盐酸掺杂聚苯胺粉体表面包覆合金镀层电磁参数研究

盐酸掺杂聚苯胺粉体作为电损耗吸波材料,存在磁损耗差的特点,吸波频带较窄。采用了化学镀的方法在盐酸掺杂聚苯胺粉体表面包覆磁性合金镀层,研究镀后粉体电磁参数的变化。实验结果表明,镀后粉体与原始粉体相比,磁性能有明显改善,但可能镀覆处理过程中粉体掺杂结构遭到破坏,镀后粉体电性能明显减弱。     

采用火焰原子吸收分光光度法测定水样中镍含量的不确定度评定

采用火焰原子吸收分光光度法对水样中镍的含量进行测定,分析测量过程中不确定度来源及各不确定度分量对总不确定度的影响,确定测定结果的置信区间。给出本实验室测定水样中镍含量的扩展不确定度为0．062mg／L（k=2）。     

N,N-双(二硫代羧基)乙二胺对微量络合镍的深度脱除特性研究

以柠檬酸镍(CA-Ni)、酒石酸镍(TA-Ni)、焦磷酸镍(SP-Ni)3种低浓度模拟络合镍废水为研究对象,选用自制的重金属捕集剂N,N-双(二硫代羧基)乙二胺(EDTC),对废水中的Ni进行深度脱除.重点研究了EDTC投加量、初始p H、反应时间对Ni去除效果的影响及螯合沉淀物的沉淀性能和溶出特性,同时分析了EDTC去除络合Ni的机理.研究结果表明,处理初始浓度5 mg·L~(-1)的CA-Ni、TA-Ni、SP-Ni,p H为4~8,EDTC最佳投加量分别为60 mg·L~(-1)、55 mg·L~(-1)和70 mg·L~(-1),PAM(聚丙烯酰胺)为1 mg·L~(-1),反应时间2 min,Ni的出水浓度均低于0.05mg·L~(-1),去除率达99%以上.螯合沉淀物沉降性能好且在弱酸弱碱条件下能稳定存在.红外光谱图和元素分析结果表明:EDTC与Ni发生螯合反应,即EDTC直接脱除络合镍中的Ni2+,并与Ni2+生成更稳定的螯合产物EDTC-Ni,进而有效地去除废水中Ni.     

厌氧消化过程中镍及其螯合物的生物可利用性研究

通过厌氧消化静态实验,研究了不同螯合剂存在条件下,产甲烷富集培养物对微量元素镍及其螯合物的生物吸收.结果表明,螯合剂的种类对厌氧消化有着一定影响.在乙酸钠浓度为85 mmol/L,硫化物浓度为1 mmol/L,消化温度为35℃,镍离子浓度为200 μmol/L时,氨三乙酸(NTA)的添加体系中甲烷产量最高,分别比柠檬酸...     

镍对厌氧消化过程的抑制作用研究

采用混合式厌氧反应器,以酒糟废水为基质,在相同条件的不同反应器中每日加入不同浓度的镍离子（以硝酸镍形式加入）,研究不同浓度的镍离子对厌氧体系的抑制作用,以及体系中溶解态的镍离子含量与抑制程度的关系。结果表明,日加入镍量低于３６．４ｍｇ／Ｌ时,对体系无影响;在４０－６０ｍｇ／Ｌ时,产生轻微的抑制;超过８０ｍｇ／Ｌ时,对体系造成严重的抑制。当体系中溶解态镍离子浓度低于２．５ｍｇ／Ｌ时,体系不受影响。厌     

化学镀镍废液的处理及再生技术研究进展

介绍了化学镀镍废液的产生和危害,综述了近年来国内外采用化学沉淀法、电解法、氧化还原法、萃取法、离子交换法、电渗析法等对化学镀镍废液进行处理及净化再生的技术研究进展,对各种方法的实用性进行了评价,并指出今后的发展方向。     

龙口褐煤对Ni^2＋,Mn^2＋,Hg^2＋等重金属离子的吸附特性

本文以龙口褐煤作吸附剂,对重金属离子Ｎｉ＾２,Ｍｎ＾２＋,Ｈｇ＾２＋的单组分水溶液进行吸附研究,探讨了吸附剂的吸附性能,影响吸附的因素和吸附机理。结果表明：褐煤对Ｎｉ＾２＋,Ｍｎ＾２＋,Ｈｇ＾２＋的吸附均表现出Ｌａｎｇｍｕｉｒ特征,ＰＨ值是影响吸附的一个重要因素。     

水样中镉镍的两次双波长分光光度法测定

研究采用两次双波长分光光度法 ,一次采用双峰双波长法 ,一次采用系数补偿法同时测定水样中的镉和镍。实验结果表明 ,以 5 Br PADAP为显色剂 ,镉和镍的最大吸收峰分别为 544 .8nm和 559.2nm ,最小吸收峰均为 430nm ;镉镍的线性范围为 1～ 1 6μg/ 2 5mL。此法的灵敏度同单波长法相比有明显的提高 ,应用于合成和电镀水样中的镉镍的测定 ,均得到了满意的结果。     

Rapid treatment of atrazine-contaminated water by nickel/iron bimetallic system

The utility of nickel/iron in the remediation of atraz.ine-contaminated water was investigated. The experimental results showed that nickel/iron had effective catalytic activity in dechlorinating atraz.ine under acidic conditions. The dechlonnation reaction approximately followed the first-order kinetics under the experimental conditions( nickel/iron: 1.0 g/250 ml: Ca~r~ = 20.0 mg/L), the reaction rate increased with decreasing pH value of the reaction solution and increasing the proportion of Ni: Fe within 2.95 %. For condition with 2.95% nickel/iron, the reaction rate constants were 0.07518( R = 0.9927), 0.06212( R = 0.9846) and 0.00131 min^-1 ( R = 0.9.565) at pH = 2.0, 3.0 and 4.0, respectively. HPLC analysis was used to monitor the decline of atraz.ine concentration.     

Dissolution behavior of metals from particulate matter emissions

Exposure to air particulate matter (PM) is linked to numerous health effects. In order to improve the understanding of the role of its metallic components, their solubility was examined by using serial short-contact dissolutions totalling 1?h and additional sequential contact periods of 1, 4, and 8 days. The dissolution experiments were performed in solutions containing the main biological electrolytes. ICPMS determinations were used to quantify the dissolved metals. The total compositions were determined after closed vessel microwave digestion. Large variations in the rate and completeness of the dissolutions were observed. Fast and extensive dissolutions within the short-contact time (e.g., Zn, Cd) as well as slow dissolutions persisting during the last contact period (e.g., Ni, Cu, Sb, Pb) were found for smelting emissions. The multi-element determinations also made it possible to identify relationships between dissolution of different metals and define gradual composition changes of residual PM. When comparing with dissolutions performed in de-ionized water, similar major fractions were observed at short-contact time for minor components of smelting or combustion emissions (e.g., V, Ni, Cd), suggesting a preponderance of easily available forms at the surface of the relatively inert particle cores. The use of these time sequential methods may help in (1) modeling metal partitioning in biological media and (2) investigating the causes of adverse effects attributed to air PM.