抗铅锌功能菌生长菌株和干菌体吸附Pb2+、Zn2+性能优化及机理分析

【目的】针对湖南资兴铅锌矿污染问题,筛选本土耐性菌株用作生物修复。【方法】供试菌株J3筛选自湖南资兴铅锌矿区的尾砂矿矿渣,利用正交实验分析其生长菌株及干菌体最佳吸附条件以优化其吸附效果,同时对相关数据进行动力学拟合以探讨其吸附机理,最后结合形态观察和18S rRNA基因序列分析对其进行分类鉴定。【结果】在最佳条件下,J3生长菌株对Pb2+和Zn2+的去除率分别为92.2%和87.7%;干菌体对Pb2+和Zn2+去除率分别为72.6%和23.8%,反应动力学模型研究表明,生长菌株吸附过程中吸附速率受重金属浓度影响,对Zn2+吸附主要为颗粒内扩散作用;干菌体对Pb2+吸附推测为膜扩散和颗粒内扩散作用,而对Zn2+的吸附则由膜扩散控制。根据形态特征和系统发育分析,J3初步鉴定为虫生轮枝菌。【结论】生长菌株吸附效果好于干菌体,二级动力学方程拟合结果可为生物吸附反应器的设计提供理论参考和实践指导。     

一株耐铅、锌、铬菌株的分离鉴定及其吸附能力

【背景】采矿带来的土壤重金属污染问题对生态环境和人类健康产生了极大的危害,因此矿区重金属污染问题亟待解决。生物修复法成本低、资源广、没有二次污染,是修复土壤重金属污染的有效途径。【目的】以山东省曲阜市某煤矸石山周围土壤为材料,采用平板划线法分离筛选一株同时对铅、锌、铬有高耐性且吸附能力强的菌株。【方法】通过形态学特征、生理生化鉴定、分子生物学方法鉴定菌种;采用原子吸收分光光度计测量各重金属的浓度。【结果】鉴定菌株为蜡状芽孢杆菌(Bacillus cereus),命名为Bacillus cereus MZ-11。菌株MZ-11在pH为5.5?8.5、温度为15?45 °C、NaCl质量分数为2%?8%时可正常生长。菌株MZ-11最高耐铅、锌、铬浓度高达1 000、1 200、1 600 mg/L。在培养基中铅、锌、铬3种重金属浓度分别为初始浓度(含Pb2+、Zn2+、Cr6+浓度分别为50、60、80 mg/L)、初始浓度的5倍、10倍、20倍的条件下,MZ-11对Cr6+和Zn2+的吸附比例则随浓度的提高逐渐增大,吸附百分比均在98%?99%以上。对Pb2+的吸附比例有一个最高值,并且Pb2+的浓度为初始浓度的5倍时,MZ-11对Pb2+的吸附比例达最大值97.01%。【结论】菌株MZ-11对铅、锌、铬有高耐性和较好的吸附能力,为生物法修复矿区复合重金属污染和矿区生态环境提供了有力的理论支持。     

三株耐铅锌菌的分离、鉴定及其吸附能力

以铅锌矿渣盆栽试验中长势较好的耐性植物夹竹桃(Nerium indicum)的根际土壤为材料,进行耐铅锌优势菌株的分离鉴定,探讨影响铅锌吸附的因素及其吸附机理。结果表明:(1)从土样中分离筛选出3株耐铅锌菌株(B1、B4、B14),3株菌均能在Pb2+、Zn2+浓度为600 mg·L-1的牛肉膏蛋白胨培养基上生长,经形态和分子生物学鉴定分别为蜡样芽孢杆菌(Bacillus cereus)或炭疽杆菌(Bacillus anthracis)、解硫胺素硫胺素芽孢杆菌(Aneurinibacillus aneurinilyticus)和藤黄微球菌(Micrococcus luteus)。(2)对影响菌株吸附铅、锌的p H、吸附时间、初始菌量3个因素进行分析,发现菌株B1在p H为5.0、吸附时间为50 min、初始菌量为0.06 g时,对Pb2+、Zn2+的去除率分别可达84.22%和70.66%。菌株B4在p H为6.0、吸附时间为50 min、初始菌量为0.18 g时,对Pb2+、Zn2+的去除率分别可达72.63%和54.17%。菌株B14在p H为4.0、吸附时间为60 min、初始菌量为0.10 g时对Pb2+、Zn2+的吸附率分别为77.56%和50.63%。(3)扫描电镜观察和红外光谱分析显示:3株菌对Pb2+、Zn2+的吸附主要是细胞表面的吸附,还存在一定的内部吸收;羟基(O-H)、胺基(N-H)、烷基、酰胺基(CONH-)是吸附、络合或螯合金属离子或原子的主要活性基团,重金属与菌株表面的活性基团结合反应是其吸附Pb2+、Zn2+的主要作用机制。     

乌鲁木齐市道路林带土壤抗重金属细菌的筛选及重金属去除能力

【背景】道路重金属污染问题日益严峻,寻找高效的微生物资源用于环境修复已迫在眉睫。【目的】从乌鲁木齐市道路林带土壤中筛选抗重金属菌株,并对其重金属去除能力进行探究。【方法】使用含5种重金属离子(铅、镉、锌、铜、镍)的4种培养基进行抗性菌株筛选,通过形态学特征和16S rRNA基因序列进行鉴定,采用电感耦合等离子体发射光谱仪(inductively coupled plasma optical emission spectrometer,ICP-OES)检测分离株对重金属离子的去除情况。【结果】4种分离培养基中,TSA是抗重金属菌株筛选的最适培养基,共筛选出16株抗重金属菌,其中4株抗Pb菌、4株抗Cd菌、4株抗Zn菌、3株抗Cu菌和1株抗Ni菌,其抗性分别高达3 000、800、600、300和400mg/L,16株菌中以芽孢杆菌属(Bacillus)数量最多。在初始浓度为700mg/L Pb²⁺下,菌株Pb6的去除率高达92.48%,菌株Pb11、Pb3和Pb9的去除率分别为27.70%、40.37%和58.88%;在200mg/L Cd²⁺...     

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。     

从铅锌矿渣中分离的微生物对重金属吸附特性的研究

从铅锌矿渣中分离到 16种菌 (包括 7株细菌和 9株真菌 ) ,并研究了它们对Zn2 + ,Pb2 + ,Cu2 + 的吸附特性。发现大多数菌株对Pb2 + 与Zn2 + 有不同程度的吸附 ,但对Cu2 + 的吸附能力较小。菌株对Zn2 + 的吸附率大于对Pb2 + 的吸附 ,能吸附Pb2 + 的菌株也能吸附Zn2 + 。pH 4～ 6是真菌吸附金属离子的较好范围 ,细菌仅在pH =5 .0条件下 ,对Pb2 + 与Zn2 + 有吸附。在测试的不同金属离子浓度范围内 (5 0mg/L 相似文献   

一株具有植物促生作用的重金属铅吸附菌的筛选与鉴定

【背景】随着工业化的发展,重金属污染逐渐成为主要的环境污染之一。微生物修复去除重金属污染成为近些年来新兴的修复方法,筛选开发具有良好修复功能的微生物菌株具有重要的现实意义。【目的】筛选具有促进植物生长作用的重金属修复菌株,为生物修复和植物促生等综合开发利用提供微生物资源。【方法】利用选择性培养基从淤泥中筛选重金属铅的抗性菌株,根据形态学观察、生理生化鉴定和16S rRNA基因序列分析对菌株进行分离鉴定,通过单因素分析不同培养条件对菌株生长的影响;采用原子吸收光谱法、比色法及平板对峙法等对菌株的重金属铅吸附率、无机磷溶解能力、吲哚乙酸(indole-3-acetic acid,IAA)分泌及拮抗镰刀菌效果等进行分析。【结果】从污染严重的塘泥中筛选到一株对重金属铅有较好吸附率的菌株,在150 mg/L Pb²⁺浓度下,对Pb²⁺的吸附率达90%以上;初步鉴定该菌株为蜡样芽孢杆菌,命名为SEM-15;菌株还具有较好的溶解无机磷、分泌IAA及拮抗镰刀菌的能力;菌株生长适应性强,可以在pH 10.0的强碱性环境下生长,该菌株具有很好的重金属铅污染修复及促生防病的应用潜力。【结论】菌株SEM-15是一株具有植物促生作用的重金属铅吸附菌株,在重金属污染土壤联合植物修复的应用中可能具有较好的开发价值。     

耐镉甲基营养芽胞杆菌吸附条件的优化及其抗逆性

【目的】对所筛选的1株耐镉甲基营养芽胞杆菌NTGB29进行了环境抗逆性的研究,及影响菌株吸附镉离子效率的条件优化。【方法】以发酵液活菌数为指标,研究其对不同NaCl浓度、酸碱度、镉离子浓度的耐受情况;进一步通过单因素实验和响应面法优化影响菌株镉离子吸附效率的发酵条件;以有效镉离子含量为指标,验证菌株在镉污染土壤中的吸附效果。【结果】结果表明,菌株NTGB29对NaCl浓度、酸碱度、Cd~(2+)浓度的最大耐受值分别为10%、pH11.0、50mg/L;菌株在发酵液初始Cd~(2+)浓度10 mg/L、起始pH 6.4、培养温度37°C、NaCl浓度4.2%、装液量50 mL/250 mL、培养时间24 h时,对Cd~(2+)的吸附率达到79.70%;菌株能有效降低镉污染土壤中的有效镉离子含量,吸附率为29.65%。【结论】菌株NTGB29在较高浓度Cd~(2+)浓度、NaCl浓度及强碱环境条件下仍然能够生长,具有良好的环境抗逆性及Cd~(2+)吸附能力,在镉污染土壤调理剂及微生物功能菌剂的研制方面能够提供有价值的菌种资源。     

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...     

耐铅镉菌株的分离鉴定及其吸附能力

堆肥中添加生物钝化剂是当前降低粪便中重金属生物毒性最为有效的方式之一,为了进一步提高其钝化重金属的能力,文中获得了复合重金属高耐性的钝化剂菌株,并探究其生物学特性和吸附特征。采集猪粪堆肥样品并在改良的牛肉膏培养基中分离和筛选耐铅又耐镉的高耐性菌株,通过形态结合分子生物学鉴定该菌株。该菌株分别在不同pH、温度和盐浓度条件下培养获得其最适的生长条件,进而在该条件下分析其对铅镉吸附的特性。结果获得一株耐铅浓度为600 mg/L、镉浓度为120 mg/L的铅镉复合耐性菌株SC19,该菌株为西地西菌属,其最适生长环境为pH值7.0、温度37℃、盐浓度0.5%。培养36 h的稳定期SC19菌株在吸附时间30min时铅的去除率最高,对铅的最大去除率和吸附量分别为60.7%和329.13mg/g;培养8h的对数期在吸附时间30min时镉的去除率最高,对镉的最大去除率和吸附量分别为51.0%和126.19 mg/g。红外光谱分析显示,SC19菌株对铅镉离子的吸附主要是细胞表面的多种活性基团与金属离子发生络合作用。该研究揭示了SC19菌株有较好的二价态铅镉离子吸附能力,可为生物钝化重金属提供重要的微生物种质资源。     

Cu(II) and Zn(II) ions alter the dynamics and distribution of Mn(II) in cultured chick glial cells

Previous studies revealed that Mn(II) is accumulated in cultured glial cells to concentrations far above those present in whole brain or in culture medium. The data indicated that Mn(II) moves across the plasma membrane into the cytoplasm by facilitated diffusion or counter-ion transport with Ca(II), then into mitochondria by active transport. The fact that 1–10 M Mn(II) ions activate brain glutamine synthetase makes important the regulation of Mn(II) transport in the CNS. Since Cu(II) and Zn(II) caused significant changes in the accumulation of Mn(II) by glia, the mechanisms by which these ions alter the uptake and efflux of Mn(II) ions has been investigated systematically under chemically defined conditions. The kinetics of [⁵⁴MN]-Mn(II) uptake and efflux were determined and compared under four different sets of conditions: no adducts, Cu(II) or Zn(II) added externally, and with cells preloaded with Cu(II) or Zn(II) in the presence and absence of external added metal ions. Zn(II) ions inhibit the initial velocity of Mn(II) uptake, increase total Mn(II) accumulated, but do not alter the rate or extent Mn(II) efflux. Cu(II) ions increase both the initial velocity and the net Mn(II) accumulated by glia, with little effect on rate or extent of Mn(II) efflux. These results predict that increases in Cu(II) or Zn(II) levels may also increase the steady-state levels of Mn(II) in the cytoplasmic fraction of glial cells, which may in turn alter the activity of Mn(II)-sensitive enzymes in this cell compartment.     

Transition metal-saccharide chemistry: d-glucose complexes of Mn(II), Co(II), Ni(II), Cu(II) and Zn(II)

Metal complexes of d-glucose (d-Glc) from large cation containing dibromo-dichloro salts of dipositive metals [NEt₄]₂[MBr₂Cl₂] (M = Mn, Co, Ni, Cu and Zn) and the disodium salt of glucose were synthesized from a MeOH:MeCN mixture. The complexes were characterized by UV-vis absorption, circular dichroism, IR and proton magnetic resonance spectroscopies, and by elemental analysis, and were found to be Na[M(d-Glc)(OMe)Cl]. Cyclic voltammetric studies of these complexes, in the acidic to neutral pH range, indicated no dissociation, even in highly acidic conditions.This paper is dedicated to Professor Richard H. Holm (Harvard University) on the occasion of his 60th birthday.     

真菌吸附铅锌的研究

正随着采矿业的迅速发展,越来越多的重金属通过多种途径进入土壤环境中,对生态环境造成了不可估量的破坏并严重威胁人类健康。铅锌在工业上具有非常重要的作用且其应用极为广泛,而他们具有的难去除、难迁移和生物累积等特性使得铅锌在环境中的污染尤为突出。通过微生物的生长代谢,有效降低土壤重金属毒性,是促进植物生长的重要步骤之一。同时也要求微生物自身具有抵抗重金属的功能,根际微生     

Antitumor activity of phenylene bridged binuclear bis(imino-quinolyl)palladium(II) and platinum(II) complexes

Antitumor effects of a known bis(imino-quinolyl)palladium(II) complex 1 and its newly synthesized platinum(II) analogue 2 were evaluated against human breast (MCF-7) and human colon (HT-29) cancer cell lines. The complexes gave cytotoxicity profiles that were better than the reference drug cisplatin. The highest cytotoxic activities were pronounced in complex 2 across the two examined cancer cell lines. Both compounds represent potential active drugs based on bimetallic complexes.     

Preparation, structural, magnetic and thermal properties of two heterobimetallic cyano-bridged nickel(II)-copper(II)/platinum(II) coordination polymers

Two unique bimetalic Pt(II) coordination polymers of composition [Ni(hydeten)₂Pt(CN)₄] (Ni-Pt) and [Cu(hydeten)₂Pt(CN)₄] (Cu-Pt) [hydeten = N-(2-hydroxyethyl-ethylenediamine) or 2-(2-aminoethylamino)ethanol] have been synthesized and structurally characterized by various methods in this study. The crystal structure of Cu-Pt was determined by single-crystal X-ray diffraction analysis. The structure of Cu-Pt forms of infinite 2,2-TT type [-Cu(hydeten)₂-NC-Pt(CN)₂-CN-] chains containing paramagnetic copper atoms bridged by tetracyanoplatinate species. In this complex, Cu(II) centers display an axially elongated octahedron with two chelating hydeten molecules in the equatorial positions and N-bonded bridging cyano groups in the axial positions, whereas Pt(II) centers are four coordinate with four cyanide-carbon atoms in a square-planar arrangement. The decrease of the moments of these complexes in temperature range of 50 305 K can assigned to the antiferromagnetic interactions in the structures. The thermal decomposition of Cu-Pt comprise of five distinguished stages, while the thermal decomposition of Ni-Pt take place four different stages.     

Determination of Mn(II) and Co(II) with Arsenazo III

Complex formation between Arsenazo III and Mn²⁺ and Co²⁺ at equilibrium has been investigated at pH 7.2, and the stoichiometry and stability of the complexes have been determined. The data indicate that Arsenazo III is suitable for determination of Mn²⁺ and Co²⁺ on the micromolar scale. The dissociation constants of the phosphate complexes of Mn²⁺ and Co²⁺ at pH 7.2 were estimated with Arsenazo III as 3.6 and 10 mM, respectively.     

Cobalt(II) and cadmium(II) chelates with nitrogen donors and O2 bonding to Co(II) derivatives

The formation of Cd(II) and Co(II) complexes with N-methylethylenediamine (men) has been studied at 298 K in dimethylsulfoxide (dmso) in an ionic medium set to 0.1 mol dm⁻³ with Et₄NClO₄ in anaerobic conditions by means of potentiometric, UV-Vis, calorimetric and FT-IR technique. Mononuclear ML_j (M=Cd, Co; j=1-3) complexes are formed in exothermic reactions, whereas the entropy changes oppose the complexes formation. The results are discussed in terms of different basicities and steric requirements and the whole of the thermodynamic data reported till now for the two ions with a number of diamines are summarized to visualize the selectivity of the ligands. The dioxygen uptake of Co(men)₂ species has also been studied by means of UV-Vis and EPR techniques. The kinetic parameters and stability constants obtained for the formation of the superoxo and μ-peroxo species are discussed in terms of solvent effect and steric hindrance due to methyl group.Cyclic voltammetry was used to confirm the stability constant for the Co(dmen)₂ (dmen=N,N^′-dimethylethylenediamine) superoxo adduct formation but was not successful to investigate this Co(men)₂-O₂ system.     

Bioaccumulation of copper(II), lead(II) and chromium(VI) by growing Aspergillus niger

The effect of copper(II), lead(II) and chromium(VI) ions on the growth and bioaccumulation properties of Aspergillus niger was investigated as a function of initial pH and initial metal ion concentration. The optimum pH values for growth and metal ion accumulation were determined as 5.0, 4.5 and 3.5 for copper(II), lead(II) and chromium(VI) ions, respectively. Although all metal ion concentrations caused an inhibition effect on the growth of A. niger, it was capable of removing of copper(II) and lead(II) with a maximum specific uptake capacity of 15.6 and 34.4 mg g⁻¹ at 100 mg dm⁻³ initial copper(II) and lead(II) concentration, respectively. Growth of A. niger was highly effected by chromium(VI) ions and inhibited by 75 mg dm⁻³ initial chromium(VI) concentration since some inhibition occurred at lower concentrations.     

Study of the coordination behaviour of (3,5-diphenyl-1H-pyrazol-1-yl)ethanol against Pd(II), Zn(II) and Cu(II)

A new easily synthetic route with a 96% yield of ligand 2-(3,5-diphenyl-1H-pyrazol-1-yl)ethanol (L) is obtained. The reactivity of L against Pd(II), Zn(II) and Cu(II) leads to [PdCl₂(L)₂] (1), [ZnCl₂(L)] (2) and [CuCl(L′)]₂ (3) (L′ is the ligand L without alcoholic proton), respectively. According to the different geometries imposed by the metallic centre and the capability of L to present various coordination links, it has been obtained complexes with square planar (1 and 3) or tetrahedral (2) geometry and different nuclearity: monomeric (1 and 2) or dimeric (3). Complete characterisation by analytical and spectroscopic methods, resolution of L and 1-3 by single-crystal X-ray diffraction and magnetic studies for complex 3 are presented.     

Synthesis and characterization of nickel(II) and copper(II) complexes with tetradentate Schiff base ligands

The 1:1 condensation of 1,2-diaminopropane and 1-phenylbutane-1,3-dione at high dilution gives a mixture of two positional isomers of terdentate mono-condensed Schiff bases 6-amino-3-methyl-1-phenyl-4-aza-2-hepten-1-one (HAMPAH) and 6-amino-3,5-dimethyl-1-phenyl-4-aza-2-hexen-1-one (HADPAH). The mixture of the terdentate ligands has been used for further condensation with pyridine-2-carboxaldehyde or 2-acetylpyridine to obtain the unsymmetrical tetradentate Schiff base ligands. The tetradentate Schiff bases are then allowed to react with the methanol solution of copper(II) and nickel(II) perchlorate separately. The X-ray diffraction confirms the structures of two of the complexes and shows that the condensation site of the diamine with 1-phenylbutane-1,3-dione is the same.