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首页> 外文期刊>Journal of nuclear science and technology >Dissolution of Oxalate Precipitate and Destruction of Oxalate Ion by Hydrogen Peroxide in Nitric Acid Solution
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Dissolution of Oxalate Precipitate and Destruction of Oxalate Ion by Hydrogen Peroxide in Nitric Acid Solution

机译:硝酸溶液中过氧化氢对草酸盐沉淀的溶解和对草酸盐离子的破坏

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This study aims at developing an oxalate precipitation process, which is applicable to a partitioning of long--lived radionuclides from the high-level radioactive liquid waste. In order to achieve this, a study for decomposition reaction of oxalic acid by hydrogen peroxide was first carried out. The decomposition rates of H_2O_2 and oxalic acid increased with an increase of nitric acid concentration, and especially those decomposition rates steeply increased at more than 2 M HNO_3. Based on this result, the decomposition kinetics of H_2O_2 and oxalic acid were suggested in this work. Then, the dissolution of oxalate precipitate and the destruction of oxalate ion in the solution were examined. Oxalate precipitates were prepared by adding oxalic acid into a simulated radioactive waste containing 8 metallic elements. The precipitates obtained thereby were dissolved in various nitric acid concentrations and reacted with H_2O_2 at 90deg. C. When the oxalates were completely dissolved, most of the oxalates were decomposed by adding H_2O_2, but in a slurry state the decomposition yield of the oxalate decreased with an increase of the slurry density in the solution. Such phenomenon was considered to be due to a catalytic decomposition of H_2O_2 on a solid surface of oxalate and the decomposition mechanism was explained by a charge transfer from a surface of oxalate solid to H_2O_2. producing OH radicals which can destruct H_2O_2 explosively. Accordingly, the experimental condition for the decomposition of the oxalate precipitates was found to be most favorable at 3 M HNO_3 under the initial concentrations of 0.2 M oxalate and 1 M H_2O_2. At 3 M HNO_3, oxa1ate precipitates could be safely and completely dissolved, and almost decomposed. Additionally, it was observed that the presence of ferric ion in the solution largely affects the decomposition rate of H_2O_2. This could be explained by a chain reaction of hydrogen peroxide with ferric ion in the solution.
机译:这项研究旨在开发草酸盐沉淀工艺,该工艺适用于从高放射性废液中分配长寿命放射性核素。为了实现这一点,首先进行了过氧化氢对草酸的分解反应的研究。 H_2O_2和草酸的分解速率随硝酸浓度的增加而增加,尤其是当分解速率大于2 M HNO_3时,分解速率急剧增加。根据该结果,提出了H_2O_2和草酸的分解动力学。然后,检查草酸盐沉淀的溶解和溶液中草酸盐离子的破坏。草酸沉淀是通过将草酸添加到含有8种金属元素的模拟放射性废物中而制得的。由此获得的沉淀物以各种硝酸浓度溶解,并在90℃下与H_2O_2反应。当草酸盐完全溶解时,大多数草酸盐通过加入H_2O_2分解,但在淤浆状态下,草酸盐的分解产率随溶液中淤浆密度的增加而降低。认为该现象是由于草酸盐的固体表面上的H_2O_2的催化分解而引起的,其分解机理通过从草酸盐固体的表面向H_2O_2的电荷转移来解释。产生可以爆炸性破坏H_2O_2的OH自由基。因此,在初始浓度为0.2 M草酸盐和1 M H_2O_2的情况下,发现在3 M HNO_3处草酸盐沉淀物分解的实验条件最为有利。在3 M HNO_3下,草酸盐沉淀可以安全且完全溶解,并且几乎可以分解。另外,观察到溶液中三价铁离子的存在极大地影响了H_2O_2的分解速率。这可以通过溶液中过氧化氢与铁离子的链式反应来解释。

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