Spatiotemporal inhomogeneity in NO 2 over Fukuoka observed by ground-based MAX-DOAS Hisahiro Takashima a, b, * , Yugo Kanaya b , Hitoshi Irie c a Faculty of Science, Fukuoka University, Fukuoka, Japan b Department of Environmental Geochemical Cycle Research, Japan Agency for Marine-Earth Science and Technology (JAMSTEC), Yokohama, Japan c Center for Environmental Remote Sensing (CEReS), Chiba University, Chiba, Japan highlights NO 2 prole observations have been made by using MAX-DOAS at Fukuoka, an urban area. NO 2 inhomogeneity is strongly related to transport associated with a landesea breeze. Observation by MAX-DOAS is a powerful tool for understanding of pollutant transport. article info Article history: Received 23 February 2014 Received in revised form 24 October 2014 Accepted 31 October 2014 Available online 31 October 2014 Keywords: Nitrogen dioxide MAX-DOAS Boundary layer Land-sea breeze Japan abstract Continuous NO 2 prole observations have been made using ground-based Multi-Axis Differential Optical Absorption Spectroscopy (MAX-DOAS) at Fukuoka (33.55 N, 130.36 E), an urban area in Japan. Throughout the year, NO 2 variations measured by MAX-DOAS (0e100 m) are in good agreement with in situ surface NO 2 measurements on several-day, week-to-week, and seasonal timescales. We investigated the spatiotemporal inhomogeneity in NO 2 over Fukuoka by observing at two azimuth angles: the Tenjin (towards the city center) and Itoshima (away from the city center) directions. In terms of diurnal vari- ations, NO 2 in both directions show clear morning maxima, on account of local emissions in the morning and the development of a boundary layer. The concentrations in the early morning are nearly the same in both directions, but they are higher in the Tenjin direction during most of the daytime on average. Variability in both directions, as well as spatial inhomogeneity, is large during most of the daytime except for in the morning. The diurnal maximum for 0e1 km between 10 and 13 LT is sometimes observed in the Tenjin direction; in some cases, 1 h after this maximum, a maximum is also observed in the Itoshima direction. The NO 2 maxima for the upper level (1e2 km) in both directions are also delayed from the maximum in the Tenjin direction for 0e1 km. Analysis of the surface wind eld indicates that the NO 2 inhomogeneity is strongly related to vertical/horizontal transport of high concentrations of NO 2 from the city center, and to horizontal transport of low concentrations from the ocean via a landesea breeze. Three-dimensional continuous observations by MAX-DOAS are potentially a powerful tool for increasing our understanding of pollutant transport and mixing in urban areas. © 2014 Elsevier Ltd. All rights reserved. 1. Introduction Satellite observations have revealed monotone increasing con- centrations of tropospheric nitrogen dioxide (NO 2 ) over the Asian continent, including China, in recent decades, due to increases in anthropogenic emissions (e.g., Richter et al., 2005; Irie et al., 2009; Ma et al., 2013). Among these emissions, NO 2 is one of the most important species for tropospheric chemistry, including ozone chemistry, and is therefore important for understanding our at- mospheric environment. The main sources of nitrogen oxides (NO x ¼ NO 2 þ NO) are fossil fuel combustion, biomass burning, and production from natural sources (soil and lightning). In urban areas, the main source is fossil fuel combustion, and spatial variations in NO x concentrations are large on account of the spatial complexity of emission sources and the short photochemical lifetimes of NO x species. To enhance our knowledge of tropospheric chemistry, it is important to gain a quantitative understanding of the impact of the emission changes on the chemical balance over both the source area and the surrounding area. * Corresponding author. Faculty of Science, Fukuoka University, Fukuoka, Japan. E-mail address: hisahiro@fukuoka-u.ac.jp (H. Takashima). Contents lists available at ScienceDirect Atmospheric Environment journal homepage: www.elsevier.com/locate/atmosenv http://dx.doi.org/10.1016/j.atmosenv.2014.10.057 1352-2310/© 2014 Elsevier Ltd. All rights reserved. Atmospheric Environment 100 (2015) 117e123