内螺纹变截面铜管拉伸工艺的研究

此文提出了内螺纹变截面铜管分段拉仲一次成形新工艺,并就工艺因素对该管拉伸成形的影响进行了试验研究,从而为合理制订成形工艺提供了依据。     

火焰原子吸收分光光度法测定鱼内脏及河流底泥中的铜

采用火焰原子吸收分光光度法测定鱼内脏及河流底泥中的铜。鱼内脏经组织捣碎机捣成匀浆后，加硝酸消解；底泥则经氢氟酸和高氯酸消化。该方法具有灵敏度高，精密度和回收率较好等特点。     

地下水中铜的形成及其与人群健康的关系

利用国家科技攻的成果，并根据国内外的研究现状，论证了地下水中铜元素的形成及其与人群健康的关系。     

铜的快速电解法测定

为适应用废铜制取电解铜时快速测定铜的需要，试验用快速电解法测定电解铜中的铜的方法，采用水浴控制溶样温度，电炉加热驱氮，加大电解电流，缩短电解时间，对不同电解酸度进行了探讨，样品测定结果重现性好，准确性较好。     

交联氨基淀粉的制备及对铜离子的吸附性能

以玉米淀粉为原料，经环氧氯丙烷交联、醚化．合成醚化淀粉3-氯-2-羟基丙烯基交联淀粉。在碱性条件下．醚化淀粉进一步通过胺化反应．制备出对重金属具有较强吸附性能的氨基淀粉。对氨基淀粉的合成工艺及其对铜离子的吸附性能的实验结果表明：随着pH的增加．吸附量增加：在相同pH时，随着溶液中铜离子初始浓度的增加，吸附量增加，但吸附速率降低：铜在固液相中的分配比降低。     

水中微量铝的间接原子吸收法测定

在ＨＡｃ－ＮａＡｃ缓冲溶液（ｐＨ４．５）体系中，利用（１－（２－萘酚（ＰＡＮ），Ａｌ＾３＾＋与Ｃｕ＾２＾＋－ＥＤＴＡ发生定量交换反应，用氯仿萃取出Ｃｕ＾２＾＋－ＰＡＮ，用原子吸收法测定水中的Ｃｕ＾２＾＋，以间接测定ＡＬ＾３＾＋。方法的最佳线性范围为０．１－１．０ｍｇ／Ｌ，最低检出浓度为０．１ｍｇ／Ｌ；测定河水，饮用水，地下水中的Ａｌ＾３＾＋，其回收率在８５．０％－１０９％之间，变异系数为１．５％－     

The composition and environmental hazard of copper slags in the context of the Basel Convention

A recent comprehensive review of the characteristics and utilization of copper slags encourages (properly) several applications for this important pyrometallurgical byproduct. However, the review does not include possible environmental effects from these slags. The United Nations Basel Convention on the Transboundary Movement of Hazardous Wastes and Their Disposal characterizes copper compounds that exhibit specified hazard characteristics as hazardous wastes. In 1996, the Convention considered further characterization of these and other compounds and substances. The final characterization of copper slags is as non-hazardous, i.e., exempt from control. This decision was based in part (if not largely) on the data that are presented here. Literature reports were used to accumulate data describing the chemical composition and acid leaching of commercial copper slags from three countries. From these data, average values of chemical composition and their statistical confidence limits (95%) were calculated. The variability of the chemical analyses of three commercial slags produced over 19 or 20 months were statistically analyzed and shown to be small. The concentrations of toxic heavy metals in the slags are low and the frequency distributions of the values are narrow. Most of the data are normally distributed, validating the use of the statistics used and permitting predictions of likely values. The amounts of heavy metals extracted by an aggressive standard acid leach procedure are low and well below the United States. regulatory levels derived from drinking water standards. The results for total composition and leaching illustrate why the U.S. Environmental Protection Agency made a regulatory determination that such slags are not hazardous wastes. Later, in 1996, the Basel Convention Technical Working Group concurred and the Parties to the Convention adopted their recommendation.     

选矿废水污染的土壤铜量与生物累积的研究

通过对花石头河沿岸研究区植物的根部、茎叶进行采样分析,探讨了土壤铜含量和铜在植物体内的累积状况。结果表明,光叶蕨、三叶鬼针草、野牡丹、紫茎泽兰4种植物体内铜含量随着土壤铜含量的增加而增加,光叶蕨增量最大。植物根部铜生物累积系数(BF)与茎叶铜生物累积系数(BF)之间相关性不显著,但根部BF为1.311,茎叶BF为0.159,前者是后者的8.2倍。光叶蕨铜的累积能力最强,其次是紫茎泽兰,植物间铜生物累积系数没有显著性差异。各采样区土壤铜含量差异大,它们之间的差异达到显著性水平。无论是全株植物、根部,还是茎叶,BF值:公路边>山坡上>河边。青蒿铜的迁移系数(TF)最大,与其余植物的迁移系数存在显著性差异,而这4种植物之间铜的迁移系数没有显著性差异,不同采样区TF均值以公路边TF值最高,其次是河边,最后才是山坡上。     

电动力学修复铜污染土壤的研究

采用电动力学方法修复重金属污染土壤。研究中采用高岭土模拟铜污染土壤,电化学装置的电压强度为0.5 V/cm,通过在阴阳极室加入不同的缓冲液来确定铜的迁移效果。结果表明在阴极室加入乙酸作为缓冲液可以有效提高铜的迁移效果,在阳极加入柠檬酸能够有效的与铜形成络合物达到更好的迁移效果。     

In situ removal of copper from sediments by a galvanic cell

This study dealt with in situ removal of copper from sediments through an electrokinetic (EK) process driven by a galvanic cell. Iron (Fe) and carbon (C) were placed separately and connected with a conductive wire. Polluted sediments were put between them and water was filled above the sediments. The galvanic cell was thus formed due to the different electrode potentials of Fe and C. The cell could remove the pollutants in the sediments by electromigration and/or electroosmosis. Results showed that a weak voltage less than 1V was formed by the galvanic cell. The voltage decreased with the increase of time. A slight increase of sediment pH from the anode (Fe) to the cathode (C) was observed. The presence of supernatant water inhibited the variation of sediment pH because H(+) and OH(-) could diffuse into the water. The removal of copper was affected by the sediment pH and the distribution of electrolyte in sediment and supernatant water. Lower pH led to higher removal efficiency. More electrolyte in the sediment and/or less electrolyte in the supernatant water favored the removal of copper. The major removal mechanism was proposed on the basis of the desorption of copper from sediment to pore solution and the subsequent electromigration of copper from the anode to the cathode. The diffusion of copper from sediment to supernatant water was negligible.