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Titanium dioxide photocatalytic oxidation of nitric oxide: Reaction parameters and kinetics.

机译:二氧化钛光催化氧化一氧化氮:反应参数和动力学。

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Nitric Oxide is the major component of nitrogen oxides (NOX), which are precursors of tropospheric ozone and particulate matter. NO X also contribute to acid rain. Environmental regulations thus make NOX emission control a top priority. Photocatalytic oxidation (PCO) using titanium dioxide (TiO2) has gained much attention in air and water pollution control due to its ability to oxidize low concentration pollutants and ease of operation compared to other competing technologies (e.g., catalytic oxidation, incineration, carbon adsorption). In PCO, the chemical activation is provided by UV (380 nm) to generate electron-hole (e - h+) pairs which in turn yield the highly oxidative hydroxyl radical (·OH).; In this study, nitric oxide, the major component of NOX, was photocatalytically oxidized to nitric acid and nitrogen dioxide (NO2 ). The latter can be collected as nitric acid in an adsorbent bed. The treatment is a nitrogen fixation process and converts a pollutant to a raw material of fertilizer. The thin-film photoreactor was irradiated with two 8W or 25W black lights with adjustable light intensity. NO and NO2 were measured with Thermo Environmental Model 10S chemiluminescent NO-NO X gas analyzer. The photocatalytic oxidation takes hours to reach a steady state and the time frame depends on inlet NO concentration, light intensity, and the catalyst weight. The amounts of NO2 and NO3 recovered from the catalyst were analyzed with an Alltech Universal Ion Chromatograph (IC); these amounts also change with time before a steady state is reached. A typical space time is ∼12 seconds.; The NO conversion decreases with temperature from of 74 to 195°F. The conversion increases with space time and decreases with inlet concentration. Two 25W black lights were used with a dimming electronic ballast to vary the light intensity. The light was measured with a radiometer in the range of 320–390 nm. Light intensity increases the conversion of NO and NO 2 selectivity. Humidity increases the oxidation rate, which is consistent with the ·OH oxidation mechanism. The kinetic data at the steady state fit a Langmuir-Hinshelwood equation very well, The process involves a series of oxidation steps by the ·OH radical: NO → HNO2 → NO2 → HNO3. The reaction essentially reaches equilibrium at a long space time (e.g., 12 seconds).; The photocatalytic oxidation mechanism was proposed. ·OH radical was a key oxidant in this reaction. HNO2 was an intermediate species which would further oxidized to NO2 and H2O, HNO 3, the major product deposited on the catalyst, was produced from the reaction between NO2 and ·OH radical.
机译:一氧化氮是氮氧化物(NO X )的主要成分,氮氧化物是对流层臭氧和颗粒物的前体。 NO X 也会导致酸雨。因此,环境法规使NO X 排放控制成为重中之重。与其他竞争技术相比,使用二氧化钛(TiO 2 )的光催化氧化(PCO)由于能够氧化低浓度污染物且易于操作,因此在空气和水污染控制中受到了广泛关注。催化氧化,焚烧,碳吸附)。在PCO中,紫外线(<380 nm)提供化学活化作用,以生成电子-空穴对(e --h + ),从而产生高度氧化的羟基自由基(·OH)。在这项研究中,NO X 的主要成分一氧化氮被光催化氧化为硝酸和二氧化氮(NO 2 )。后者可作为硝酸收集在吸附床中。该处理是固氮过程,可将污染物转化为肥料的原料。用两个光强度可调的8W或25W黑光照射薄膜光反应器。用Thermo Environmental Model 10S化学发光NO-NO X 气体分析仪测量NO和NO 2 。光催化氧化需要几个小时才能达到稳定状态,时间范围取决于入口NO浓度,光强度和催化剂重量。使用Alltech通用离子色谱仪分析了从催化剂中回收的NO 2 -和NO 3 -的量(我知道了);这些数量也会在达到稳定状态之前随时间而变化。典型的时空约为12秒。 NO转化率随温度从74至195°F降低。转化率随时空增加,而随入口浓度降低。两个25W黑灯与调光电子镇流器一起使用,以改变光强度。用辐射计在320–390 nm范围内测量光。光强度提高了NO和NO 2 选择性的转化率。湿度增加了氧化速率,这与·OH氧化机理一致。稳态下的动力学数据非常符合Langmuir-Hinshelwood方程,该过程涉及·OH自由基的一系列氧化步骤:NO→HNO 2 →NO 2 →HNO 3 。反应基本上在很长的间隔时间(例如12秒)达到平衡。提出了光催化氧化机理。 ·OH自由基是该反应中的关键氧化剂。 HNO 2 是一种中间物质,它会进一步氧化为NO 2 和H 2 O,HNO 3 。 NO 2 与·OH自由基的反应产生了沉积在催化剂上的主要产物。

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