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首页> 外文期刊>Atmospheric Measurement Techniques Discussions >Investigation of potential interferences in the detection of atmospheric ROsubix/i/sub radicals by laser-induced fluorescence under dark conditions
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Investigation of potential interferences in the detection of atmospheric ROsubix/i/sub radicals by laser-induced fluorescence under dark conditions

机译:在黑暗条件下用激光诱导荧光检测大气中RO x 自由基的潜在干扰的研究

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Direct detection of highly reactive, atmospheric hydroxyl radicals (OH) is widely accomplished by laser-induced fluorescence (LIF) instruments. The technique is also suitable for the indirect measurement of HOsub2/sub and ROsub2/sub peroxy radicals by chemical conversion to OH. It requires sampling of ambient air into a low-pressure cell, where OH fluorescence is detected after excitation by 308a?ˉnm laser radiation. Although the residence time of air inside the fluorescence cell is typically only on the order of milliseconds, there is potential that additional OH is internally produced, which would artificially increase the measured OH concentration. Here, we present experimental studies investigating potential interferences in the detection of OH and peroxy radicals for the LIF instruments of Forschungszentrum J??lich for nighttime conditions. For laboratory experiments, the inlet of the instrument was over flowed by excess synthetic air containing one or more reactants. In order to distinguish between OH produced by reactions upstream of the inlet and artificial signals produced inside the instrument, a chemical titration for OH was applied. Additional experiments were performed in the simulation chamber SAPHIR where simultaneous measurements by an open-path differential optical absorption spectrometer (DOAS) served as reference for OH to quantify potential artifacts in the LIF instrument. Experiments included the investigation of potential interferences related to the nitrate radical (NOsub3/sub, Nsub2/subOsub5/sub), related to the ozonolysis of alkenes (ethene, propene, 1-butene, 2,3-dimethyl-2-butene, i?±/i-pinene, limonene, isoprene), and the laser photolysis of acetone. Experiments studying the laser photolysis of acetone yield OH signals in the fluorescence cell, which are equivalent to 0.05a????a??10sup6/supa?ˉcmsupa??3/sup OH for a mixing ratio of 5a?ˉppbv acetone. Under most atmospheric conditions, this interference is negligible. No significant interferences were found for atmospheric concentrations of reactants during ozonolysis experiments. Only for propene, i?±/i-pinene, limonene, and isoprene at reactant concentrations, which are orders of magnitude higher than in the atmosphere, could artificial OH be detected. The value of the interference depends on the turnover rate of the ozonolysis reaction. For example, an apparent OH concentration of approximately 1a????a??10sup6/supa?ˉcmsupa??3/sup is observed when 5.8a?ˉppbv limonene reacts with 600a?ˉppbv ozone. Experiments with the nitrate radical NOsub3/sub reveal a small interference signal in the OH, HOsub2/sub, and ROsub2/sub detection. Dependencies on experimental parameters point to artificial OH formation by surface reactions at the chamber walls or in molecular clusters in the gas expansion. The signal scales with the presence of NOsub3/sub giving equivalent radical concentrations of 1.1a????a??10sup5/supa?ˉcmsupa??3/sup OH, 1a????a??10sup7/supa?ˉcmsupa??3/sup HOsub2/sub, and 1.7a????a??10sup7/supa?ˉcmsupa??3/sup ROsub2/sub per 10a?ˉpptv NOsub3/sub.
机译:通过激光诱导荧光(LIF)仪器可以直接检测高反应性的大气羟基自由基(OH)。该技术还适用于通过化学转化为OH间接测量HO 2 和RO 2 过氧自由基的方法。它需要将环境空气采样到一个低压电池中,在该电池中,通过308a?nm激光辐射激发后会检测到OH荧光。尽管空气在荧光池中的停留时间通常仅为几毫秒,但内部可能会产生额外的OH,这会人为地增加所测OH的浓度。在这里,我们目前进行的实验研究调查了Forschungszentrum J?lich的LIF仪器在夜间条件下检测OH和过氧自由基的潜在干扰。对于实验室实验,仪器的入口被过量的含有一种或多种反应物的合成空气流过。为了区分进样口上游反应产生的OH和仪器内部产生的人工信号,对OH进行了化学滴定。在模拟腔室SAPHIR中进行了其他实验,在该腔室中,通过开放路径差分光学吸收光谱仪(DOAS)进行的同时测量用作OH的参考,以量化LIF仪器中的潜在伪像。实验包括调查与烯烃臭氧分解有关的硝酸根自由基(NO 3 ,N 2 O 5 )的潜在干扰。乙烯,丙烯,1-丁烯,2,3-二甲基-2-丁烯,<-pine烯,柠檬烯,异戊二烯)和丙酮的激光光解。对丙酮进行激光光解的实验研究了荧光池中OH的产生,该信号相当于0.05a ???? a ?? 10 6 a?ˉcm a ?? 3 OH,混合比为5a?ˉppbv丙酮。在大多数大气条件下,这种干扰可以忽略不计。在臭氧分解实验中,未发现反应物的大气浓度有明显的干扰。只有在反应物浓度比大气中高几个数量级的丙烯,?-pine烯,li烯和异戊二烯才能检测到人工OH。干扰的值取决于臭氧分解反应的周转率。例如,当5.8a-ˉppbvli烯与之反应时,观察到的表观OH浓度约为1a-≤a-10-6-sup -a -cm-sup -a -3-sup>。 600appbv臭氧。硝酸根NO 3 的实验表明,在OH,HO 2 和RO 2 检测中存在小的干扰信号。对实验参数的依赖性表明,在腔室壁或气体膨胀中的分子簇中,通过表面反应可形成人工OH。信号在存在NO 3 的情况下进行缩放,给出的等效自由基浓度为1.1a ???? a ?? 10 5 a?ˉcm a ?? 3 < / sup> OH,1a ???? a ?? 10 7 a?cm a ?? 3 HO 2 和1.7a?每10a的a ?? 10 7 a?ˉcm a ?? 3 RO 2 ?pptv NO 3

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