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Nighttime observation and chemistry of HOsubx/sub in the Pearl River Delta and Beijing in summer 2006

机译:2006年夏季在珠江三角洲和北京的HO x 夜间观测和化学

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Nighttime HOx chemistry was investigated in two ground-based fieldcampaigns (PRIDE-PRD2006 and CAREBEIJING2006) in summer 2006 in China bycomparison of measured and modeled concentration data of OH and HO2. Themeasurement sites were located in a rural environment in the Pearl RiverDelta (PRD) under urban influence and in a suburban area close to Beijing,respectively. In both locations, significant nighttime concentrations ofradicals were observed under conditions with high total OH reactivities ofabout 40–50 s?1 in PRD and 25 s?1 near Beijing. For OH, thenocturnal concentrations were within the range of (0.5–3) × 106 cm?3, implying a significant nighttimeoxidation rate of pollutants on the order of several ppb per hour. Themeasured nighttime concentration of HO2 was about(0.2–5) × 108 cm?3, containing a significant,model-estimated contribution from RO2 as an interference. A chemical boxmodel based on an established chemical mechanism is capable of reproducingthe measured nighttime values of the measured peroxy radicals and$k_{ext{OH}}$, but underestimates in both field campaigns the observed OHby about 1 order of magnitude. Sensitivity studies with the box modeldemonstrate that the OH discrepancy between measured and modeled nighttime OHcan be resolved, if an additional ROx production process (about1 ppb h?1) and additional recycling (RO2 → HO2 → OH) with an efficiencyequivalent to 1 ppb NO is assumed. The additional recycling mechanismwas also needed to reproduce the OH observations at the same locations duringdaytime for conditions with NO mixing ratios below 1 ppb. This couldbe an indication that the same missing process operates at day and night. Inprinciple, the required primary ROx source can be explained byozonolysis of terpenoids, which react faster with ozone than with OH in thenighttime atmosphere. However, the amount of these highly reactive biogenicvolatile organic compounds (VOCs) would require a strong local source, forwhich there is no direct evidence. A more likely explanation for anadditional ROx source is the vertical downward transport ofradical reservoir species in the stable nocturnal boundary layer. Using asimplified one-dimensional two-box model, it can be shown that ground-basedNO emissions could generate a large vertical gradient causing a downward fluxof peroxy acetic nitrate (PAN) and peroxymethacryloyl nitrate (MPAN).The downward transport and the following thermal decomposition of thesecompounds can produce up to 0.3 ppb h?1 radicals in theatmospheric layer near the ground. Although this rate is not sufficient toexplain the complete OH discrepancy, it indicates the potentially importantrole of vertical transport in the lower nighttime atmosphere.
机译:通过测量和模拟的OH和HO 2 浓度数据,在中国2006年夏季的两个地面野外活动(PRIDE-PRD2006和CAREBEIJING2006)中研究了夜间HO x 化学。测量地点分别位于受城市影响的珠江三角洲(PRD)的农村环境和靠近北京的郊区。在这两个地方,在珠三角地区大约40–50 s ?1 和北京附近25 s ?1 的总OH反应性较高的条件下,观察到夜间自由基的浓度很高。对于OH,则其夜间浓度在(0.5–3)×10 6 cm ?3 范围内,这意味着污染物的显着夜间氧化率约为数ppb / pp小时。夜间测得的HO 2 浓度约为(0.2–5)×10 8 cm ?3 ,其中包括RO 2 作为干扰。基于已建立的化学机制的化学盒模型能够再现所测得的过氧自由基和$ k _ { text {OH}} $的夜间测量值,但在两次野战中都低估了所观测到的OH大约1个数量级。使用盒子模型进行的敏感性研究表明,如果额外的RO x 生产过程(大约1 ppb h ?1 )和额外的回收利用,则可以解决夜间和模拟夜间OH之间的OH差异。假定(RO 2 →HO 2 →OH)具有等于1 ppb NO的效率。对于NO混合比低于1 ppb的条件,还需要使用额外的回收机制在白天的同一位置重现OH值。这可能表明同一缺失过程在白天和晚上都在运行。原则上,所需的主要RO x 源可以通过萜类化合物的臭氧分解来解释,萜类化合物在夜间大气中与臭氧的反应比与OH的反应更快。但是,这些高反应性的生物成因挥发性有机化合物(VOC)的量需要强大的本地来源,对此尚无直接证据。另一个RO x 源的更可能解释是在稳定的夜间边界层中自由基储层物质的垂直向下传输。使用简化的一维两箱模型,可以证明地面NO排放会产生较大的垂直梯度,从而导致过氧乙酸硝酸盐(PAN)和过氧甲基丙烯酰硝酸盐(MPAN)的向下通量。这些化合物可以在接近地面的大气层中产生高达0.3 ppb h ?1 的自由基。尽管此速率不足以解释OH的完全差异,但它表明在较低的夜间大气中垂直传输的潜在重要作用。

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