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1.
自然水体中生物膜不同化学组分与铅、镉最大吸附量的关系   总被引:19,自引:0,他引:19  
生物膜存在于河流、湖泊和湿地环境中岩石和表层沉积物表面上 ,并由地球上不同种类的微生物组成 [1,2 ] .大量证据表明 ,生物膜在决定水环境中痕量金属的迁移、最终归宿、生物地球化学特性、生物可利用性和毒性过程中起着非常重要的作用 .因此 ,研究生物膜对痕量金属的吸附、预测重金属在水环境中的迁移转化规律具有重要的理论意义 .从环境化学角度看 ,生物膜上的主要成分铁氧化物、锰氧化物和有机质一直被认为是影响痕量金属在固体表面吸附的 3个最重要的因素[3] .有的文献认为 ,金属氧化物是痕量金属吸附唯一最重要的决定因素 [4 ,5] ,有…  相似文献   

2.
采集的生物膜中痕量重金属的形态分布特征   总被引:1,自引:0,他引:1  
采用改进的Tessier连续萃取方法对从松花江中采集的生物膜中锰、 铁、 铜、 铅、 锌及镉的化学形态进行分析, 考察了生物膜上铁、 锰氧化物和有机质吸附重金属的相对作用, 同时讨论了在研究培养的生物膜吸附痕量重金属时所建立的选择性萃取方法对于采集的生物膜组分分离的适用性. 研究结果表明, 在采集的生物膜上痕量重金属以铁、 锰的氧化物为主要结合形态存在, 以此种形态存在的铜、 锌、 铅和镉分别占其总含量的62.9%, 58.3%, 53.8%和32.6%, 而以有机结合态存在的铜、 锌、 铅和镉, 分别占其总含量的1.1%, 0.6%, 9.9%和1.8%, 表明采集的生物膜上铁、 锰氧化物在吸附重金属的过程中起主要的控制作用, 而有机质的作用相对较小, 与以往利用选择性萃取技术研究培养的生物膜吸附重金属的规律一致. 进一步分析表明, 如扣除生物膜上铁的残渣态部分, 则选择性萃取分离技术可以有效地将采集的生物膜上的铁、 锰氧化物及有机质分离开.  相似文献   

3.
湖水中的颗粒物对水体生物膜吸附铅、镉的影响   总被引:2,自引:0,他引:2  
采用逐级过滤的方式对湖水进行过滤,并用含有不同粒径颗粒物的湖水进行生物膜的培养,以研究水中颗粒物对生物膜吸附痕量重金属的影响.研究结果表明,生物膜上铁、锰氧化物含量与水中总铁、总锰含量呈明显的线性关系,锰氧化物的含量受水中颗粒物粒径分布的影响很大.生物膜吸附铅、镉的热力学过程符合Langmuir方程,且膜上铁、锰氧化物吸附铅、镉的能力随着湖水中颗粒物粒径的减小呈增强的趋势.  相似文献   

4.
不同水体生物膜中各化学组分对铅的吸附作用研究   总被引:9,自引:0,他引:9  
水中的底泥、悬浮物和生物膜等固相物质对重金属在水中的迁移和转化有重要影响 [1,2 ] ,而固相物质中起主要作用的是吸附能力强的铁、锰氧化物和有机质 [3,4 ] .对生物膜与重金属相互作用的研究已经有报道 [5,6] .Nelson等[3] 用吸附加和模型模拟生物膜上各组分对铅吸附 ;Dong等 [7] 用选择性萃取的方法研究生物膜各组分对铅、镉的吸附情况 ,但他们的研究均局限于单一水体 ,本文采用萃取 -吸附-统计分析的方法研究多个自然水体生物膜中铁、锰氧化物和有机质对铅吸附的相对贡献 .1 实验部分1 .1 生物膜的培养及组分测定 选吉林省境内的净…  相似文献   

5.
Selective extraction techniques followed by adsorption experiment and statistical analysis were employed to estimate and compare the relative roles of metal oxides and organic substance in adsorption of Pb, Cd, Cu and Co onto surface coatings. Results indicated that metal oxides were very important sorbents for all of metal ions involved in this study, especially for Pb and Co. Furthermore, manganese oxides contributed to the absolute majority of Co adsorption regardless of concentration. But for Cu and Cd, organic materials are also very important sorbent phases, particularly for Cu, organic materials contributed to most of the Cu adsorption regardless of concentration. In addition, the analysis suggested the extraordinary predominance of Mn oxides for metal adsorption at the low concentrations. Considering the low concentration in natural water environments, Mn oxides might exert the greatest influence on the behavior of heavy metals.  相似文献   

6.
Multistage sequential extraction with different sequences was applied to extracting natural surface coatings( NSCs), and the results were compared with those by single stage extraction technique. The optimal sequential extraction scheme with the best performance was selected and incorporated into the method of selective extraction followed by adsorption and statistic analyses to study the adsorption parameters of Fe oxides, Mn oxides and organic matters in NSCs for Pb and Cd, to validate the applicability of the sequential extraction scheme. The Langmuir adsorption parameters of each component of surface coating estimated according to the adsorption data of single stage extraction of NSCs were all similar to those of sequential extraction of NSCs, and the maximum difference between the metal adsorption abilities of the components estimated via the two extraction techniques was only about 20%, indicating that either extraction techniques could be used. The optimal sequential extraction scheme obtained was first extracted with NH2OH·HCl, then with Na2S2O4, and finally with oxalic acid.  相似文献   

7.
Natural surface coatings collected from natural substances(NSCsNS)were employed to study the roles of the main chemical components(iron oxides,manganese oxides,and other components)in controlling the adsorption of lead(Pb)and cadmium(Cd)in aquatic environments.The selective chemical extraction followed by the adsorption of Pb and Cd experiments and statistical analysis,were used to investigate the adsorption property of each component.Hydroxylamine hydrochloride was used to remove manganese oxides selectively,and sodium dithionite was used to extract iron oxides and manganese oxides.The result indicated that iron oxides and manganese oxides played an important role in the adsorption of Pb and Cd on NSCsNS,and the relative contribution was about two-thirds.The contribution of manganese oxides was the greatest,with a lesser role indicated for other components.The adsorption ability of manganese oxides for Pb and Cd was greater than that of iron oxides or other components for Pb and Cd.The Pb adsorption observed in each component was greater than Cd adsorption.  相似文献   

8.
镉在自然水体生物膜生长过程中的积累   总被引:4,自引:0,他引:4  
镉在自然水体生物膜生长过程中的积累;吸附性积累  相似文献   

9.
铁、锰氧化物在自然水体生物膜上的分布   总被引:3,自引:0,他引:3  
在自然水体中 ,生物膜是一个开放的动力学系统 ,生物膜的形成及其组分处于动态的变化中——水环境中的各种成分在生物膜上发生着合成、聚结、转化、降解等作用 ,从而成为生物膜的一部分 ,还会随着生物膜的脱落重新进入水相中 ,所有这些变化 ,与生物膜本身的性质是分不开的 [1~ 3] 。从环境化学角度看 ,自然水体中生物膜主要化学组分包括金属氧化物 (铁氧化物、锰氧化物和铝氧化物等 )、有机质及少量的矿物质 ,其中 ,铁、锰氧化物在影响痕量重金属在水环境中的迁移、最终归宿、生物地球化学特性、生物可利用性和毒性过程中起着非常重要的作…  相似文献   

10.
用选择性萃取法萃取天然基质采集的生物膜中的铁/锰氧化物, 考察生物膜上铁/锰氧化物对水体中Pb, Cu及Zn的富集作用. 结果表明, 锰氧化物对生物膜富集Pb起主要作用, 而铁氧化物和除铁/锰氧化物以外的以有机质为主的其它组分的作用很小; 膜上其它组分对Cu的富集贡献较大, 锰氧化物的贡献与铁氧化物的接近; 锰氧化物对Zn的富集贡献最大, 铁氧化物和其它组分的贡献比较接近. 锰氧化物对Pb, Cu及Zn的富集能力分别高于铁氧化物的富集能力, 铁氧化物和锰氧化物对3种金属富集能力的大小顺序分别是Zn>Cu>Pb和Zn>Pb≥Cu.  相似文献   

11.
采用化学萃取技术对表层沉积物(生物膜)的非残渣态组分(铁、锰氧化物及有机质)进行了分离, 并研究了表层沉积物(生物膜)非残渣态和残渣态组分吸附铜、锌的特性. 结果表明, 0.1 mol/L NH2OH·HCl+0.1 mol/L HNO3, (NH4)2C2O4-H2C2O4缓冲溶液和体积分数为30%的H2O2可选择性地萃取分离表层沉积物(生物膜)非残渣态的锰氧化物、铁锰氧化物和有机质, 萃取率为63.15%~97.59%, 同时对非目的组分影响较小; 表层沉积物(生物膜)及其各组分对铜的吸附能力均大于对锌的吸附能力, 且生物膜及其各组分对铜、锌的吸附能力均高于表层沉积物及其相应组分对铜、锌的吸附能力; 表层沉积物(生物膜)非残渣态组分对铜、锌的吸附能力均大于残渣态组分, 且非残渣态组分中锰氧化物的单位吸附能力最强, 其次是铁氧化物, 而有机质的单位吸附能力较弱, 比锰氧化物低2个数量级, 说明生物膜对水体中痕量重金属的迁移转化作用强于表层沉积物, 而表层沉积物(生物膜)中金属(铁、锰)氧化物对水中痕量重金属起主要控制作用.  相似文献   

12.
自然水体中大多数微生物是以附着状态而不是以游离状态存在的 [1] .微生物附着在固体表面形成生物膜 ,存在于河流、湖泊及湿地环境中的岩石、表层沉积物和悬浮颗粒物表面 ,由不同种类的微生物组成 [2 ] .从环境微生物学角度来看 ,生物膜被定义为一种活跃地生长发育着的单一或混合的微生物群体 ,其不可逆地附着到一种活跃的或非活跃的表面 [3] ,并由微生物群体组成 [4 ] .从环境化学角度来看 ,生物膜是由金属氧化物、有机质及少量矿物质组成的 .金属氧化物和有机质在影响重金属于固相吸附的相对作用已有报道 [5~ 10 ] .生物膜在自然水体中是…  相似文献   

13.
To quantify the effect of the interaction of non-residual fractions[Fe oxides(Fe), Mn oxide(Mn), organic materials(OMs)] in the surficial sediments and the natural surface coating samples on the adsorption of atrazine(AT), an AT multiple regression adsorption model(AT-MRAM) was developed. The AT-MRAM improves upon the previous AT additional adsorption model(AT-AAM) with superior goodness-of-fit test(adjusted R2=ca.1.000), F-test and t-test(P<0.01), and reveals the effect of the interaction among the compone...  相似文献   

14.
To reveal the relative contribution of the components, Fe, Mn oxides or organic materials(OMs) in the surficial sediments(SSs), and the natural surface coating samples(NSCSs) to adsorbing atrazine(AT), a selective chemical extraction technique was employed, to remove the different components, and the adsorption characteristics of AT on the SSs and the NSCSs were investigated. The observed adsorptions of AT on the original and extracted SSs and NSCSs were analyzed by nonlinear least squares fitting(NLSF) to estimate the relative contribution of the com-ponents. The results showed that the maximum adsorption of AT on the NSCSs was greater than that in the SSs, be-fore and after extraction treatments, implying that the NSCSs were more dominant than the SSs for organic pollutant adsorption. It was also found that the Fe oxides, OMs, and residues in SSs(NSCSs) facilitated the adsorption of AT, but Mn oxides directly or indirectly restrained the interaction of AT with SSs(NSCSs) particles. The contribution of the Fe oxides to AT adsorption was more than that of OMs; the greatest contribution to AT adsorption on a molar ba-sis was from the Fe oxides in the nonresidual fractions, indicating that the Fe oxides played an important role in con-trolling the environmental behavior of AT in an aquatic environment.  相似文献   

15.
A silica-based inorganic sorbent was synthesized by the thermal decomposition of ammonium heptamolybdate on silica and applied for the preconcentration and simultaneous determination of Cd, Co, Cr, Cu, Fe, Mn, Ni, and Pb in river water samples using a column system with flame atomic absorption spectrometry. Attenuated total reflection-Fourier transformation infrared spectroscopy, scanning electron microscopy, and electron dispersive spectroscopy were used for sorbent characterization. The effects of pH, sample volume, eluent type, eluent concentration, eluent volume, sample flow rate, and matrix ions (Al, Bi, Ca, Mg, and Zn) on the recovery of the metals in model solutions were investigated. The adsorption capacities (µmol g?1) of SiO2-MoO3 were 88.96 (Cd), 169.69 (Co), 153.85 (Cr), 188.88 (Cu), 179.05 (Fe), 163.81 (Mn), 136.31 (Ni), and 38.61 (Pb). The detection limits of the method were 9.09, 10.82, 10.77, 49.57, 31.64, 6.40, 8.86, 19.15?µg L?1 for Cd, Co, Cr, Cu, Fe, Mn, Ni, and Pb, respectively, with a preconcentration factor of 25. The developed method was used for the determination of the target metals in real samples and the recoveries for spiked samples were found to be from 91.2% to 102.9%.  相似文献   

16.
The aim of this paper is to study the adsorption of the heavy metals (Cd(II), Cu(II), Mn(II), Pb(II), and Zn(II)) from aqueous solutions by a natural Moroccan stevensite called locally rhassoul. We carried out, first, a mineralogical and physicochemical characterization of stevensite. The surface area is 134 m2/g and the cation exchange capacity (CEC) is 76.5 meq/100 g. The chemical formula of stevensite is Si3.78Al0.22Mg2.92Fe0.09Na0.08K0.08O10(OH)2.4H2O. Adsorption tests of Cd(II), Cu(II), Mn(II), Pb(II), and Zn(II) in batch reactors were carried out at ambient temperature and at constant pH. Two simplified models including pseudo-first-order and pseudo-second- order were used to test the adsorption kinetics. The equilibrium time and adsorption rate of adsorption were determined. The increasing order of the adsorption rates follows the sequence Mn(II) > Pb(II) > Zn(II) > Cu(II) > Cd(II). The Dubinin-Radushkevich (D-R), Langmuir, and Redlich-Peterson (R-P) models were adopted to describe the adsorption isotherms. The maximal adsorption capacities at pH 4.0 determined from the D-R and Langmuir models vary in the following order: Cu(II) > Mn(II) > Cd(II) > Zn(II) > Pb(II). The equilibrium data fitted well with the three-parameter Redlich-Peterson model. The values of mean energy of adsorption show mainly an ion-exchange mechanism. Also, the influence of solution pH on the adsorption onto stevensite was studied in the pH range 1.5-7.0.  相似文献   

17.
Hydrous amorphous Al (HAO), Fe (HFO), and Mn (HMO) oxides are ubiquitous in the subsurface as both discrete particles and coatings and exhibit a high affinity for heavy metal contaminants. To assess risks associated with heavy metals, such as Pb, to the surrounding environment and manage remedial activities requires accurate mechanistic models with well-defined transport parameters that represent sorption processes. Experiments were conducted to evaluate Pb sorption to microporous Al, Fe, and Mn oxides, as well as to montmorillonite and HAO-coated montmorillonite. Intraparticle diffusion, a natural attenuating process, was observed to be the rate-limiting mechanism in the sorption process, where best-fit surface diffusivities ranged from 10(-18) to 10(-15) cm(2) s(-1). Specifically, diffusivities of Pb sorption to discrete aluminum oxide, aluminum oxide-coated montmorillonite, and montmorillonite indicated substrate surface characteristics influence metal mobility where diffusivity increased as affinity decreased. Furthermore, the diffusivity for aluminum oxide-coated montmorillonite was consistent with the concentrations of the individual minerals present and their associated particle size distributions. These results suggest that diffusivities for other coated systems can be predicted, and that oxide coatings and montmorillonite are effective sinks for heavy metal ions.  相似文献   

18.
《Analytical letters》2012,45(9):1807-1820
ABSTRACT

5-amino-1,3,4-thiadiazole-2-thiol groups attached on a silica gel surface have been used for adsorption of Cd(II), Co(II), Cu(II), Fe(III), Ni(II), Pb(II) and Zn(II) from aqueous solutions. The adsorption capacities for each metal ion were (in mmol.g?1): Cd(II)= 0.35, Co(II)= 0.10, Cu(II)= 0.15, Fe(III)= 0.20, Hg(II)= 0.46, Ni(II)= 0.16, Pb(II)= 0.13 and Zn(II)= 0.15. The modified silica gel was applied in the preconcentration and quantification of trace level metal ions present in water samples (river, and bog water).  相似文献   

19.
Two approaches to immobilize complex-forming analytical reagents (PAN, PAR, Xylenol orange, Brombenzothiazo, Crystal violet, Cadion, and Sulfochlorophenolazorhodanine) for the preparation of new sorbents and indicator powders are suggested: on-line coating of reversed-phase silica gel by reagents or doping of porous sol-gel silica with reagents. The retention of Ag, Cd, Cu(II), Co(II), Fe(III), Mn(II), Ni, Pb, and Zn on the sorbents developed was investigated. Quantitative sorption and desorption conditions were optimized. Procedures for the determination of Cd, Cu(II), Fe(III), Pb, and Zn with flame atomic absorption, spectrophotometric, and diffusion scattering spectrometric detection were elaborated. Detection limits for Cd, Cu(II), Fe(III), Pb, and Zn were 3 μg/L, 6 μg/L, 5 μg/L, 40 μg/L, and 1 μg/L, respectively. The procedures were used for the analysis of various real samples, e.g., natural and waste waters, and food.  相似文献   

20.
Two approaches to immobilize complex-forming analytical reagents (PAN, PAR, Xylenol orange, Brombenzothiazo, Crystal violet, Cadion, and Sulfochlorophenolazorhodanine) for the preparation of new sorbents and indicator powders are suggested: on-line coating of reversed-phase silica gel by reagents or doping of porous sol-gel silica with reagents. The retention of Ag, Cd, Cu(II), Co(II), Fe(III), Mn(II), Ni, Pb, and Zn on the sorbents developed was investigated. Quantitative sorption and desorption conditions were optimized. Procedures for the determination of Cd, Cu(II), Fe(III), Pb, and Zn with flame atomic absorption, spectrophotometric, and diffusion scattering spectrometric detection were elaborated. Detection limits for Cd, Cu(II), Fe(III), Pb, and Zn were 3 μg/L, 6 μg/L, 5 μg/L, 40 μg/L, and 1 μg/L, respectively. The procedures were used for the analysis of various real samples, e.g., natural and waste waters, and food. Received: 17 July 1997 / Revised: 20 January 1998 / Accepted: 5 February 1998  相似文献   

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