Cadmium has been determined by β-correction spectrophotometry with cadion,p-nitrobenzenediazoaminoaz-obenzone,and a non-ionic surfactant,tuiton X-100.The real absorbance of a Cd-cadion chelate in the colored solution...Cadmium has been determined by β-correction spectrophotometry with cadion,p-nitrobenzenediazoaminoaz-obenzone,and a non-ionic surfactant,tuiton X-100.The real absorbance of a Cd-cadion chelate in the colored solution can be accurately determined and the complex-ratio of cadion with Cd(II) has been worked out to be 2.Beer's law is obeyed over the concentration range of 0-0.20mg/1 cadmium and the detec-tion limit for cadmium is only 0.003mg/1.Satisfactory experimental results are presented with respect to the determination of trace cadmium in wastewaters.展开更多
文摘Cadmium has been determined by β-correction spectrophotometry with cadion,p-nitrobenzenediazoaminoaz-obenzone,and a non-ionic surfactant,tuiton X-100.The real absorbance of a Cd-cadion chelate in the colored solution can be accurately determined and the complex-ratio of cadion with Cd(II) has been worked out to be 2.Beer's law is obeyed over the concentration range of 0-0.20mg/1 cadmium and the detec-tion limit for cadmium is only 0.003mg/1.Satisfactory experimental results are presented with respect to the determination of trace cadmium in wastewaters.
文摘选择造林树种大叶相思(Acacia auriculiformis)和樟树(Cinnamomum camphora)为对象,采用开顶生长箱(open-top chamber,OTC)构建实验林,探讨镉(Cd)胁迫及其与大气CO_(2)浓度升高、氮(N)添加的复合作用对2种树木叶片N、P养分利用策略和Cd积累特征的影响。试验设5个处理:对照(CK)、加Cd[10 kg Cd/(hm^(2)·a)](Cd)、加Cd与加CO_(2)(700μmol/mol)(CdC)、加Cd与加N[100 kg N/(hm^(2)·a)](CdN)、加Cd加CO_(2)加N(CdCN)。处理约2.5 a后,测定两树种的成熟叶和衰老叶中N、磷(P)和Cd含量。结果表明,不同处理对两树种叶片P含量及P回收率均无显著影响,但显著影响叶片N含量及N回收率;CdN处理下两树种叶片N含量升高;Cd和CdN处理下樟树叶N回收率显著降低。Cd、CdC、CdN和CdCN处理下两树种叶片Cd积累浓度及樟树成熟叶中的Cd/N和Cd/P升高。大叶相思叶片N、P回收率显著高于樟树,Cd积累浓度显著低于樟树。速生豆科固氮树种大叶相思比普通非固氮树种樟树具有更好的N、P养分利用策略和抵御叶片积累Cd的能力,表明大叶相思可以作为Cd污染林地土壤生态修复的适宜树种。
