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Catalytic ozonation of oxalate with a cerium supported palladium oxide: An efficient degradation not relying on hydroxyl radical oxidation

机译:铈负载氧化钯催化草酸盐的臭氧氧化反应:不依赖羟基自由基氧化的有效降解

摘要

The cerium supported palladium oxide (PdO/CeO 2) at a low palladium loading was found very effective in catalytic ozonation of oxalate, a probe compound that is difficult to be efficiently degraded in water with hydroxyl radical oxidation and one of the major byproducts in ozonation of organic matter. The oxalate was degraded into CO 2 during the catalytic ozonation. The molar ratio of oxalate degraded to ozone consumption increased with increasing catalyst dose and decreasing ozone dosage and pH under the conditions of this study. The maximum molar ratio reached around 1, meaning that the catalyst was highly active and selective for oxalate degradation in water. The catalytic ozonation, which showed relatively stable activity, does not promote hydroxyl radical generation from ozone. Analysis with ATR-FTIR and in situ Raman spectroscopy revealed that 1) oxalate was adsorbed on CeO 2 of the catalyst forming surface complexes, and 2) O 3 was adsorbed on PdO of the catalyst and further decomposed to surface atomic oxygen (*O), surface peroxide (*O 2), and O 2 gas in sequence. The results indicate that the high activity of the catalyst is related to the synergetic function of PdO and CeO 2 in that the surface atomic oxygen readily reacts with the surface cerium-oxalate complex. This kind of catalytic ozonation would be potentially effective for the degradation of polar refractory organic pollutants and hydrophilic natural organic matter. © 2011 American Chemical Society.
机译:发现低钯负载量的铈负载氧化钯(PdO / CeO 2)在草酸盐的催化臭氧氧化中非常有效,草酸盐是一种很难在水中被羟基自由基氧化而降解的探针化合物,并且是臭氧氧化的主要副产物之一有机物质。草酸盐在催化臭氧化过程中被降解为CO 2。在本研究条件下,草酸盐降解为臭氧消耗的摩尔比随催化剂剂量的增加以及臭氧剂量和pH的降低而增加。最大摩尔比达到约1,这意味着该催化剂是高活性的,并且对水中的草酸盐降解具有选择性。表现出相对稳定活性的催化臭氧化反应不会促进臭氧产生羟基自由基。用ATR-FTIR和原位拉曼光谱分析表明,1)草酸盐被吸附在形成表面配合物的催化剂的CeO 2上,2)O 3被吸附在催化剂的PdO上并进一步分解为表面原子氧(* O) ,表面过氧化物(* O 2)和O 2气体顺序排列。结果表明,催化剂的高活性与PdO和CeO 2的协同功能有关,因为表面原子氧容易与表面草酸铈络合物反应。这种催化臭氧化技术可能对降解极性难熔有机污染物和亲水性天然有机物有效。 ©2011美国化学学会。

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