普通小球藻对复合重金属镉和铬的生物吸附及影响因素

【背景】微藻对重金属具有极强的耐受性,而且有较高的吸附率,是一种优良的生物吸附剂。【目的】探究环境因素对小球藻吸附镉离子(Cd²⁺)和铬离子(Cr³⁺)的影响。【方法】以普通小球藻（Chlorella vulgaris）在不同条件下对重金属离子的吸附率为基准,利用CdCl₂·2H₂O和CrCl₃·7H₂O提供重金属离子,根据不同处理下小球藻吸附率的变化情况探讨重金属离子浓度、p H和温度等环境因素对普通小球藻吸附Cd²⁺和Cr³⁺的影响。【结果】在温度为30°C、p H值为5.5、Cd²⁺和Cr³⁺浓度分别为0.4 mg/L和4.0 mg/L及生物量为0.59 g/L的条件下,普通小球藻对复合Cd²⁺和Cr³⁺吸附率达到最大,吸附率分别达到84.5%和75.2%,同时发现普通小球藻对Cd²⁺的吸附率大于C...     

粗毛栓菌和蜡状芽孢杆菌及其共固定菌对Pb2+的吸附

将粗毛栓菌菌丝球与蜡状芽孢杆菌共固定为共固定菌.以粗毛栓菌菌丝球、蜡状芽孢杆菌和共固定菌为研究对象,测定不同吸附时间、初始pH、吸附剂浓度和Pb²⁺浓度对3种生物吸附剂吸附Pb²⁺的影响,并将3种生物吸附剂吸附Pb²⁺前后的红外吸收光谱进行分析比较.结果表明： 在吸附剂浓度为2 g·L^-1、pH为5.0、Pb²⁺浓度为50 mg·L^-1条件下对Pb²⁺吸附1 h效果良好,其吸附率分别为71.7%、91.0%和96.9%.生物吸附剂红外光谱主要由蛋白质、碳水化合物和含硫、磷酸基团的吸收带组成,表明对Pb²⁺吸附起主要作用的官能团是羟基、羧基、磷酸基和含硫基团.     

改性粉煤灰对废水中镉的吸附作用

以工业固废粉煤灰(FA)为原料,将其与NaOH和Ca(OH)₂混合后,在250 ℃下焙烧1.5 h,制得改性粉煤灰(MFA).利用扫描电镜(SEM)、能量色散X射线光谱仪(EDS)、X-射线衍射仪(XRD)、全自动比表面积分析仪(BET)和傅里叶红外光谱仪(FTIR)等技术分析MFA的理化性质.BET分析表明,MFA的比表面积比FA增大了20.6倍.SEM分析表明,FA表面玻璃相溶解,表面粗糙,具有多孔结构.FTIR分析表明,-OH官能团在Cd²⁺的吸附过程中具有重要作用.静态吸附试验研究表明,当MFA的投加量为0.2 g、Cd²⁺初始浓度为100 mg·L^-1、溶液pH为7、25 ℃下吸附90 min时,Cd²⁺的去除率达到97.3%;共存阳离子(K⁺、Na⁺、Mg²⁺和Ca²⁺)均会抑制MFA对Cd²⁺的吸附,其中Ca²⁺的抑制作用最强.Langmuir等温吸附模型和准二级吸附动力学方程能较好地描述Cd²⁺在MFA上的吸附行为,且最大吸附量为55.77 mg·g^-1.热力学研究表明,MFA对Cd²⁺的吸附是一个自发的吸热过程.MFA吸附能力优于FA,在废水处理方面有一定的应用前景.     

不同炭化温度制备的蚕丝被废弃物生物炭对重金属Cd2+的吸附性能

以蚕丝被废弃物为原料,在300、500和700 ℃高温缺氧条件下热解炭化制备成3种生物炭(BC300、BC500和BC700).利用扫描电镜(SEM)、傅里叶红外光谱仪(FT-IR)、X-射线衍射仪(XRD)、比表面积分析仪等对其理化性质进行表征,并研究了不同温度下制备的生物炭对溶液中Cd²⁺的吸附特性.结果表明: 随着炭化温度上升,BET比表面积、pH、灰分均增大,生物炭表面形态结构越来越不规则.XRD结果显示:不同温度下获得的生物炭中均含有一定量的方解石,FT-IR光谱图上的峰主要为-OH和方解石典型的吸收峰;pH对生物炭吸附Cd²⁺的影响不大;Langmuir方程能更好地拟合3种生物炭对Cd²⁺的吸附等温过程,其最大吸附量分别为25.61、52.41和91.07 mg·g^-1.3种生物炭对Cd²⁺吸附过程均更符合准二级动力学方程,且BC700对Cd²⁺的吸附效果最佳.进一步研究离子浓度及阳离子共存对BC700吸附Cd²⁺的影响,结果显示: NaCl浓度越高,对Cd²⁺的吸附抑制越明显;共存阳离子中,Ca²⁺和Mg²⁺对Cd²⁺的吸附抑制更明显,而K⁺几乎无影响.因此,以蚕丝被废弃物制备的生物炭作为去除水体中Cd²⁺的吸附剂具有较强的应用潜力.     

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。     

Cr3+对盐藻(Dunaliella salina)生长及营养品质的影响

以盐藻Dunaliella salina为材料,设定0ìg·L^-1、3ìg·L^-1、12ìg·L^-1、50ìg·L^-1、200ìg·L^-1和800ìg·L^-16个添加Cr³⁺浓度处理,分析测定了不同铬浓度下盐藻的生物量(细胞密度).蛋白质、â胡萝卜素和可溶性糖含量.研究结果表明,中低量添加Cr³⁺对盐藻的生长有一定的促进作用,在50ìg·L^-1和200ìg·L^-1Cr³⁺条件下,盐藻的生物量高于对照,中低量添加Cr³⁺对盐藻的生长有一定的促进作用,盐藻蛋白质含量比对照分别提高3.06%和6.55%,Cr³⁺浓度在200ìg·L^-1时,盐藻的â胡萝卜素和可溶性糖含量比对照分别提高3.93%和2.38%,适当添加Cr³⁺可提高盐藻蛋白质、â胡萝卜素和可溶性糖含量,有效改善盐藻的营养品质.     

生物吸附剂-活性污泥法吸附处理含铬电镀废水

研究了复合生物吸附剂FY01和活性污泥处理含铬电镀废水的吸附性能.结果表明,铬的生物吸附分为快速15g·L^-1污泥对通用电镀废水、康力电镀废水中铬的联合去除率分别高达97.7%和88.1%,比两者单独处理电镀废水的吸附和缓慢吸附两个阶段.FY01具有良好的吸附稳定性,对废水的pH适应能力强,当pH=2.5~6时,10g·L^-1FY01和5g·L^-1污泥曝气处理2000mL电镀废水2h后,68.6mg·L^-1含铬通用电镀废水中总铬的去除率达71.5~75.6%;50.1mg·L^-1含铬康力电镀废水中总铬的去除率高达80.0~90.0%.FY01和活性污泥具有良好的协同促进作用,10g·L^-1FY01和除铬率总和分别高出39.8%、44.6%.     

Cr3+,Cr6+及其复合污染对狐尾藻的毒害作用

采用急性毒害水培法,研究比较了不同浓度的Cr⁶⁺,Cr³⁺单一及复合处理对狐尾藻不定根和叶片生理生态的影响。实验结果表明:1)当浓度≤1mg·L^-1时,Cr³⁺对不定根的生长表现出促进作用,数量增加,长度增长。而Cr⁶⁺及复合处理系列对不定根却表现出强烈的抑制作用,在高浓度时甚至使其生长停止;2)叶绿素含量在1mg·L^-1Cr³⁺培养液中达到最大值,随Cr⁶⁺及复合处理浓度的增大而呈连续下降趋势;3)可溶性蛋白含量在三种处理方式中都表现出抛物线形式,复合处理组在1mg·L^-1时使蛋白含量出现高峰;4)细胞内超氧阴离子产生速率,膜脂过氧化水平与污染浓度和时间呈显著正相关;5)随着处理浓度的增加,SOD,OD,CAT活性先升后降,但其高峰分别出现在处理浓度为1mg·L^-1,10mg·L^-1,5mg·L^-1时;6)研究证实,Cr⁶⁺,Cr³⁺复合处理对狐尾藻的毒害作用较单一Cr⁶⁺,Cr³⁺显著,二者表现出协同作用,而其中Cr⁶⁺毒性大于Cr³⁺。     

一株高效菲降解菌的筛选及降解条件研究

从南京某石化厂排污口附近采集土样,以菲为碳源的选择性培养基分离筛选到一株菲高效降解菌F10a,根据形态和生理生化特性初步鉴定为芽孢杆菌属,并对其降解菲的特性及各种影响因素进行了研究.结果表明,F10a在50 mg·L^-1的条件下,28 ℃振荡培养27 h,菲的降解率达到98.12%;静置培养8 h,菲的降解率达到98.7%.pH值分别为、6、8时,F10a对菲具有良好的降解效能;pH值为10时F10a不生长.Zn²⁺与Pb²⁺的存在不影响F10a的降解效能,Cu²⁺可以延缓菲的降解,Cr²⁺对F10a有毒性.F10a在菲浓度为200 mg·L^-1时,28 ℃振荡培养8 h,降解率为99.6%.菲的降解程度与细菌数量的增长呈正相关关系.     

胁迫时间与非毒性离子对重金属抑制拟南芥种子发芽及幼苗生长的影响

测定了Hg²⁺、Cd²⁺、Cu²⁺、Pb²⁺单一重金属胁迫对拟南芥种子发芽和幼苗生长的影响.结果表明,重金属对幼苗生长的毒性大于对种子发芽的毒性,以抑制种子发芽的IC₅₀为指标,4种重金属的毒性顺序为Hg²⁺＞Cd²⁺＞Pb²⁺/Cu²⁺,以幼苗生长为指标,则毒性顺序为:Cu²⁺＞Hg²⁺＞Cd²⁺/Pb²⁺,并随着胁迫时间延长,种子萌发率下降.此外,不同重金属在不同发芽时段对种子的毒性也不尽相同,Cd²⁺的毒性在种子吸水后的0～12 h大于12～24 h,而Hg²⁺毒性在12～24 h大于0～12 h,其中,种皮对减轻重金属毒性起着十分重要的作用.通过非毒性离子(Ca²⁺、Mg²⁺、K⁺、Na⁺)与重金属离子(Hg²⁺、Cd²⁺、Cu²⁺、Pb²⁺)交互作用对拟南芥种子发芽及幼苗生长效应的研究发现, mmol·L^-1的Ca²⁺、Mg²⁺、K⁺、Na⁺可以增强Hg²⁺对种子发芽的毒性,但对Cd²⁺的毒性却没有影响.对于幼苗来说,Ca²⁺、Mg²⁺、K⁺、Na⁺可以显著增强Hg²⁺的毒性,Ca²⁺可以缓解Cd²⁺的毒性,但却增加Cu²⁺的毒性,K⁺可以缓解Pb²⁺对幼苗的毒害作用.最后,本文对重金属的毒害机理进行了探讨.     

改性沸石粉吸附去除微污染水中Ni(Ⅱ)的试验研究

用壳聚糖改性天然沸石粉,制备了改性沸石粉吸附材料,对微污染水源水中微量镍(Ⅱ)的吸附去除进行了研究。考察了吸附时间、沸石粉投加量、镍(Ⅱ)初始浓度以及原水pH 值等因素对镍(Ⅱ)去除效果的影响。结果表明,改性沸石粉对镍(Ⅱ)的去除效果明显优于天然沸石粉;当镍(Ⅱ)初始浓度低于0.2 mg/L 时, 投加1.5 g/L 壳聚糖改性沸石粉,经20 min 吸附后,水中镍(Ⅱ)的剩余浓度低于 0.02 mg/L,可满足《生活饮用水卫生标准》(GB5749-2006)中的要求;提高水的pH 值有利于两种沸石粉对镍(Ⅱ)的去除。另外,两种沸石粉对镍(Ⅱ)的吸附过程均符合Freudlich 等温吸附模型,且改性沸石粉的吸附指数更小,其吸附能力更强。     

Vitamin B6 compounds prevent the death of yeast cells due to menadione, a reactive oxygen generator

The antioxidant effects of natural vitamin B(6) compounds on Schizosaccharomyces pombe cells treated with menadione sodium bisulfite (water-soluble menadione and a generator of superoxide, MSB) and the mechanism underlying the function were examined with the yeast cells treated with pyridoxal 5'-phosphate. Vitamin B(6) compounds showed no ex vivo reactivity toward MBS at pH 5.5 or 7.0. The yeast cells showed no growth in the medium containing 1.0 mM MSB. The coexistence of 1.0 mM of each vitamin B(6) compound supported the growth of the yeast cells. The efficacy order was pyridoxal 5'-phosphate>/=pyridoxamine 5'-phosphate>pyridoxamine>pyridoxal>/=pyridoxine. The first three compounds showed higher antioxidant activity than vitamin C did. Pyridoxal 5'-phosphate prevented the reduction of the glutathione content in the MSB-treated cells and, in turn, suppressed the increases in peroxide and thiobarbituric acid reactive substances in the yeast cells and increased the viability of the yeast cells under oxidative stress. The antioxidant function of pyridoxal 5'-phosphate was not dependent on the phosphorelay pathway, which finally triggers the expression of the catalase gene.     

Functionalization of PVC membrane with ss oligonucleotides for a potentiometric biosensor

A novel application of a single stranded (ss) oligonucleotide as an active component of polymeric membrane in an ion-selective electrode (ISE) is described. The original oligonucleotides, oligo(dA)(15), modified by cholesterol, triphenylmethyl and hexadecyl derivatives, were immobilized into poly(vinyl chloride) (PVC) membrane using extraction protocol. In parallel, the adsorption protocol was used to immobilize unmodified oligo(dA)(15) on the PVC membrane based on tridodecylmethyammonium chloride (TDDMA(+)Cl(-)). Immobilization of ss oligonucleotide probe through spacer was more effective for the potentiometric detection of the hybridization between complementary oligonucleotides. It was found that cholesterol-oligo(dA)(15) modified membranes were sensitive toward complementary oligo(dT)(15) in the concentration range 2-80 nM at pH 7. An explanation for the detection mechanism is proposed.     

Using pretreated chestnut endothelium to adsorb lead and cadmium ions from water

The nature chestnut endothelium, as waster source from chestnut (Castaneamollissima) has pigment effecting the process of adsorbing heavy metalions, and the decolorized endothelium has low adsorption capacity. In order to raise the adsorption capacity of heavy metal ions, the discolor endothelium was pretreated by acidic formaldehyde, cis-butenedioic acid and irradiation. Thermodynamic and kinetics model was fitted to the adsorption of Pb (II) and Cd(II) ions onto modified chestnut endothelium by cis-butenedioic acid. Three independent variables including pH, adsorption time and contact temperature were selected as affecting factors to Response Surface. The modified experiment results showed adsorption rate of Pb(II) and Cd(II) ions on the chestnut endothelium modified by 0.5?mol/L cis-butenedioic acid was higher than other modified methods. Thermodynamic and kinetics model was fitted with Langmuir and Pseudo-second-order kinetic model, respectively. 59.23?°C of the adsorption temperature, the 5.72?h of adsorption time and the 6.16 of pH are the optimized conditions of the adsorption rate of Pb²⁺ on modified chestnut endothelium. 55.93?°C of the adsorption temperature, the 4.43?h of adsorption time and the 6.06 of pH are the optimized adsorption conditions of Cd²⁺. Under the optimized condition, the experiment value of the adsorption of Pb²⁺ and Cd²⁺ was 99.76% and 98.90%, respectively, which are close to the predicted value. The FTIR indicated that CO, OH and CH involved in the adsorption process of Pb²⁺ and Cd²⁺.     

Characterization of Aqueous Pb(II) and Cd(II) Biosorption on Native and Chemically Modified Alstonia macrophylla Saw Dust

This study was conducted in order to understand the mechanism of Cd and Pb adsorption in aqueous solutions by raw and modified saw dust (SD) of Alstonia macrophylla. The biosorbent was characterized by Boehm titration, specific surface area, scanning electron microscopy (SEM), X-ray energy dispersion (EDAX), and Fourier transform infrared (FTIR) analyses. SD was treated using organic acids and bases. Batch studies were conducted for raw and modified SD to determine the effect of initial concentration, pH, ionic strength, and contact time on metal adsorption. The specific surface area and total basic and acidic groups of SD were 77 m²/g and 1521 and 2312 μmol/g, respectively. The adsorption of both metals onto SD was pH dependent. No ionic strength dependency was observed in adsorption of Cd and Pb at pH >6, indicating inner sphere surface complexation. Monolayer adsorption is dominant in both metal sorptions by SD. Furthermore, there is no competition between metals on adsorption and raw SD was found to be suitable for removal of Cd and Pb as compared to organic acid– or base-treated SD. Maximum adsorption capacity of SD for Cd and Pb were 30.6 and 204.2 mg/g, respectively. Results indicate that the A. macrophylla SD can be considered as a potential material for metal ion removal from wastewater.     

极端耐热木聚糖酶基因在大肠杆菌和毕赤酵母中的高效表达

以海栖热袍菌 (Thermotoga maritima) MSB8菌株基因组DNA为模板,通过PCR扩增出木聚糖酶（XylanaseB）基因, 将此基因克隆至大肠杆菌表达载体pET_28a（+）和毕赤酵母表达载体pPIC9K,并分别转化大肠杆菌 BL21和毕赤酵母GS115。该木聚糖酶在大肠杆菌细胞中表达量高, 但不能分泌; 而在毕赤酵母细胞的表达产物可分泌至胞外。酶学性质分析表明,此酶分子量约为40kD,其最适反应温度为90℃, 最适反应pH值为6.65,且在碱性条件下稳定,具有重要的工业应用前景。     

Photocontrol of urease-collagen membrane activity.

(1) Urease (EC 3.5.1.5.) was modified with beta-1-[3,3-dimethyl-6'-nitrospiro-(indoline-2,2'-2H-benzopyrene)] propionic anhydride. Three amino acid residues of urease were modified by the anhydride at a molar ratio of 2000. (2) The activity of modified urease was decreased with ultraviolet irradiation and then restored to the initial activity with visible light irradiation. (3) Modified urease was used to prepare a urease-collagen membrane. The apparent Michaelis constant (Km) of the modified urease-collagen membrane ultraviolet light was identical to that of the membrane under visible light. (4) The optimum pH of the modified urease-collagen membrane was displaced toward lower pH values with ultraviolet irradiation. At higher ionic strength, the pH activity curve of the membrane was displaced toward higher pH values. (5) The thermostability of urease was increased with its modification.     

活性绿19修饰花生壳粉微球的制备及对溶菌酶的吸附

以天然产物花生壳粉作为基质,环氧氯丙烷为交联剂,活性绿19(Reactive Green 19,简称RG19)为修饰剂,制备了新型的生物吸附剂RG19修饰花生壳粉微球,比较了RG19修饰花生壳粉前后对溶菌酶的吸附性能,包括吸附溶液的pH,溶菌酶的初始浓度,吸附时间,温度及NaCl的浓度对吸附的影响。结果表明,用25.0 mgRG19修饰花生壳粉微球处理溶菌酶溶液10 mL,pH值7.4,吸附时间4 h的条件下,对溶菌酶的吸附量是149.6mg·g-1,其酶活力保持率为96.4%,而未修饰的花生壳粉微球对溶菌酶的吸附量只有23.6 mg·g-1,修饰后是修饰前的6.3倍。在上述条件下从鸡蛋清中分离纯化溶菌酶,纯化倍数为31.0,收得率为64.2%。而且该吸附剂的复用性好。     

Amperometric detection of insulin at renewable sol-gel derived carbon ceramic electrode modified with nickel powder and potassium octacyanomolybdate(IV)

A renewable three-dimensional chemically modified carbon ceramic electrode (CCE) containing nickel powder and K4[Mo(CN)8] was constructed by sol-gel technique. The electrochemical properties and stability of modified electrode was evaluated by cyclic voltammetry in pH range 4-10. The redox couple of [Mo(CN)8] (4-/3-) was shown both as a solute in electrolyte solution and as a component of a carbon based conducting composite electrode. The apparent electron transfer rate constant (ks) and transfer coefficient (alpha) were determined by cyclic voltammetry and they were about 17.1 and 0.57 s(-1), respectively. The catalytic activity of the modified CCE toward insulin oxidation was investigated at pH range of 3-8 by cyclic votammetry. The modified electrode showed excellent electrocatalytic activity toward insulin electroxidation at physiological pH value. The modified electrode was used for insulin detection chronoamperometrically at pH 7. Under optimized condition in amperometry method, the concentration calibration range, detection limit and sensitivity were 0.5-500 nM, 0.45 nM and 6140 nA/microM, respectively. Flow injection amperometric determination of insulin at pH 7.4, at this modified electrode yielded a calibration curve with the following characteristics, linear dynamic range 100-500 pM; sensitivity 8.1 nA/nM and detection limit 40 pM (based on S/N = 3). The inherent stability at wide pH range, high sensitivity, low detection limit, low cost and ease of preparation are of advantageous of this insulin sensor. This sensor indicates great promise for monitory insulin in chromatographic effluents.     

Removal of Ca(II) and Mg(II) from aqueous single metal solutions by mercerized cellulose and mercerized sugarcane bagasse grafted with EDTA dianhydride (EDTAD)

In a previous work, chemically modified cellulose (EMC) and sugarcane bagasse (EMMB) were prepared from mercerized cellulose (MC) and twice-mercerized sugarcane bagasse (MMB) using ethylenediaminetetraacetic dianhydride (EDTAD) as modifying agent. In this work we described in detail the modification of these materials in function of reaction time and EDTAD amount in the reaction media. The resistance of ester bond at pH 1, 2, 11, and 12 was also evaluated by FTIR. The results were used to model the hydrolysis process and a kinetic model was proposed. The modified materials (EMMB and EMC) were used to adsorb Ca²⁺ and Mg²⁺ ions from aqueous single solutions. The adsorption isotherms were developed at two pH values. These materials showed maximum adsorption capacities for Ca²⁺ and Mg²⁺ ions ranging from 15.6 to 54.1 mg/g and 13.5 to 42.6 mg/g, respectively. The modified material from sugarcane bagasse (EMMB) showed larger maximum adsorption capacities than modified material from cellulose (EMC) for both metals.