酵母菌Y17吸附Cu2+的影响因素及吸附机理研究

以高效吸附Cu2 的酵母菌Y17为材料,对其吸附Cu2 过程中的主要影响因素,包括溶液Ph、Cu2 初始浓度、菌体添加量、吸附时间和温度以及吸附机理进行了探讨.结果表明,对吸附过程影响较大的因素依次为吸附液Ph值、Cu2 初始浓度、菌体添加量和吸附时间.正交试验得到最佳吸附条件为溶液Ph5.0,吸附时间40min,加菌量5.Og湿菌/L时,对初始浓度为8mmol/L的Cu2 达到最佳吸附率为82.7%.通过对Y17菌体不同处理及解吸实验,初步确定Y17吸附Cu2 的位点在细胞壁,细胞壁表面的-NH2,-COOH基团在其吸附过程中起着重要作用.     

出芽短梗霉菌JB16铅镉吸附特性的研究北大核心

【目的】本文对污染土壤中的耐重金属菌株进行分离鉴定,研究菌株在不同条件下对吸附铅镉的影响因素。【方法】通过生理生化特征及ITS序列分析确定菌株种属,采用平板划线法确定最大耐铅镉浓度并探究菌株吸附的最佳条件;通过准二级动力学、Langmuir和Freundlich等温吸附的模型及红外光谱探究吸附过程。【结果】菌落形态和ITS序列分析鉴定表明,筛选分离的JB16为出芽短梗霉菌(Aureobasidium pullulans),最大耐铅浓度达1500 mg/L,最大耐镉浓度达750 mg/L,最大耐铅镉混合浓度达1500 mg/L和300 mg/L。通过单因素实验(温度、时间、菌龄、pH、湿菌体浓度和初始重金属浓度)得出结论,在温度30℃、时间2 h、菌龄72 h、pH 6、湿菌体浓度5 g/L和初始铅浓度150 mg/L的最佳条件下,菌体对铅的吸附率为88.5%;在温度30℃、时间1 h、菌龄96 h、pH 6、湿菌体浓度5 g/L和初始镉浓度20 mg/L的最佳条件下,菌体对镉的吸附率为59.4%。菌株吸附铅镉过程符合Langmuir吸附模型和准二级动力学模型,为表面单分子层吸附。扫描电镜和红外光谱分析表明,重金属离子对菌体造成影响,吸附前后形态发生变化,细胞表面的羟基、羧基、饱和C−H键和酰胺基等基团参与了吸附过程。【结论】菌株JB16具有一定的铅镉吸附效果,为修复重金属铅镉污染的水体和土壤提供宝贵的菌种资源和数据支持。     

壳聚糖改性竹炭对铜吸附性能研究

为了提高竹炭去除废水中重金属离子能力,采用交联法设计合成新型的磁性壳聚糖改性竹炭复合吸附剂,并采用傅里叶红外光谱对改性竹炭复合吸附剂进行表征,同时开展不同Cu2+初始浓度、吸附剂投加量、吸附时间、pH和温度等因素对Cu2+吸附去除率的影响。结果表明,吸附效率与Cu2+初始浓度和吸附剂投加量成正效应;吸附平衡时间约8 h;在作用温度范围内,吸附效率随温度升高而上升;pH为7时吸附效果最好。振荡条件吸附效果优于静置处理。该结果为废水重金属深度处理及水环境保护提供依据。     

废啤酒酵母吸附水溶液中Cu2+的性能及机理研究

用废啤酒酵母吸附水溶液中Cu2+,考察了溶液pH值、Cu2+浓度和吸附时间对Cu2+吸附的影响。结果表明：废啤酒酵母吸附Cu2+在4-6个小时内达到吸附平衡,酸性条件利于吸附,以pH为5时最佳,吸附等温曲线符合Langmuir模式。用电位滴定及FTIR分析的方法确定生物吸附剂主要含有磺酸基、羧基及氨基等功能团。生物吸附剂对Cu2+的吸附以单分子层的化学吸附为主,功能团在不同的pH条件下呈现不同的电离性能,在吸附过程中发挥重要作用。     

1株鞘细菌的分离筛选及对铅离子吸附条件的研究

通过单因素试验设计,探讨了不同鞘细菌添加量、初始浓度的铅离子溶液、吸附时溶液的温度和p H对鞘细菌吸附铅离子的影响。在此基础上,采用4因素3水平正交试验设计,进一步探讨鞘细菌对铅离子吸附影响的主要因素及最佳吸附组合。试验结果表明,最佳吸附组合为鞘细菌制备液添加量0.3 g/L、吸附溶液中铅离子初始浓度10 mg/L、摇床振荡吸附温度30℃以及吸附液p H 8。在此条件下,鞘细菌吸附铅离子的吸附量为3.09 mg/g,吸附率达92.74%。     

细菌吸附Pd2+的研究

从不同来源的细菌菌株中筛选获得一株吸附Pd²⁺能力较强的菌株R08,经鉴定为地衣芽孢杆菌(\%Bacillus licheniformis)\%R08。R08死菌体吸附Pd²⁺的最适pH值为3.5,其吸附作用是一种快速而非依赖温度的过程。吸附作用受菌体浓度和Pd²⁺浓度影响。在起始Pd²⁺浓度200mg/L\,菌浓度0.4g/L\,pH35和30℃条件下,吸附45min,吸附量为2248mg/g。透射电镜观察显示,R08死菌体能够还原Pd²⁺成Pd0颗粒。红外光谱分析表明,细胞壁上的COO－和ＨＰＯ４２－基团可能与Pd²⁺的生物吸附有关。     

啤酒废酵母对镉离子的吸附研究

以啤酒酿造厂的啤酒废酵母为生物吸附剂,研究啤酒废酵母对Cd2 的生物吸附行为。利用原子吸收光谱法测定Cd2 含量。结果表明,啤酒废酵母吸附Cd2 受吸附时间、吸附温度、溶液pH值、酵母添加量和Cd2 起始浓度等因素的影响。实验确定了啤酒废酵母对Cd2 的最佳吸附条件。即:pH值6,Cd2 浓度为50mg/L,酵母添加量为1.0g/L,吸附温度25℃,吸附时间30min,此时啤酒废酵母对Cd2 的吸附量可达42.92mg/g干酵母。吸附Cd2 的啤酒废酵母用1.0mol/L的HCl解吸,解吸率达75.46%。对未吸附Cd2 的空白酵母和吸附Cd2 的酵母进行红外光谱分析,结果显示啤酒废酵母吸附Cd2 后羟基和羧基吸收峰发生明显变化,因此认为羟基和羧基在生物吸附中起着重要作用。     

耐性真菌HA吸附铅、锌的影响因素及吸附机理研

【目的】从铅锌矿区分离筛选出耐铅锌性菌株,并研究其吸附铅、锌的影响因素及吸附机理,为重金属污染微生物修复提供参考。【方法】以从铅锌矿区筛选出的耐铅锌真菌HA作为试验菌株,考察影响其对铅、锌去除能力的主要因素(初始浓度、pH、接种量),同时通过等温吸附模型、动力学分析及红外光谱分析探讨其相关的吸附机理。【结果】经鉴定,从矿区筛选的对Pb2+、Zn2+有较强耐性的菌株HA为米曲霉(Aspergillus oryzae);在初始铅、锌浓度的实验范围内(100-800mg/L),HA对铅、锌离子的去除率随着其初始浓度增加而减小,25h后HA的生长进入平稳期,且对铅、锌离子的去除率趋于稳定。当铅、锌初始浓度为100mg/L、pH为5.0时,HA对铅、锌离子的去除率均达到最高,分别为97.8%、54.1%;当HA接种量为1mL时,其对铅、锌去除率的增长率达到最大。HA对铅、锌的吸附过程满足Langmuir吸附模型,其吸附以单层吸附为主。在动态吸附过程中,HA对Pb2+、Zn2+离子吸附性能与准二级动力学吸附方程的拟合程度更高,且对Pb2+的吸附效果明显高于Zn2+。红外光谱分析表明,HA细胞中羟基、烷基、酰胺基、羰基、磷酸基等参与了Pb2+、Zn2+的吸附过程。【结论】HA是一株对铅、锌有较强吸附能力的真菌,其吸附铅、锌影响因素及吸附机理研究结果将为重金属污染微生物修复提供指导。     

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。     

植物乳杆菌对重金属Pb~(2+)、Cr~(6+)和Cu~(2+)的耐受性与吸附作用相关性比较

从四川矿区泡菜样品中分离得到1株对重金属铅(Pb)、铬(Cr)和铜(Cu)具有较高耐受性的菌株,经16S rDNA初步鉴定为1株植物乳杆菌。研究重金属铅、铬和铜对该植物乳杆菌的最小抑制浓度(MIC)。比较不同初始pH、初始离子浓度、吸附时间和菌体加入量对植物乳杆菌吸附3种重金属的影响,探讨MIC与吸附作用相关性。使用MIC的方法测定重金属对该菌的最小抑制浓度,原子吸收法测定对重金属的吸附效果。研究表明,该菌对Pb~(2+)、Cr~(6+)和Cu~(2+)的耐受性分别为6.67、0.67和2.17 mmol/L;其吸附性最适初始pH分别为4、6和6;最优初始离子浓度分别为100、100和50 mg/L;最优加菌量分别为3、6和5 g/L;最佳吸附时间分别为12、2和8 h。在100 mg/L的初始离子浓度下对Pb~(2+)、Cr~(6+)和Cu~(2+)的吸附率最高分别可达96%、61%和49%。MIC与吸附作用没有明显相关性。结果表明该菌具有优良的吸附性能,为今后含有乳酸菌的食品或饲料制剂的开发提供了新的乳酸菌种。     

Enhanced and selective adsorption of Pb2+ and Cu2+ by EDTAD-modified biomass of baker's yeast

Enhanced and selective removal of Pb2+ and Cu2+ in the presence of high concentration of K+, Na+, Ca2+ and Mg2+ were achieved by adsorption on biomass of baker's yeast modified with ethylenediaminetetraacetic dianhydride (EDTAD). The modified biomass was found to have high adsorption capacities and fast rates for Pb2+ and Cu2+, and it also displayed consistently high levels of metal uptake over the pH range from 2.7 to 6.0. From Langmuir isotherm, the adsorption capacities for Pb2+ and Cu2+ were found to be 192.3 and 65.0 mg g(-1), respectively, which are about 10 and 14 times higher than that of the unmodified biomass. Competitive biosorption experiments showed that the co-ions of K+, Na+, Ca2+ and Mg2+ had little effects on the uptake of Pb2+ and Cu2+ even at the concentration of 1.0 mol L(-1). The adsorbed Pb2+ and Cu2+ on the modified biomass could be effectively desorbed in an EDTA solution, and the regenerated biomass could be reused repeatedly with little loss of the adsorption capacity.     

Biosorption of chromium, copper, manganese and zinc by Pseudomonas aeruginosa AT18 isolated from a site contaminated with petroleum

The study describes the sorption of Cr, Cu, Mn and Zn by Pseudomonas aeruginosa AT18 isolated from a site contaminated with petroleum and heavy metals. The concentrations studied were 50, 49, 60 and 70 (mg L(-1)) for Cr, Cu, Mn and Zn, respectively. The solution pH and ionic strength were very important factors in the metal biosorption performance and the biosorption capacity of P. aeruginosa AT18 for Cr3+,Cu2+, Mn2+ and Zn2+. In aqueous solution, the biosorption increased with increasing pH in the range 5.46-7.72. The results obtained in the experimental assays show that P. aeruginosa AT18 has the capacity for biosorption of the metallic ions Cr3+, Cu2+ and Zn2+ in solutions, although its capacity for the sorption of manganese is low (22.39 mg Mn2+/g of biomass) in comparison to the Cr3+, Cu2+ and Zn2+ ions, as shown by the individual analyses. However, 20% of the manganese was removed from an initial concentration of 49.0 mg L(-1), with a Qm value similar to that obtained in solutions containing mixtures of Cr3+, Cu2+, Mn2+and Zn2+. The chromium level sorbed by P. aeruginosa AT18 biomass was higher than that for Cu, Mn and Zn, with 100% removal in the pH range 7.00-7.72 and a Qm of 121.90-200.00 mg of Cr3+/g of biomass. The removal of Cr, Cu and Zn is also a result of precipitation processes.     

Biosorption characteristics of Aspergillus flavus biomass for removal of Pb(II) and Cu(II) ions from an aqueous solution

The Pb(II) and Cu(II) biosorption characteristics of Aspergillus flavus fungal biomass were examined as a function of initial pH, contact time and initial metal ion concentration. Heat inactivated (killed) biomass was used in the determination of optimum conditions before investigating the performance of pretreated biosorbent. The maximum biosorption values were found to be 13.46 +/- 0.99 mg/g for Pb(II) and 10.82 +/- 1.46 mg/g for Cu(II) at pH 5.0 +/- 0.1 with an equilibrium time of 2 h. Detergent, sodium hydroxide and dimethyl sulfoxide pretreatments enhanced the biosorption capacity of biomass in comparison with the heat inactivated biomass. The biosorption data obtained under the optimum conditions were well described by the Freundlich isotherm model. Competitive biosorption of Pb(II) and Cu(II) ions was also investigated to determine the selectivity of the biomass. The results indicated that A. flavus is a suitable biosorbent for the removal of Pb(II) and Cu(II) ions from aqueous solution.     

Application of dried sewage sludge as phenol biosorbent

The aim of this work was to determine the potential application of dried sewage sludge as a biosorbent for removing phenol from aqueous solution. Results showed that biosorption capacity was strongly influenced by the pH of the aqueous solution with an observed maximum phenol removal at pH around 6-8. Biosorption capacity increased when initial phenol concentration was increased to 110 mg/L but beyond this concentration, biosorption capacity decreased suggesting an inhibitory effect of phenol on biomass activity. Biosorption capacity decreased from 94 to 5 mg/g when biosorbent concentration was increased from 0.5 to 10 g/L suggesting a possible competitive effect of leachable heavy metals from the sludge. The effect of Cu2+ on biosorption capacity was also observed and the results confirmed that the phenol biosorption capacity decreased when concentration of Cu2+ in the sorption medium was increased up to 15 mg/L. Desorption of phenol using distilled deionized water was less than 2% suggesting a strong biosorption by the biomass.     

白腐真菌吸附铅的研究

含重金属废水的传统处理方法有化学沉淀法、离子交换法、吸附法、电解法和膜分离法等,它们虽然也能达到一定的净化效果,但因过程繁琐并易造成二次污染而不够理想,尤其是金属离子浓度较低时,往往操作费用和原材料成本相对过高。近年来采用生物吸附法去除废水中的重金属...     

Copper biosorption by Auricularia polytricha

AIMS: The objective of the present study was to determine the optimum conditions for copper (Cu) biosorption by Auricularia polytricha mycelium in view of its immobilization in polyvinyl alcohol (PVA). METHODS AND RESULTS: The adsorption of Cu(II) onto A. polytricha was studied in batch with respect to initial pH, temperature, adsorption time, initial metal ion and biomass concentration. At optimal adsorption conditions, biomass was immobilized in PVA in column and a biosorption capacity of about 90% was obtained. CONCLUSIONS: Auricularia polytricha strain could successfully be used as Cu biosorbent. SIGNIFICANCE AND IMPACT OF THE STUDY: The low cost and simplicity of the technique make it suitable for the detoxification of contaminated effluents before their environmental discharge.     

Biosorption of cadmium and lead ions by ethanol treated waste baker's yeast biomass

The biosorption of cadmium and lead ions from artificial aqueous solutions using waste baker's yeast biomass was investigated. The yeast cells were treated with caustic, ethanol and heat for increasing their biosorption capacity and the highest metal uptake values (15.63 and 17.49 mg g(-1) for Cd(2+) and Pb(2+), respectively) were obtained by ethanol treated yeast cells. The effect of initial metal concentration and pH on biosorption by ethanol treated yeast was studied. The Langmuir model and Freundlich equation were applied to the experimental data and the Langmuir model was found to be in better correlation with the experimental data. The maximum metal uptake values (qmax, mg g(-1)) were found as 31.75 and 60.24 for Cd(2+) and Pb(2+), respectively. Competitive biosorption experiments were performed with Cd(2+) and Pb(2+) together with Cu(2+) and the competitive biosorption capacities of the yeast biomass for all metal ions were found to be lower than in non-competitive conditions.     

Application of Arthrospira (Spirulina) platensis biomass for silver removal from aqueous solutions

The cyanobacterium Arthrospira (Spirulina) platensis was used to study the process of silver biosorption. Effects of various parameters such as contact time, dosage of biosorbent, initial pH, temperature, and initial concentration of Ag(I) were investigated for a batch adsorption system. The optimal biosorption conditions were determined as pH 5.0, biosorbent dosage of 0.4 g, and initial silver concentration of 30 mg/L. Equilibrium adsorption data were analyzed by the Langmuir and Freundlich models – however, the Freundlich model provided a better fit to the experimental data. The kinetic data fit the pseudo-second-order model well, with a correlation coefficient of 0.99. The analysis of thermodynamic parameters (ΔG°, ΔH° and ΔS°) revealed that the adsorption process of silver ion by spirulina biomass was exothermic and spontaneous (ΔG° < 0), and exothermic (ΔH° < 0) process. The biosorption capacity of biomass A. platensis serves as a basis for the development of green technology for environmental remediation.