500 mg/kg) clearly had a negative effect on colonisation by several taxa. This negative response was more pronounced at the relatively pristine location in the outer fjord compared to the more polluted sites, probably as a result of an increased bioavailability of the metals in sediments with lower concentrations of organic carbon. Sediments with high levels of cadmium (∼9-23 mg/kg), on the other hand, did not have negative effects on colonisation of any taxa. In the boxes with polluted harbour sediments, only the polychaete Raricirrus beryli showed reduced abundance. This lack of community response clearly indicates that hypoxia is more critical than high concentrations of contaminants for the establishment of a normal benthic fauna in the Oslo harbour area. The experiment only lasted for 6 months and the recolonising fauna was dominated by opportunistic and r-selected species. Long-term toxic effects may therefore have occurred if the experiment had lasted longer. The experiment also showed that the time for the development of a community resembling the ambient community was faster on the polluted than on the more pristine location.     

硫化镉纳米粒子对原核生物的毒理作用

硫化镉纳米粒子（cadmium sulfide nanoparticles,CdS NPs）是一种重要的半导体,具有突出的光电特性、可调带隙和化学稳定性,在分析化学、生物医学、荧光成像和生物传感器等方面具有潜在应用价值。生物合成CdS NPs具有可控、低成本、环境友好等优势而被广泛研究。然而CdS NPs本身兼具纳米材料毒性及重金属硫化物毒性,其对原核微生物的毒性研究受到广泛关注。本文以大肠杆菌为例,对CdS NPs在原核生物细胞内的毒性机理研究进展进行了综述,包括CdS NPs的生物合成机制、CdS NPs对大肠杆菌的毒害作用以及大肠杆菌对该毒害作用的防御机制,着重论述了细菌在合成CdS NPs过程中Cd²⁺及CdS对合成细菌本身的毒理作用及该细菌所产生的相应应激机制。本文旨在更好、更全面地评估CdS NPs的毒性,促进抗CdS NPs的原核生物在相关领域的发展和应用。     

Enhancement of bioremediation by Ralstonia sp. HM-1 in sediment polluted by Cd and Zn

In this study, the potential for the application of the bioaugmentation to Cd and Zn contaminated sediment was investigated. A batch experiment was performed in the lake sediments augmented with Ralstonia sp. HM-1. The degradation capacity of 18.7 mg-DOC/l/day in the treatment group was bigger than that of the blank group (4.4 mg-DOC/l/day). It can be regarded as the result of the reduction of the metal concentration in the liquid phase due to adsorption into the sediments, with the increased alkalinity resulting from the reduction of sulfate by sulfate reducing bacteria (SRB). The removal efficiency of cadmium and zinc in the treatment group was both 99.7% after 35 days. Restrain of elution to water phase from sediment in the Ralstonia sp. HM-1 added treatment group was also shown. In particular, the observed reduction of the exchangeable fraction and an increase in the bound to organics or sulfide fraction in the treatment group indicate its role in the prevention of metal elution from the sediment. Therefore, for bioremediation and restrain of elution from the sediment polluted by metal, Ralstonia sp. augmentation with indigenous microorganism including SRB, sediment stabilization and restrain of elution to surface water is recommended.     

Engineering hydrogen sulfide production and cadmium removal by expression of the thiosulfate reductase gene (phsABC) from Salmonella enterica serovar typhimurium in Escherichia coli

The thiosulfate reductase gene (phsABC) from Salmonella enterica serovar Typhimurium was expressed in Escherichia coli to overproduce hydrogen sulfide from thiosulfate for heavy metal removal (or precipitation). A 5.1-kb DNA fragment containing phsABC was inserted into the pMB1-based, high-copy, isopropyl-beta-D-thiogalactopyranoside-inducible expression vector pTrc99A and the RK2-based, medium-copy, m-toluate-inducible expression vector pJB866, resulting in plasmids pSB74 and pSB77. A 3. 7-kb DNA fragment, excluding putative promoter and regulatory regions, was inserted into the same vectors, making plasmids pSB103 and pSB107. E. coli DH5alpha strains harboring the phsABC constructs showed higher thiosulfate reductase activity and produced significantly more sulfide than the control strains under both aerobic and anaerobic conditions. Among the four phsABC constructs, E. coli DH5alpha (pSB74) produced thiosulfate reductase at the highest level and removed the most cadmium from solution under anaerobic conditions: 98% of all concentrations up to 150 microM and 91% of 200 microM. In contrast, a negative control did not produce any measurable sulfide and removed very little cadmium from solution. Energy-dispersive X-ray spectroscopy revealed that the metal removed from solution precipitated as a complex of cadmium and sulfur, most likely cadmium sulfide.     

Synthesis, thermal stability and photoluminescence of new cadmium sulfide/organic composite hollow sphere nanostructures

Novel cadmium sulfide/organic composite hollow spheres composed of sword-like nanorods were synthesized via a simple reaction between cadmium salts and thioglycolic acid (TGA) at room temperature. The products were characterized by X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), selected area electron diffraction (SEAD) and Fourier transform infrared (FT-IR) spectra. Thermal stability of the organic composite was investigated. CdS/organic composite would decompose into pure wurtzite CdS through hydrothermal treatment. Effect of the cadmium source on the formation of the CdS/organic composite was investigated. Photoluminescence (PL) was used to study the optical properties of CdS/organic composite and pure CdS.     

Studies of sulfate utilization by algae: 8. The ubiquity of sulfate reduction to thiosulfate

Cell-free extracts from several microorganisms, when prepared by methods originally devised for Chlorella pyrenoidosa (Emerson strain 3) and incubated anaerobically with ATP, Mg²⁺, and 2, 3-dimercaptopropan-1-ol, are capable of reducing sulfate-³⁵S to thiosulfate. These microorganisms include, in addition to C. pyrenoidosa (Emerson strain 3), several other strains of C. pyrenoidosa, Chlorella protothecoides, Chlorella vulgaris, Anacystis sp., Chlamydomonas reinhardi, Escherichia coli, Salmonella typhimurium, and baker's yeast. Three of these organisms, E. coli, S. typhimurium, and baker's yeast, were previously reported by others to reduce sulfate to sulfite. Moreover, three mutant strains of S. typhimurium (Ba-25, Ce-363, and Bc-482) previously reported by other workers to be unable to reduce sulfate to sulfite also cannot form thiosulfate, and one mutant strain (Cd-68) reportedly able to form sulfite can also form thiosulfate. Taken together, this suggests that thiosulfate-forming activity may be a common feature of sulfate-reducing systems, and it may be present in enzymatic systems previously thought to be forming sulfite. Reasonably conclusive identification of thiosulfate is provided by ion exchange chromatography and by paper electrophoresis; the ambiguities associated with other analytical methods are discussed.     

Iron promotes cadmium binding to citrate.

Iron-cadmium interactions are important in cadmium toxicity. Dietary iron supplements may decrease cadmium retention after oral cadmium exposure but the underlying mechanism is not known. Using a CdS/AgS ion selective electrode to measure [Cd2+] in physiological saline solution at pH 7.4, we show that Fe2+ promotes Cd2+ binding to citrate thereby decreasing the availability of free Cd2+. This suggests the formation of high molecular weight Cd2+-Fe2+-citrate complexes. We confirm this suggestion by showing that 109Cd2+ is retained by 1 kDa cut off filters when present with total 50 microM Fe2+ plus 1 mM citrate but not when present with citrate alone. The formation of high molecular weight complexes may prevent Cd2+ absorption. As citrate is part of the diet, we suggest that these iron-cadmium interactions may contribute to the protective effect of iron against cadmium toxicity.     

Role of the yeast ABC transporter Yor1p in cadmium detoxification

Growth of yeast strains, either deleted for the vacuolar ABC transporter Ycf1 or deleted for the plasma membrane ABC transporter Yor1p or overexpressing Yor1p, were compared for their sensitivity to cadmium. On solid medium cell death (or growth inhibition) was observed at cadmium concentrations higher than 100 microM when yeasts were grown at 30 degrees C for 24 h. However, for all tested strains cell death (or growth inhibition) was already observed at 40 microM cadmium when incubated at 23 degrees C for 60 h. Thus cadmium is more toxic to yeast at 23 degrees C than at 30 degrees C. At 23 degrees C, the Deltayor1 strain grew more slowly than the wild-type strain and the double Deltayor1, Deltaycf1 deleted strain was much more sensitive to cadmium than each single Deltayor1 or Deltaycf1 deletant. Overexpression of Yor1p in a Deltaycf1 strain restores full growth. Cadmium uptake measurements show that Deltaycf1 yeast strains expressing or overexpressing Yor1p store less cadmium than the corresponding Deltaycf1, Deltayor1 strain. The strains expressing Yor1p display an energy-dependent efflux of cadmium estimated for the yeast overexpressing Yor1p to be about 0.02 nmol 109Cd/mg protein/min. Yeast cells loaded with radiolabeled glutathione and then with radioactive cadmium displayed a twice-higher efflux of glutathione than that of cadmium suggesting that Yor1p transports both compounds as a bis-glutathionato-cadmium complex. All together, these results suggest that in addition to being accumulated in the yeast vacuole by Ycf1p, cadmium is also effluxed out of the cell by Yor1p.     

Lyophilized,non-viable,recombinant E. coli cells for cadmium bioprecipitation and recovery

The phoN gene, encoding a non-specific acid phosphatase from Salmonella enterica sv. Typhi, was cloned and overexpressed into Escherichia coli. The E. coli cells bearing phoN showed high acid phosphatase activity and removed 83% of cadmium from a 1 mM solution in 3 h, when provided with 5 mM β-glycerophosphate as a source of phosphate. Such cells, when lyophilized without any lyo/cryoprotectant, were rendered non-viable but fully retained cadmium precipitation ability. Lyophilized recombinant cells could be stored at room temperature, without significant loss of activity for up to 6 months, and removed upto 21 g cadmium/g dry weight. The precipitated cadmium could be easily recovered from the cells by dilute acid wash, following which the cells retained their cadmium precipitation ability, facilitating their reuse. The use of genetically engineered, non-viable E. coli cells offers an environmentally safe biotechnology for bioremediation of cadmium from contaminated sites.     

Biosorption of cadmium by a Cd2+-hyperresistant Bacillus cereus strain HQ-1 newly isolated from a lead and zinc mine

A Cd²⁺-hyperresistant bacterial strain HQ-1 was isolated from a lead–zinc mine. The strain was characterized and identified as Bacillus cereus based on morphology, physiological tests and 16S rRNA gene analysis. The minimal inhibitory concentration of Cd²⁺ for the bacterium was 0.012 mol/l. Isotherms for cadmium (Cd) biosorption by cells of B. cereus strain HQ-1 were investigated. The equilibrium data could be fitted by a Langmuir isotherm equation. The possible functional sites that might be influenced by the sorption were determined. The results indicate that this B. cereus strain has excellent potential for biosorption of Cd. Physiological characterization of the isolate also indicates possible application of this strain for bioremediation of sites with Cd contamination.     

Lead,cadmium and nickel removal efficiency of white-rot fungus Phlebia brevispora

Widespread of heavy metals contamination has led to several environmental problems. Some biological methods to remove heavy metals from contaminated wastewater are being widely explored. In the present study, the efficiency of a white-rot fungus, Phlebia brevispora to remove different metals (Pb, Cd and Ni) has been evaluated. Atomic absorption spectroscopy of treated and untreated metal containing water revealed that all the metals were efficiently removed by the fungus. Among all the used metals, cadmium was the most toxic metal for fungal growth. Phlebia brevispora removed maximum Pb (97·5%) from 100 mmol l⁻¹ Pb solution, which was closely followed by Cd (91·6%) and Ni (72·7%). Scanning electron microscopic images revealed that the presence of metal altered the morphology and fine texture of fungal hyphae. However, the attachment of metal on mycelia surface was not observed during energy-dispersive X-ray analysis, which points towards the intracellular compartmentation of metals in vacuoles. Thus, the study demonstrated an application of P. brevispora for efficient removal of Pb, Cd and Ni from the metal contaminated water, which can further be applied for bioremediation of heavy metals present in the industrial effluent.     

镉污染条件下水稻对假单胞菌TCd-1微生物修复的生理响应

微生物在修复重金属污染土壤中发挥重要作用。为阐明假单胞菌TCd-1降低水稻镉吸收的机理,通过加镉土培盆栽试验,在10 mg/kg镉处理下,对比研究了接种菌株对2种镉耐性不同水稻品种(特优671、百香139)镉含量、根系活力、光合作用、抗氧化酶活性及抗氧化物质含量的影响。结果表明：与10 mg/kg镉处理相比,接种假单胞菌TCd-1后水稻“特优671”和“百香139”的根、茎、叶、糙米的镉含量分别依次降低了30.4%、39.1%、40.7%、29.2%和52.2%、51.7%、18.4%、38.8%;提高了2种水稻的根系活力、光合作用,促进了水稻的生长;“特优671”、“百香139”叶片的超氧化物歧化酶(Superoxide dismutase, SOD)活性分别提高了7.3%、138.5%,过氧化物酶(Peroxidase, POD)活性提高了82.0%、106.2%,过氧化氢酶(Catalase, CAT)活性提高了58.8%、172.7%;叶片的类黄酮含量提高了139.4%、73.6%,总酚含量提高了27.2%、23.1%;超氧阴离子含量降低了44.2%、29.0%,丙二醛(Mal...     

Support-controlled chemoselective olefin-imine addition photocatalyzed by cadmium sulfide on a zinc sulfide carrier.

The semiconductor catalyzed photoaddition of cyclopentene or cyclohexene to various novel electron-poor imines of type p-XC(6)H(4)(CN)C[double bond, length as m-dash]N(COPh) (X = H, F, Cl, Br, Me, MeO) was investigated as a function of the nature of the cadmium sulfide photocatalyst. Irradiation (lambda>/= 350 nm) of silica supported cadmium sulfide surprisingly did not afford the expected olefin-imine adducts but an imine hydrocyanation product via an unprecedented dark reaction. However, when silica was replaced by zinc sulfide as the support for cadmium sulfide, the expected homoallylic N-benzoyl-alpha-amino cyanides were isolated in yields of 65-84%. Thus, chemoselectivity is introduced through replacing an insulating by a semiconducting support, a hitherto unknown effect in semiconductor photocatalysis. From the sign of the time resolved photovoltage it is found that the mixed metal sulfide interface CdS/ZnS increases the lifetime of photogenerated electron-hole pairs by about one order of magnitude as compared to the SiO(2)/CdS system. The reaction rate increases with increasing imine sigma-Hammett constants and decreasing stability of intermediate benzyl radicals.