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ELECTRON BEAM DEGRADATION OF CHLORINATED HYDROCARBONS IN AIR

机译:空气中氯化氢的电子束降解

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Using a low-energy electron accelerator ( 180 keV, 3 kW ) synthetic air polluted with chlorinated hydrocarbons such as cis-dichloro-, trichloro- and perchloroethene was irradiated in a flow system. Already at doses of 2.5 kGy, more than 90 vol% of the initial pollutant concentration (2-50 ppm ) could be removed. As main products HCl, CO, chloromethanes, chloroacetyl chlorides and phosgene were identified. After hydrolysis of phosgene and chloroacteyl chlorides in a wet scrubbing system, the chlorine balance shows nearly complete mineralization of the pollutants to HCl, CO and CO_2. Less than 5 vol% of chloromethanes and about 0.1 vol% chloroacetic acids were detected after irradiation and hydrolysis. An attempt is made to describe the degradation mechanism as OH radical induced chain reaction.The OH radical adds to the ethene double bond. The resulting adduct releases a chlorine radical. In presence of oxygen a chain reaction is initiated by this radical, which leads to decomposition of the chloroethenes.
机译:使用低能电子加速器(180 keV,3 kW),在流动系统中辐照被氯代烃(如顺二氯,三氯和全氯乙烯)污染的合成空气。在2.5 kGy的剂量下,可以去除90%以上的初始污染物浓度(2-50 ppm)。作为主要产品,鉴定出HCl,CO,氯甲烷,氯乙酰氯和光气。在湿式洗涤系统中将光气和氯乙二酰氯水解后,氯气平衡显示污染物几乎完全矿化成HCl,CO和CO_2。辐照和水解后,检测到的氯甲烷含量少于5%(体积),氯乙酸含量约为0.1%(体积)。尝试将降解机理描述为OH自由基诱导的链反应.OH自由基加成到乙烯双键上。所得的加合物释放出氯自由基。在氧存在下,该自由基引发链反应,导致氯乙烯分解。

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