絮凝酵母吸附Cr(VI)的机理

絮凝酵母SPSC01为酿酒酵母Saccharomyces cerevisiae和粟酒裂殖酵母Schizosaccharomyces pombe的融合菌株,用其吸附水溶液中的重金属Cr(VI),可以大大降低生物吸附的固液分离成本。为了探讨SPSC01菌体絮凝蛋白对Cr(VI)还原吸附的影响,对SPSC01与其亲本菌株的吸附行为进行了比较。结果表明,SPSC01和其具有絮凝性状的亲本S.pombe的Cr(VI)去除速率基本同步,远优于无絮凝性状的亲本S.cerevisiae;达到吸附平衡时,S.pombe、SPSC01和S.cerevisiae对总Cr去除率分别达68.8%、48.6%和37.5%;从而证明了絮凝有利于Cr(VI)的还原、吸附,絮凝蛋白在Cr(VI)的还原吸附过程中起促进作用。通过化学屏蔽方法和傅立叶变换红外光谱(FTIR)分析,对SPSC01菌体表面吸附Cr(VI)的机理进行了研究,结果表明SPSC01菌体表面吸附Cr(VI)起主要作用的基团是氨基、羧基和酰胺基。     

微生物还原Cr(VI)的研究进展

随着现代工业的发展, 水环境中的重金属对人类健康和环境带来严重的危害, 其中的Cr(VI)具有强烈的毒性。微生物在代谢过程中可以将Cr(VI)还原为Cr(III), 有效降低Cr(VI)的毒性。本文从可还原Cr(VI)的微生物、微生物还原Cr(VI)的机理、还原过程中存在的问题及发展方向等方面进行了综述。     

木霉生物吸附重金属铬机理的研究

利用木霉（Trichoderma lhd）菌体作为吸附剂,对水体中的六价铬进行生物吸附,借助傅立叶红外变换光谱和拉曼光谱对六价铬的生物吸附机理进行了探讨。实验条件优化结果表明,温度28 ℃以及酸性环境条件（pH 1）有利于Cr （VI） 的生物吸附,12小时内,Cr （VI） 的生物吸附去除效率达99 %。吸附机理实验结果分析表明,相比于对照实验,2350 cm^-1吸收峰的出现为吸附剂表面质子化的氨基如＞NH2^＋, NH^＋, ＞C=NH^＋―等基团吸附Cr （VI）所致。拉曼光谱中吸收峰2097 cm^-1强度显著增强进一步表明,Cr （VI）的生物吸附是吸附剂表面氨基基团在起作用。     

融合酵母对重金属Cr的富集机理

研究了1株高效融合酵母对Cr的富集机理及其微观结构变化.研究结果表明,融合酵母对Cr6+的还原、吸附过程伴随着溶液H+离子的消耗.菌体表面的络合基团主要有氨基、羟基、磷酸基等,其中磷酸基团对吸附的影响最大,该基团屏蔽后总Cr去除率及Cr6+还原率分别降低了70%和46%;吸附过程趋向于将表面络合的Cr运输至细胞内并和细胞内物质形成更稳定的结合态,该过程可在吸附90min内达到平衡;Cr在细胞表面的吸附及还原作用会改变细胞微观结构,使细胞通透性增强.     

黄麻吸附重金属Cr(Ⅵ)专用种质筛选

首次以国内外23个代表性黄麻种质为研究对象,用主茎嫩梢和一、二级分枝嫩梢制成天然重金属吸附剂,测定其对溶液中Cr(Ⅵ)离子的去除率,并对与黄麻吸附能力及产量密切相关的功能性状:生育期动态、株高、分枝习性、各级分枝嫩梢的产量进行调查、方差分析和相关性分析。结果表明,不同黄麻种质制成的生物吸附剂对Cr(Ⅵ)的吸附能力不同,去除率在85.25%~96.88%之间;不同级次分枝嫩梢的产量及对Cr(Ⅵ)的去除率不同;种质间除出苗速度外所有调查性状均存在较大差异;去除率与株高呈极显著负相关(P<0.01)。从产量和去除率方面综合考虑,J001和J011 2个种质表现优良,适宜作为吸附重金属专用品种推广种植。     

微生物还原Cr(VI)的研究进展

随着现代工业的发展,水环境中的重金属对人类健康和环境带来严重的危害,其中的Cr(VI)具有强烈的毒性.微生物在代谢过程中可以将Cr(VI)还原为Cr(Ⅲ),有效降低Cr(VI)的毒性.本文从可还原Cr(VI)的微生物、微生物还原Cr(VI)的机理、还原过程中存在的问题及发展方向等方面进行了综述.     

异化铁还原细菌LQ25还原重金属Cr (VI)的特性研究

[背景] 异化铁还原细菌能够在还原Fe （III）的同时将毒性较大的Cr （VI）还原成毒性较小的Cr （III）,解决铬污染的问题。[目的] 基于丁酸梭菌（Clostridium butyricum） LQ25异化铁还原过程制备生物磁铁矿,开展异化铁还原细菌还原Cr （VI）的特性研究。[方法] 构建以氢氧化铁为电子受体和葡萄糖为电子供体的异化铁培养体系。菌株LQ25培养结束时制备生物磁铁矿。设置不同初始Cr （VI）浓度（5、10、15、25和30 mg/L）,分别测定菌株LQ25对Cr （VI）还原效率以及生物磁铁矿对Cr （VI）的还原效率。[结果] 菌株LQ25在设置的Cr （VI）浓度范围内都能良好生长。当Cr （VI）浓度为15 mg/L时,在异化铁培养条件下,菌株LQ25对Cr （VI）的还原率为63.45%±5.13%,生物磁铁矿对Cr （VI）的还原率为87.73%±9.12%,相比菌株还原Cr （VI）的效率提高38%。pH变化能影响生物磁铁矿对Cr （VI）的还原率,当pH 2.0时,生物磁铁矿对Cr （VI）的还原率最高,几乎达到100%。电子显微镜观察发现生物磁铁矿表面有许多孔隙,X-射线衍射图谱显示生物磁铁矿中Fe （II）的存在形式是Fe （OH）₂。[结论] 基于异化铁还原细菌制备生物磁铁矿可用于还原Cr （VI）,这是一种有效去除Cr （VI）的途径。     

Cr(VI)污染细粒土壤化学淋洗修复效果与经济成本分析

土壤淋洗技术具有修复效率高、修复彻底、污染土壤减量化等特点,但目前土壤淋洗的药剂成本相对较高,且淋洗后的细粒土壤仍需固化、稳定化处理,限制了淋洗技术大规模的推广应用。本研究以重庆市某Cr(VI)污染场地细粒土壤为对象,探究了Cr(VI)污染细粒土壤化学淋洗修复的效果与经济可行性。结果表明:除EDTA外,随着草酸、柠檬酸、醋酸和盐酸浓度的增加,土壤中Cr(VI)的去除率均逐渐增加,且草酸和柠檬酸复配淋洗效果最佳;液固比5∶1～10∶1时淋洗效果和稳定性最佳,液固比大于10∶1或低于5∶1淋洗效果和稳定性降低。淋洗时间越长,土壤中Cr(VI)的去除效果越好,土壤中Cr(VI)的浸出浓度越低;以草酸和柠檬酸作为复配淋洗剂,在液固比5∶1,淋洗45 min情况下,土壤中Cr(VI)去除率为62.73%,Cr(VI)的浸出浓度为0.64 mg·L^-1,低于垃圾填埋场Cr(VI)浸出标准1.5 mg·L^-1,且Cr(VI)污染细粒土壤淋洗药剂成本为300元·t^-1土,具备工程应用的经济可行性。     

解脂假丝酵母(Candida lipolytica)对铜的吸附

研究了解脂假丝酵母的表面特性及培养时间、pH值、铜浓度、菌体投加量、吸附时间等因素对铜吸附的影响,并探讨了吸附动力学特征。结果表明,菌体表面可能有-OH和-PO₄^3-,培养96 h的菌体吸附性能最佳,适宜pH为4.0-6.0,适宜菌体投加量为25.0g·L^-1(湿重)。在初始浓度为20mg·L^-1的铜溶液中投加25.0g·L^-1(湿重)的菌体,吸附2h,铜的去除率最高达86.5%。铜浓度为5,10mg·L^-1时,铜的去除率高达95%以上。动力学分析表明,在实验设定的浓度范围内解脂假丝酵母对铜的吸附基本符合Freundlich吸附模型。红外光谱分析表明吸附后-OH吸收峰蓝移18cm^-1,其它吸收峰没有明显的变化。     

自絮凝酵母颗粒连续发酵生产酒精的新工艺

用既有优良酒精发酵性能,又具有强自絮凝能力的融合酵母株ＳＰＳＣ,在单釜有效容积为１０ｍ３的四釜并联气升环流悬浮床生物反应器系统中,进行了连续发酵生产酒精的研究。以玉米为原料,双酶法制糖,过滤得到清糖液作为底物,在稀释速率为０１／ｈ的条件下,终点发酵液中酒精浓度为７０～８０ｇ／Ｌ,残余还原糖和残余总糖分别为２～３ｇ／Ｌ和３～５ｇ／Ｌ,悬浮床反应器的设备生产强度达到７～８ｇ（ＥｔＯＨ）／（Ｌ·ｈ）。     

Comparative Study of Cr(VI) Removal by Exiguobacterium sp. in Free and Immobilized Forms

Cr(VI) is a toxic environmental pollutant. To determine the potential role of microbes towards chromate bioremediation, two bacterial strains, E1 and E4, that could tolerate Cr(VI) at levels up to 2250 μg ml^?1 were isolated from the soil of a tannery. They were identified as Exiguobacterium sp. To estimate the removal of Cr(VI) using immobilized bacterial cells, 2% sodium alginate and 2.5% agar were used as immobilizing matrices. In the case of sodium alginate, 89% and 93% of Cr(VI) removal by E1 and E4, respectively, were observed. When agar beads were used as an immobilizing matrix, removal was recorded as 39% and 48% for E1 and E4, respectively. Removal of Cr(VI) was also estimated in sterile and nonsterile tannery effluent. More Cr(VI) removal was noted in the nonsterile effluent than in the sterile effluent. The maximum uptake of Cr(VI) of bound cells of E1 and E4 was found to be 17.54 and 20.04 μg ml^?1, respectively. Fourier transform infrared (FTIR) spectra of cells of E4 with Cr(VI), without Cr(VI), and immobilized cells depicted several absorption peaks, mainly for P?OH group, C?H bending, C?O bond, and amide II groups, reflecting the complex nature of the bacterial cells and the contribution of these functional groups to the Cr(VI) binding process.     

Cr(VI) reduction by Enterobacter sp. DU17 isolated from the tannery waste dump site and characterization of the bacterium and the Cr(VI) reductase

Out of nineteen bacteria screened from the tannery waste dump site, the most effective isolate, strain DU17 was selected for Cr(VI) reduction process among the non-pathogenic once. Based on 16S rRNA gene sequence analysis, the bacterium was identified as Enterobacter sp. DU17. Its amplified Cr(VI) reductase gene showed maximum homology with flavoprotein of Enterobacter cloacae. Enterobacter sp. DU17 reduced Cr(VI) maximally at 37 °C and pH 7.0. Various co-metals, electron (e⁻) donors and inhibitors were tested to study their effect on Cr(VI) reduction. In presence (0.2% each) of glucose and fructose, Enterobacter sp. DU17 reduced Cr(VI) completely after 16 and 20 h, respectively. Since the concentration of total Cr was invariable after remediation as detected through AAS analysis, this experiment disclosed that responsible operation was associated with extracellular Cr(VI) reduction process rather than uptake mechanism. Multiple antibiotic resistance index of 0.08 for this bacterium was very low as compared to standard risk assessment value of 0.20. With high Cr(VI) reducing capability, non-pathogenicity and antibiotic sensitivity, Enterobacter sp. DU17 is found to be very efficient in removing Cr(VI) toxicity from the environment.     

Influence of Cr(III) and Cr(VI) on the interaction between sparfloxacin and calf thymus DNA

Cr(III) and Cr(VI) have different binding capacity with sparfloxacin, and have different combination modes with calf thymus DNA. Selecting these two different metal ions, the influence of them on the binding constants between sparfloxacin (SPFX) and calf thymus DNA, as well as the related mechanism has been studied by using absorption and fluorescence spectroscopy. The result shows that Cr(III) has weaker binding capacity to SPFX in the SPFX-Cr(III) binary system, but influences the binding between SPFX and DNA obviously in SPFX-DNA-Cr(III) ternary system. However, although Cr(VI) has a stronger binding capacity to SPFX, it has no effect on the binding between SPFX and DNA. Referring to the different modes of Cr(III) and Cr(VI) binding to DNA, the mechanism of the influence of metal ions on the binding between SPFX and DNA has been proposed. SPFX can directly bind to DNA by chelating DNA base sites. If a metal ion at certain concentration binds mainly to DNA bases, it can decrease the binding constants between SPFX and DNA through competing with SPFX. While if a metal ion at certain concentration mainly binds to phosphate groups of DNA, it can increase the binding constants by building a bridge between SPFX and DNA. If a metal ion at certain concentrations binds neither to bases nor phosphate groups in DNA, it will have no effect on the binding constant between SPFX and DNA. Our result supports Palumbo's conclusion that the binding between SPFX and the phosphata groups is the precondition for the combination between SPFX and DNA, which is stabilized through stacking interactions between the condensed rings of SPFX and DNA bases.     

Simultaneous bioremediation of Cr(VI) and lindane in soil by actinobacteria

Environments co-contaminated with metals and organic compounds are difficult to remediate. Actinobacteria is an important group of microorganisms found in soils, with high metabolic versatility and potential for bioremediation. In this paper, actinobacteria were used to remediate soil co-contaminated with Cr(VI) and lindane. Five actinobacteria, tolerant to Cr(VI) and lindane mixture were selected: Streptomyces spp. A5, A11, M7, and MC1, and Amycolatopsis tucumanensis DSM 45259. Sterilized soil samples were inoculated with actinobacteria strains, either individually or as a consortium, and contaminated with Cr(VI) and lindane, either immediately or after 7 days of growth, and incubated at 30 °C during 14 days. All actinobacteria were able to grow and remove both contaminants, the consortium formed by Streptomyces spp. A5, M7, MC1, and A. tucumanensis showed the highest Cr(VI) removal, while Streptomyces sp. M7 produced the maximum lindane removal. In non-sterile soil samples, Streptomyces sp. M7 and the consortium removed more than 40% of the lindane, while Streptomyces sp. M7 demonstrated the greatest Cr(VI) removal. The most appropriate strategy for bioremediation of Cr(VI) and lindane co-contaminated soils would be the inoculation with Streptomyces sp. M7.     

Effect of complexing agents on reduction of Cr(VI) by Desulfovibrio vulgaris ATCC 29579

The reduction of Cr(VI) at the expense of molecular hydrogen was studied using resting cells of Desulfovibrio vulgaris ATCC 29579 in anaerobic resting cell suspensions in MOPS buffer. Bioreduction occurred only in the presence of ligands or chelating agents (CO32-, citrate, NTA, EDTA, DTPA). The stimulatory effect of these ligands on the rate of Cr(VI) reduction was correlated (r = 0.988) with the strength of the ligand/chelate complex of Cr(III). The data are examined with respect to likely solution and redox equilibria in the ionic matrix of the carrier solution, and with respect to the potential for bioremediation of Cr(VI).     

Adsorption Mechanism of Cr(VI) onto Coir Pith

Reductive adsorption of Cr(VI) on coir pith (hereafter CP) was examined as a function of pH, ionic strength, and temperature. The CP contains 1.33 meq g^{? 1} phenolic, 0.43 meq g^{? 1} of lactonic, and 0.35 meq g^{? 1} carboxylic sites. Thus the CP surface is enriched with electron-donating oxygen functionalities. As evidenced by infrared (IR) spectroscopy, the Cr(VI) → Cr(III) conversion is facilitated by CP sites that are enriched with O─ O functional groups. The adsorption of reduced Cr(VI) was found to occur via C─ O─ functional groups first forming innersphere complexes with the CP surface, yielding keto (> C═ O) groups on the CP surface. The reductive adsorption of Cr(VI) was almost completed within 3 to 4 h, and it was dependent on pH and background ionic strength, yielding the highest monolayer coverage (9.56E-7 mol m^{? 2}) at pH 3.7 in 0.1 M NaNO₃. The Γ_Cr(III) followed the order with respect to the ionic strength: Γ_{0.1 M} > Γ_{0.01 M} > Γ_{0.001 M}. The initial rate constant, k _i , increased with temperature as k _i ^{313 K} > k _i ^{303 K} > k _i ^{293 K} > k _i ^{283 K}.