Department of Environmental and Natural Resource Science, Faculty of Agriculture, Tokyo University of Agriculture and Technology, 3-5-8 Saiwai-cho, Fuchu, Tokyo 183-8538, Japan.
Department of Applied Chemistry, Graduate School of Engineering, Osaka Prefecture University, 1-1, Gakuen-cho, Naka-ku, Sakai, Osaka 599-8531, Japan.
Sci Total Environ. 2017 Aug 15;592:178-186. doi: 10.1016/j.scitotenv.2017.03.122. Epub 2017 Mar 17.
Nitrous acid (HONO) plays an important role in the formation of OH radicals, which are involved in photochemical oxidation. HONO concentrations in ambient air at urban sites have previously been measured, but very few studies have been performed in central Tokyo. In this study, HONO concentrations in ambient air in southeast central Tokyo (near Tokyo Bay) in winter were determined by incoherent cavity enhanced absorption spectroscopy. The O, NO, NO, and SO concentrations were simultaneously determined. The NO concentrations were used to classify the parts of the study period into types I (high pollution), II (medium pollution), and III (low pollution). The maximum HONO concentrations in the type I, II, and III periods were 7.1, 4.5, and 3.0ppbv, respectively. These concentrations were comparable to concentrations previously found in other Asian megacities. The mean HONO concentration varied diurnally, and HONO was depleted between 00:00 and 03:00 each day. The sampling site is surrounded by roads with high traffic loads, but vehicular emissions were estimated to contribute <10% of the HONO concentrations. Two positive and negative relative humidity dependences of the HONO to NO ratio were confirmed, implying the existence of the two different secondary formation process of HONO. The NO to HONO conversion rates at night in the type I, II, and III periods were 6.3×10, 7.6×10, and 4.2×10h, respectively.
亚硝酸(HONO)在 OH 自由基的形成中起着重要作用,而 OH 自由基又参与光化学氧化。此前已经测量了城市地区环境空气中的 HONO 浓度,但在东京中心进行的研究很少。本研究采用非相干腔增强吸收光谱法测定了冬季东京东南部(靠近东京湾)环境空气中的 HONO 浓度。同时测定了 O、NO、NO 和 SO 浓度。利用 NO 浓度将研究期间的部分时间分为 I 型(高污染)、II 型(中污染)和 III 型(低污染)。I 型、II 型和 III 型期间的 HONO 最大浓度分别为 7.1、4.5 和 3.0ppbv,与之前在其他亚洲特大城市中发现的浓度相当。HONO 浓度随时间呈日变化,每天 00:00 至 03:00 之间 HONO 被消耗。采样点周围有交通负荷较高的道路,但车辆排放估计仅占 HONO 浓度的<10%。证实了 HONO 与 NO 比值与相对湿度呈正相关和负相关两种关系,这意味着存在两种不同的 HONO 二次形成过程。I 型、II 型和 III 型期间夜间的 NO 向 HONO 的转化率分别为 6.3×10、7.6×10 和 4.2×10h。