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快速催化极谱法测定土壤中的有效态钼

The Determination of Available Molybdenum in Soil by Rapid Catalytic Polarography

  • 摘要: 土壤中的有效态钼是生态地球化学评价的重要内容之一。经典的测定方法是以草酸-草酸铵溶液(Tamm溶液)为浸提剂的催化极谱法,在测定过程中存在铁、锰等离子及草酸盐、有机质的干扰,而消除这些干扰的程序繁琐、耗时较长。本文通过实验初步探讨了干扰机理,认为草酸根和有机质都具有还原性,在浸取过程中铁、锰等多变价的金属离子转变成还原态离子,这几种物质都与测定体系中的氯酸钠发生氧化还原反应,从而影响催化波的灵敏度。本文提出在草酸-草酸铵浸提液中加入固体氢氧化钠沉淀分离铁、锰等杂质,以硝酸-硫酸破坏浸提液中草酸盐及有机质,利用钼-苯羟乙酸-氯酸盐-硫酸体系极谱催化波实现了土壤标准物质中有效态钼的测定。相比于传统消除干扰的方法,本方法所用试剂种类少,操作时间短,有效地减少了分析过程中的误差来源,方法检出限为0.0015 μg/g,低于传统方法的检出限(0.0068 μg/g),精密度(RSD,n=12)<7%,相对误差小于8%,国家标准物质的测定值和标准值更加吻合。经上千件土壤样品的验证,此法适用于pH 3.6~10.5土壤中有效态钼的测定,可测定范围为0.005~2 mg/kg,具有快速简便、测定结果准确和稳定等特点,适合推广应用于大批量土壤有效态钼的快速分析。

     

    Abstract: Available molybdenum in soil is an important proxy of ecological geochemistry evaluation. The classic method to determine available molybdenum in soil is catalytic polarography, which uses oxalic acid-ammonium oxalate (Tamm solution) as an extracting agent. The procedure to eliminate the iron ion, manganese ion, and oxalate and organics interferences is complicated and time consuming. Consequently, the interference mechanism is discussed in this paper. Since oxalate and organics are reductive, the metallic ions with variable valences changed to a reduction state during leaching. The oxidation-reduction reaction proceeds between the before mentioned materials and sodium chlorate in the measurement system, affecting the sensitivity of the catalytic wave. The method presented in this article is to add solid natrium hydroxide into oxalic acid-ammonium oxalate solution so that iron and manganese impurities can be removed through precipitation separation. Afterwards, HNO3-H2SO4 was used to destroy the organics and oxalate in the leaching liquor. In the system of molybdenum-benzoglycolic acid-chlorate-sulfuric acid, available Mo in soil standard reference materials was determined by polarographic catalytic wave. Compared with the classic interference elimination method, this method effectively reduces reagent types, operating time and error sources in analysis. The detection limit of this method is 0.0015 μg/g, which is below the detection limit of the classic method (0.0068 μg/g). The precision (RSD, n=12) is less than 7% and relative error is less than 8%. Measured values of soil standard reference materials are in agreement with the certified values. Verified by thousands of soil samples, this method is suitable to measure available Mo in soil that pH range is from 3.6 to 10.5. The measuring range of available Mo is 0.005-2 mg/kg. The method has the advantage of simple operation, short process, is accurate and has stable analysis results. It could be widely used in large quantities for rapid analysis of available Mo in soil.

     

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