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Revisiting the effectiveness of HCHO/NO_2 ratios for inferring ozone sensitivity to its precursors using high resolution airborne remote sensing observations in a high ozone episode during the KORUS-AQ campaign

机译:重新探测HCHO / NO_2比率在KORUS-AQ运动期间使用高臭氧集中的高分辨率空气遥感观测推断出对其前体的臭氧敏感性的效果

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The nonlinear chemical processes involved in ozone production (P(O-3)) have necessitated using proxy indicators to convey information about the primary dependence of P(O-3) on volatile organic compounds (VOCs) or nitrogen oxides (NOx). In particular, the ratio of remotely sensed columns of formaldehyde (HCHO) to nitrogen dioxide (NO2) has been widely used for studying O-3 sensitivity. Previous studies found that the errors in retrievals and the incoherent relationship between the column and the near-surface concentrations are a barrier in applying the ratio in a robust way. In addition to these obstacles, we provide calculational-observational evidence, using an ensemble of 0-D photochemical box models constrained by DC-8 aircraft measurements on an ozone event during the Korea-United States Air Quality (KORUS-AQ) campaign over Seoul, to demonstrate the chemical feedback of NO2 on the formation of HCHO is a controlling factor for the transition line between NOx-sensitive and NOx-saturated regimes. A fixed value (similar to 2.7) of the ratio of the chemical loss of NOx (LNOx) to the chemical loss of HO2+RO2 (LROx) perceptibly differentiates the regimes. Following this value, data points with a ratio of HCHO/ NO2 less than 1 can be safely classified as NOx-saturated regime, whereas points with ratios between 1 and 4 fall into one or the other regime. We attribute this mainly to the HCHO-NO2 chemical relationship causing the transition line to occur at larger (smaller) HCHO/NO2 ratios in VOC-rich (VOC-poor) environments. We then redefine the transition line to LNOx/LROx similar to 2.7 that accounts for the HCHO-NO2 chemical relationship leading to HCHO = 3.7 x (NO2 - 1.14 x 10(16) molec.cm(-2)). Although the revised formula is locally calibrated (i.e., requires for readjustment for other regions), its mathematical format removes the need for having a wide range of thresholds used in HCHO/NO2 ratios that is a result of the chemical feedback. Therefore, to be able to properly take the chemical feedback into consideration, the use of HCHO = a x (NO2 - b) formula should be preferred to the ratio in future works. We then use the Geostationary Trace gas and Aerosol Sensor Optimization (GeoTASO) airborne instrument to study O-3 sensitivity in Seoul. The unprecedented spatial (250 x 250 m(2)) and temporal (similar to every 2 h) resolutions of HCHO and NO2 observations form the sensor enhance our understanding of P(O-3) in Seoul; rather than providing a crude label for the entire city, more in-depth variabilities in chemical regimes are observed that should be able to inform mitigation strategies correspondingly.
机译:臭氧生产中涉及的非线性化学方法(P(O-3))需要使用代理指示器来传送关于P(O-3)对挥发性有机化合物(VOC)或氮氧化物(NOx)的主要依赖性的信息。特别地,甲醛(HCHO)与二氧化氮(NO2)的远程感测柱(NO2)的比例已被广泛用于研究O-3敏感性。以前的研究发现,检索中的误差和柱子和近表面浓度之间的不连贯的关系是以稳健的方式施加比率的屏障。除了这些障碍之外,我们还提供了通过在韩国 - 美国空气质量(Korus-AQ)在首尔的臭氧活动期间由DC-8飞机测量限制的0-D PhotoChemical盒模型的集合提供了计算观测证据。 ,为了证明NO2的化学反馈在Hcho的形成上是NOx敏感和NOx饱和的制度之间的过渡线的控制因子。 NOx(LNOX)化学损失与HO2 + RO2(LNAX)化学损失的比例的固定值(类似于2.7)明显区分了该制度。在此值之后,具有小于1的HCho / No2之比的数据点可以安全地归类为NOx饱和的制度,而1至4之间的比率落入一个或另一个方案。我们主要将其归因于HCHO-NO2化学关系,导致过渡线在VOC富含(VOC-POWER)环境中的较大(较小)HCHO / NO2比率发生。然后,我们将过渡线重新定义为类似于2.7的LNOx / LrrOx,其考虑了通向Hcho-No2化学关系的2.7,导致Hcho = 3.7 x(No2 - 1.14 x 10(16)分子(-2))。虽然修改过的公式是局部校准的(即,需要对其他地区的重新调整),但其数学格式消除了在HCho / No2比率中使用的广泛阈值,这是化学反馈的结果。因此,为了能够正确考虑化学反馈,使用HCho = X(NO2-B)公式应该是未来工作中的比例。然后,我们使用地球静止痕量气体和气溶胶传感器优化(Geotaso)空气传播仪器在首尔研究O-3敏感性。前所未有的空间(250 x 250米(2))和时间(类似于每2小时)的HCHO和NO2观察的分辨率,形成传感器,增强了首尔的P(O-3)的理解;观察到化学制度的更深入的变量,而不是为整个城市提供原油标签,而是能够相应地向缓解策略提供信息。

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