铁屑—粉煤灰处理含铬电镀废水的探讨

根据腐蚀电池原理，用铁屑－铁煤灰处理电镀含铬废水，结果表明，Cr(Ⅵ)去除率达到98％处理后出水水质良好，水质符合排放标准要求。     

矿渣对废水中铅,铬的吸附去除试验

进行了矿渣去除废水中铬、铅离子的试验研究，探讨了接触时间、金属离子初始浓度、废水酸度等因素对吸附性能的影响。结果表明，有较宽的ｐＨ范围内矿渣对铬、铅离子有较强的吸附能力，基本符合Ｆｒｅｕｎｄｌｉｃｈ吸附等温式，铅离子的吸附容量略大于价铬离子。     

不同粒径降尘中痕量金属元素Cu、Pb、Zn、Cr的形态分析

运用Ｔｅｓｓｌｅｒ形态分类法和石墨炉原子吸收分光光度法研究了不同粒径降尘样品中痕量金属元素Ｃｕ、Ｐｂ、Ｚｎ、Ｃｒ的存在形态，讨论了不同存在形态的分布规律。结果表明，Ｃｕ、Ｐｂ、Ｚｎ、Ｃｒ在降尘中的主要形态按顺序分别为有机结合态、铁锰氧化物结合态、铁锰氧化物结合态、残渣晶格态，其活性顺序为Ｚｎ＞Ｐｂ＞Ｃｕ＞Ｃｒ；４种元素的可交换态、碳酸盐结合态、铁锰氧化物结合态在小颗粒中的分布均比在大颗粒中占优势，说明小颗粒中金属元素较为活泼，其环境危害性更大。     

Comparison of three sequential extraction procedures for trace element partitioning in three contaminated Mediterranean soils

The sequential extraction procedures described by Tessier et al., McGrath and Cegarra, and Gimeno-García et al. were compared to investigate trace element (As, Cr, Cu, Pb, and Zn) partitioning patterns and extraction efficiency in three contaminated soils from Mediterranean regions of Spain. Soils were selected from Onda (Castellón) (S1), Aznalcóllar (Sevilla) (S2), and Silla (Valencia) (S3). S1 was a soil contaminated with Pb and Zn after dumping of wastes from the manufacture of ceramic tiles, S2 was polluted accidentally with a highly acid and As-concentrated sludge from mining activities, and S3 was a soil with a high Cr content from tannery sludge disposal. Trace element distribution in the soils—soluble, exchangeable, organically bound, precipitated with carbonates, bound to iron and manganese oxides, and precipitated with sulfides fractions—varied significantly according to the extraction procedure used. In addition, different extraction efficiencies were found for the three sequential extraction procedures compared. Finally, the trace elements studied showed different and specific distribution patterns between the various soil fractions examined.     

细菌X07吸附Cr(Ⅵ)的研究

从不同来源的样品中分离出一株吸附Cr(Ⅵ)较强的菌株X07,经鉴定为蜡状芽孢杆菌(Bacillus.cereus)。通过吸附实验探讨了X07死菌体对Cr(Ⅵ)的吸附特性,结果表明,X07死菌体吸附Cr(Ⅵ)的最适pH值为6.0;其吸附Cr(Ⅵ)是一个快速、非温度依赖过程,吸附50min达到饱和,在最初的5min内,吸附量达到最大吸附量的76.8%;菌体浓度的增加有利于对Cr(Ⅵ)的吸附:其吸附等温线符合Langmuir和Freundlich吸附模型,在试验的条件下,对Cr(Ⅵ)的饱和吸附容量为146.9mg/g干菌体。     

反应柱充填活性炭法处理轧钢含铬废水的研究

针对轧钢含铬废水,分别采用活性炭和离子交换树脂吸附处理的方法对其中的Cr^6＋和Cr^3＋的去除效果进行了系统的研究。静态试验考查了pH、吸附剂用量和搅拌速度等因素的影响,同时使用微型反应柱集成装置对穿透时间、吸附容量及活性炭再生方法进行了探讨,动态试验表明反应柱充填活性炭法能有效地处理含铬废水。     

Enzymatic and cellular level effects of chromium∗

Exposure of Cr to four hepatic enzymes activities of tilapia, viz. acid‐ and alkaline phosphatases, catalase and glucose‐6‐phosphatase, was contrary to the results obtained for Cd and Ni. This is the only heavy metal investigated thus far that dramatically augmented glucose‐6‐phosphatase by approximately 83% at a concentration of 12 mg L^‐1 in vivo in lieu of the fact of an initial inhibition of approximately 45 % at a lower concentration of Cr; 6 mg L^‐1. In the case of acid phosphatase and catalase activities progressive increment was observed up to 50 and 217% respectively at a concentration of 12 mg L^‐1 Cr. On the other hand, in contrast to all the investigated enzymes interestingly alkaline phosphatase was inhibited continuously at all concentrations up to 46% at 12 mgL^‐1 Cr. In vitro experiments were contrary to the above mentioned results, whereby all hepatic enzymes were inhibited with major inhibition observed for acid phosphatase of approximately 60% from 5 mgL^‐1 Cr onwards in the system.

At cellular level, Cr exposure at a lethal dose of 12 mgL^‐1 demonstrated similar effects to that of Cd. In general, the glycogen and fat reserves were depleted while lysosomal activity is increased. As compared to the effects of Cd, the mitochondria did not indicate any prominent reflection in the formation of intramitochondrial bodies. Further, similar to Cd, the cell membrane as well as nucleus were not affected.     

Fluorescence studies of dye displacement from DNA by chromium(III) complexes: Evidence for cation induced DNA condensations

The interactions of 10 different chromium(III) complexes with isolated calf thymus DNA have been analysed by studying the electronic and fluoresence spectra of intercalated ethidiumbromide. Triply charged cationic complexes including: [Cr(urea)₆]Cl₃.3H₂O, [Cr(1,10‐phenanthroline)₃](ClO₄)₃.2H₂O, [Cr(2,2'‐bipyridyl)₃] (ClO₄)₃.2H₂O, [Cr(ethylendiamine)₃]Cl₃.3.5H₂O and [Cr(NH₃)₆](NO₃)₃ displaced the dye from DNA. Similar effects were observed in experiments using the non‐intercalating dye bisbenzimidazole ("Hoechst 33258"). However, singly charged cationic, anionic and uncharged chromium(III) complexes such as: cis‐[Cr(1,10‐phenanthroline)₂Cl₂]Cl.2H₂O, cis‐[Cr(2,2'‐bipyridyl)₂Cl₂]Cl.2H₂O, [Cr(glutathione)₂]Na₂, [Cr(cysteine)₂]Na.2H₂O and [Cr(glycine)₃] were unable to displace both ethidiumbromide and bisbenzimidazole from DNA. There was no evidence for the formation of co‐ordinate bonds between chromium(III) and DNA for any of the above complexes. The charge and type of ligand are important in controlling the interaction of chromium(III) with isolated DNA in vitro. Our findings indicate that the outer sphere interaction of a chromium(III) complex with DNA is weak and unlikely to be the mechanism by which chromate causes DNA impairments in vivo and in vitro.     

Biochemical responses of Cr-tolerant and Cr-sensitive mung bean cultivars grown on varying levels of chromium

Biochemical investigations were carried out in Cr-tolerant and Cr-sensitive cultivars of mung bean (Vigna radiata L.) with different concentrations of hexavalent chromium (as K₂Cr₂O₇) in hydroponics culture. Seeds were germinated and grown in the presence or absence of chromium under controlled environmental conditions. Protein, pigment and enzyme analysis were conducted in both Cr-tolerant and Cr-sensitive cultivars of mung bean after 72 h of treatments. Chlorophyll and protein contents were reduced in Cr-sensitive cultivars more than those of the tolerant ones. The enzyme activity varied among the Cr-tolerant and Cr-sensitive ones. Activities of catalase, peroxidase, glucose-6-phosphate dehydrogenase and superoxide dismutase were greater in Cr-sensitive than tolerant cultivars.     

石墨炉原子吸收分光光度法测定土壤中总铬

建立了土壤中总铬测定的石墨炉原子吸收分光光度法;以塞曼效应扣除背景,优化了石墨炉灰化、原子化温度、停留时间及基体改进剂用量。结果表明:当原子化温度为2 700℃,灰化温度为700℃,原子化时间2 s,灰化时间为9 s;基体改进剂用量为3~5μL时,仪器可以达到最佳工作状态。该方法铬元素浓度在0~32μg/L内呈良好的线性关系,相关系数r=0.999 9,检出限为0.3 mg/kg;对土壤标样GSS-1和ESS-1的铬测定精密度均小于5%,相对误差在-4.8%~-0.7%之间,方法的灵敏度和准确度均符合要求。因此,石墨炉原子吸收分光光度法测定土壤中总铬具有原子化温度高、干扰少、灵敏度高等特点可适用土壤中总铬的测定。