采取化学分析和Tessier连续提取法,对西宁市6个功能区城市土壤重金属cu、zn、Pb和cd的含量及形态进行研究。结果表明:西宁市各功能区土壤的cu、zn、Pb和cd的全量分别是全国土壤相应重金属几何平均值的1.9。5.2,1.9~6.9,0.8-4.0,7.4~11.1倍,4种重金属污染比较严重。6个功能区的重金属cu、zn、Pb和cd含量进行差异显著性分析,结果是广场区cu的含量与风景区的差异不显著(P〉0.05),但与其他4个功能区差异显著(P〈0.05);风景区与开发区差异显著(P〈0.05),但与其他4个功能区差异不显著(P〉0.05);开发区zn的含量与商业区和居民区的差异显著(JP〈0.05),而其他各功能区间差异均不显著(P〉0.05);各功能区Ph和cd的含量均无显著差异(P〉0.05)。研究土壤中重金属的化学形态有较大的差异,Cu以残渣态和有机结合态为主;Zn以残渣态和铁锰氧化物结合态为主;Pb和cd以残渣态为主。Cu活性相对较高的土壤出现在风景区、矿冶区和居民区,zn活性相对较高的土壤出现在风景区和广场区,Pb活性相对较高的土壤出现在风景区和居民区,cd活性相对较高的土壤出现在矿冶区和开发区,研究土壤中4种重金属均具有一定的生物有效性和潜在的生态危害性。
Decalcification using hydrochloric acid is an important pretreatment in the process of the analysis of soil particle-size distribution from calcareous soil samples. Decalcification procedure is characterized by complex operations, time consuming and low accuracy. To analyze differences and convert relationships for soil particle-size distribution between decalcification and non-decalcification, 368 soil samples were determined by the Mastersizer 2000 laser particle-size analyzer. Results showed that there was a difference in soil particle-size distribution between decalcifica tion and non-decalcification. For coarse sand and clay contents, the samples of the ~〈 3% difference value accounted for 97.28% and 98.91%, respectively. For fine sand and silt contents, the samples of the ~ 3% difference value accounted for 70.65% and 76.63%, respectively. The changes in soil particle-size distribution were mainly influenced by calcium carbonate contents. The correlation of soil particle-size distribution was very significant between decalcification and non-decalcification. The conversion equations of data between the two cases were established so that soil particle-size distribution by the decalcification method could be calculated using the data obtained by the non-decalcification one.