939 resultados para Cd


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为探讨螯合剂对植物吸收重金属的影响,采用盆栽试验,研究了螯合剂乙二胺四乙酸(EDTA)和柠檬酸(CA)对土壤重金属Cd的的的态的及的用的的的(Beta vulgaris var.cicla L)富集Cd能力的影响。结果表明:EDTA的添加比柠檬酸更显著增加了土壤重金属镉的的的态含量,同时提高了的用的的的茎的的富集系数和转运能力;施用螯合剂促进了Cd从的用的的的茎的菜部菜茎的的菜菜,的用的的的茎的含Cd量显著增加,EDTA的作用是柠檬酸的2~3倍。

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研究黄土高原主要农田土壤重金属Cd的形态与生物有效性的关系,为评价本区土壤重金属Cd污染程度及其生物有效性提供一定的理论与数据依据。【方法】以黄土高原自北向南采集的12个0~20 cm耕层土壤为供试土样,通过室内分析和盆栽试验,研究了黄土高原石灰性土壤中不同形态Cd的分布特征及其生物有效性。【结果】黄土高原农田土壤Cd各形态总体分布特征为:有机结合态Cd、铁锰氧化物结合态Cd>碳酸盐结合态Cd>交换态Cd>残渣态Cd,自北向南各形态Cd含量均呈不同程度的增加趋势。各土壤类型间铁锰氧化物结合态Cd及碳酸盐结合态Cd平均含量均表现为:干润砂质新成土<黄土正常新成土<简育干润均腐土<土垫旱耕人为土,自北向南依次增加。碳酸盐结合态Cd和全Cd含量主要受到全氮、有效磷和砂粒含量的影响,且全氮和有效磷含量对其的影响为正效应。铁锰氧化物结合态Cd含量主要受全氮、有效磷、砂粒和粉砂粒含量的影响,且全氮、有效磷和粉砂粒含量对其的影响为正效应。土壤中各形态Cd含量与有机质、C/N、pH、CaCO3、粘粒含量的相关性均不显著,其中与C/N、pH、粘粒含量呈负相关。Cd在小麦茎叶层的含量小于根系;而作物不同部位Cd累积量表现...

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在PDA平板培养条件下,研究Cd、Pb及其复合污染对平菇菌丝体生长的影响以及平菇菌丝体对生长基质中Cd、Pb的生物富集作用.结果表明,在实验浓度范围内,菌丝生长势、菌落直径和菌丝体干重等均随着重金属浓度的增大而减弱(小)或降低.平菇菌丝体对Cd、Pb均具有生物富集作用,并且随着重金属浓度的增大菌丝体中重金属含量逐渐增大.Cd、Pb复合污染能促进平菇菌丝体对Pb的吸收,而抑制对Cd的吸收.

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采用盆栽方法,以风花菜(Rorippa islandica)为对照植物,研究Cd超积累植物球果蔊菜[Rorippa globosa(Turcz.)Thell.]脯氨酸的积累、丙二醛含量、生物量及叶绿素含量的变化,及其与Cd生物积累的关系.结果显示,Cd处理能明显促进2种植物体内脯氨酸的积累,当土壤中Cd浓度≤25μg/g时,球果蔊菜叶片脯氨酸的积累效应尤为显著;此时叶片生物量、叶绿素及丙二醛含量与对照相比均无显著差异,表明其叶片脯氨酸的积累在一定程度上可缓解Cd胁迫造成的氧化损伤.相关分析表明,球果蔊菜根系脯氨酸可指示球果蔊菜根系中Cd的积累.

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通过对大蒜的重金属添加土培试验,采用DTPA(二乙基胺五乙酸)为有效态铅、镉提取剂,对受试土壤进行浸提检测,分析Pb和Cd在大蒜不同部位的吸收、积累及其与土壤中有效态含量的相关性。根据GB 2762-2005《食品中污染物限量标准》中对食品中Pb、Cd的限量要求,初步确定了本试验条件下,土壤中重金属Pb、Cd有效态的临界值,并以此临界点评价该种土壤中Pb、Cd对大蒜的潜在污染。

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采用室内培养和室内分析相结合的方法,研究了外源Cd2+进入土壤30d后,在土壤各级微团聚体中的含量富集和形态赋存情况。研究结果表明:外源水溶性镉进入土壤30d后,100%转化成了颗粒态,其中58.5%转化为了可交换态,0.98%转化成了碳酸盐结合态,1.26%转化成了铁锰氧化物结合态,7.68%转化成了有机结合态,31.5%转化成了残渣态,这基本与其中各粒级微团聚体中的赋存形态的情况一致。在土壤中赋存的镉主要分布在各级微团聚体中,在各粒级微团聚体中的含量分布顺序为<10μm微团聚体>10~50μm微团聚体>50~250μm微团聚体;外源镉向小粒级微团聚体的富集倾向明显高于向大粒级微团聚体的富集倾向,其中在<10μm微团聚体中富集系数为1.43,在50~250μm微团聚体中的富集系数只有0.60。

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利用地统计学方法研究了沈阳市细河流域表层土壤中Hg、Cd、Pb和Zn含量的空间结构及其分布特征。结果表明,土壤中Hg、Cd、Pb和Zn的平均含量均高于其背景值;土壤Cd和Zn含量属中等程度的空间相关,Hg和Pb属于空间弱相关,其空间变异均为随机性因素和结构性因素共同作用的结果,但Cd和Zn含量主要受结构性因素影响,而Hg和Pb主要受随机性因素影响。土壤中Hg、Cd、Pb和Zn空间分布特征表明,4种重金属含量在上游较高,顺流而下含量明显下降;土壤中Hg和Pb含量最大值在四方台地区,Cd和Zn含量最大值分布在甘官和富官一带。细河流域土壤Hg、Cd、Pb和Zn含量空间分异是污水灌溉、固体废弃物堆放、农业生产及交通尾气等因素综合作用的结果。

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通过静态吸附试验,研究一种由超分子受体化合物磺化硫杂杯芳烃(TCAS)与树脂结合的产物——新型TCAS吸附树脂对重金属Cd2+的吸附去除性能,并初步探讨了吸附机理。试验研究结果表明,TCAS吸附树脂对Cd2+的饱和吸附量为14.45 mg/g。当温度为20℃,0.5 g TCAS吸附树脂对10 mL浓度为5 mg/L的Cd2+溶液吸附60 min时,Cd2+的去除率可达到99%以上。pH值是影响TCAS吸附树脂吸附效果的重要因素,在pH=5~9时,Cd2+的去除率随着pH值的升高而增大。在试验范围内,TCAS吸附树脂对Cd2+吸附符合Freundlich方程。吸附在TCAS吸附树脂上的Cd2+可洗脱回收,TCAS吸附树脂也可再生利用。TCAS吸附树脂对重金属Cd2+的吸附机理主要归因于TCAS对Cd2+的络合作用。

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Ilmenite-type (Zn1-xCdx)TiO3 (0 <= x <= 0.15 and 0.8 <= x <= 1.0) was synthesized by a modified sol-gel route including the Pechini process via two-step heat treatments. The thermal stability of (Zn1-xCdx)TiO3 depended on the amount of cadmium content. The as-synthesized (Zn1-xCdx)TiO3 (0 <= x <= 0.15 and 0.8 <= x <= 1.0) showed higher thermal stability than that of ZnTiO3. The variation of the dielectric constant of all synthesized (Zn1-xCdx)TiO3 samples for all measurement frequencies showed a similar tendency.

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In this work, a new method for the simultaneous determination of Pb(II) and Cd(II) on the multiwalled carbon nanotubes (MWNT)-Nafion-bismuth modified glassy carbon electrode (GCE) using square-wave anodic stripping voltammetry has been studied. Scanning electron microscopy was used to investigate the characteristics of the MWNT-Nafion-bismuth modified GCE.

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Here we investigated the analytical performances of the bismuth-modified zeolite doped carbon paste electrode (BiF-ZDCPE) for trace Cd and Pb analysis. The characteristics of bismuth-modified electrodes were improved greatly via addition of synthetic zeolite into carbon paste. To obtain high reproducibility and sensitivity, optimum experimental conditions for bismuth deposition Were Studied.

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This work herein reports the approach for the simultaneous determination of heavy metal ions including cadmium (Cd(II)), lead (Pb(II)), and chromium (Cr(VI)) using a bismuth film electrode (BFE) by anodic stripping voltammertry (ASV). The BFE used was plated in situ. Due to the reduction of Cr(VI) with H2O2 in the acid medium, on one hand, the Cr(III) was produced and Cr(VI) was indirectly detected by monitoring the content of Cr(III) using square-wave ASV. On the other hand, Pb(II) was also released from the complex between Pb(II) and Cr(VI). Furthermore, the coexistence of the Cd(II) was also simultaneously detected with Pb(II) and Cr(VI) in this system as a result of the formation of an alloy with Bi. The detection limits of this method were 1.39 ppb for Cd(II), 2.47 ppb for Pb(II) and 5.27 ppb for Cr(VI) with a preconcentration time of 120 s under optimal conditions (S/N = 3), respectively. Furthermore, the sensitivity of this method can be improved by controlling the deposition time or by using a cation-exchange polymer (such as Nafion) modified electrode.

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The electrochemiluminescence (ECL) in the S2O82- system occurs under conventional cyclic voltammetry, when the Pt working electrode was coated with Cd elementary substance. The ECL mechanism was proposed, due to the reaction between the strongly oxidizing intermediate SO4 center dot- and the transitory production, CdO, generated by oxidation of Cd with SO4 center dot-. Moreover the ECL behavior was studied in different pHs and concentrations of S2O82- solution. It was showed that the ECL signal was strongest at pH 8.0, and its intensity increased with S2O82-. The experimental results verified well with the proposed ECL mechanism.

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The homogeneous electrocatalytic reduction of 1,2-diiodoethane by anions of the supramolecular complex of (beta-CD)(2)/C-60 in DMF solution is reported. The results show that the trianion of (beta-CD)(2)/C-60 exhibits electrocatalytic behavior towards the reduction of 1,2-diiodoethane, whereas the diani on is unable to reduce the diiodoethane. The second-order catalytic rate constant in DMF solution was determined to be 3.1 x 10(5) M-1 s(-1) by analysis of voltammetric responses under pseudo-first-order conditions with respect to (beta-CD)(2)/C-60. The results suggest that the host beta-cyclodextrin molecules have little effect on the electrocatalytic ability of the encapsulated C-60 toward organic halides.