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INFLUENCE OF THE VARIOUS ORGANIC OR INORGANIC ELEMENTS ON THE H_2O_2 DECOMPOSITION IN DARK FENTON REACTION

机译:各种有机或无机元素对黑色芬顿反应中H_2O_2分解的影响

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Dark Fenton process which is frequently employed in treating non-biodegradable organics in wastewater uses ferrous or ferric ion to produce OH radical from hydrogen peroxide. Since the decomposition rate of hydrogen peroxide determines the formation rate of OH radical which is a key compound in Advance Oxidation Process, it is important to improve the current understanding of the Fenton chemistry affecting the decomposition rate of hydrogen peroxide under the presence of various inorganic/organic elements in aqueous conditions. Many researches which investigated the influence of inorganic/organic elements on Fenton chemistry were more focused on the behavior of target compounds not hydrogen peroxide (Ming-Chun Lu et.al., 1997; Kiwi et.al, 2000; and Pignatello, 1992). The effects of organic or inorganic compounds on hydrogen peroxide decomposition were not well defined. This study was attempted to investigate the effects of various organic or inorganic compounds on the decomposition rate of hydrogen peroxide in dark Fenton reaction. Most of the experiments were conducted in excess presence of hydrogen peroxide over ferric ion (≈100) in the following conditions: [H_2O_2]_0 ≈ 100 mM, [Fe~(3+)]_0 = 1mM, pH_0 = 2.8, temp.= 20 ~ 22°C. Inorganic/organic elements of interest in this study are classified into several groups; (1) perchlorate (C1O_4~-), nitrate (NO_3~-), sulfate (SO_4~(2-)), and chloride (C1~-) as the anions of iron salt, (2) EDTA (ethylene diamine tetra acetic acid), oxalate and phosphate (also often used as a buffer) as a well known complex forming agent, (3) tertiary butanol as a well known OH radical scavenger, (4) phenol and p-chloro phenol as a model compound of synthetic organic chemicals, (5) methanol and acetic acid which are frequently encountered in biologically treated wastewater. The results of inorganic/organic elements affecting hydrogen peroxide decomposition rate were expressed as the observed rate constants of pseudo-first order decay kinetics of hydrogen peroxide as a function of the concentration of inorganic/organic elements (Figure 1). The assumption of pseudo-first order decay kinetics of hydrogen peroxide under the given experimental conditions was reasonable (R~2 > 0.99).
机译:其在废水中治疗非生物可降解的有机物经常采用暗芬顿处理使用亚铁或铁离子,以产生从过氧化氢OH基。由于过氧化氢的分解速率决定OH自由基的形成速度是预先氧化过程的关键化合物,它以改进芬顿化学的当前理解影响过氧化氢的在各种无机/存在下的分解速率是重要在水性条件下的有机元素。其中许多研究了芬顿化学无机/有机元素的影响进行了研究更侧重于目标化合物不过氧化氢的行为(明春路等人,1997;猕猴桃et.al,2000;和Pignatello,1992) 。过氧化氢分解的有机或无机化合物的作用没有得到很好的限定。本研究试图探讨过氧化氢的在暗Fenton反应的分解速率的各种有机或无机化合物的作用。大多数实验是在氢气的过量存在下进行的过氧化物在三价铁离子(≈100)在下列条件下:[H_2O_2] _0≈100毫米,的[Fe〜(3 +)] _ 0 = 1mm时,PH_0 = 2.8,温度。 = 20〜22℃。在这项研究中所关注的无机/有机元素被分类成若干组; (1)高氯酸盐(C1O_4〜 - ),硝酸根(NO_3〜 - ),硫酸根(SO_4〜(2-)),和氯化(C1〜 - )作为铁的盐的阴离子;(2)EDTA(乙二胺四乙酸酸),草酸盐和磷酸盐(也经常被用来作为缓冲液)作为公知的配合物形成剂,(3)叔丁醇作为公知的OH自由基清除剂,(4)苯酚和对 - 氯苯酚合成的模型化合物有机化学品,(5)甲醇和乙酸被生物处理过的污水中经常遇到的。影响过氧化氢分解率的无机/有机元件的结果表示为过氧化氢的伪一级衰变动力学作为无机/有机元件(图1)的浓度的函数所观察到的速率常数。过氧化氢的伪一级衰变动力学的给定的实验条件下的假设是合理的(R〜2> 0.99)。

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