Pergamon zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQPONMLKJIHGFEDCBA Atmospherrc Environment Vol. 30, No. 4, pp. 649-659, 1996 Copyright Q 1996 Elsevier Science Ltd Printed in Great Britain. All rights resnvd 135%2310/96 $15.00 + 0.00 1352-2310(95)00294-A MEASUREMENTS AND ANALYSIS OF REACTIVE NITROGEN SPECIES IN THE RURAL TROPOSPHERE OF SOUTHEAST UNITED STATES: SOUTHERN OXIDANT STUDY SITE SONIA VINEY P. ANEJA,* DEUG-SO0 KIM, MITA DAS and BENJAMIN E. HARTSELL Department of Marine, Earth and Atmospheric Sciences, North Carolina State University, Raleigh, NC 27695-8208, U.S.A. zyxwvutsrqponmlkjihgfedcbaZYXWVUTSRQP (First received 18 March 1993 and infinalform 10 July 1995) Abstract-Ambient concentrations of reactive nitrogen compounds as well as total NO, were measured during June and early July 1992 at a rural site, site SONIA, in the central Piedmont region of North Carolina as a part of the Southern Oxidants Study. The measurements of reactive nitrogen species were made in an effort to provide a comprehensive understanding of nitrogen chemistry and to investigate the total nitrogen budget at the site. NO, NO, and NO showed diurnal variations with maxima in the morning between 0600 and 0900 EST. The maximum NO,, concentration reached was _ 14.5 ppbv, and the maximum concentrations of NO and NO, were 5.4 and 7.8 ppbv, respectively. The mean NO, mixing ratio was found to be 2.88 + 1.58 ppbv (n = 743) with an average daily maximum of 3.6 ppbv. The mean mixing ratios of NO and NO, were found to be 0.15 f 0.29 ppbv (n = 785) and 1.31 + 0.99 ppbv (n = 769). Average daily maxima of NO and NO, were 0.4 and 2.0 ppbv, respectively. HNO, and PAN showed diurnal variation with maxima in the afternoon and minimum in the night, and mean mixing ratios were found to be 0.67 + 0.33 ppbv (n = 250) and 0.40 + 0.24 ppbv (n = 578). The fractions of individual reactive nitrogen species to total NO, were investigated and contrasted to the results from a remote marine site and rural continental sites. As in two other rural continental sites in the U.S., NO, was found to be the most abundant constituent (~45%) of NO,; while HNO, was the most abundant compound in NO, measured at a remote marine site. The discrepancy between the NO, partitioning at site SONIA and the marine site is attributed to the influence of local and regional anthropogenic sources of NO, and the continental origin of the majority of air masses encountered at the site. The NO,/NO, ratio and NO, ( = NO, - NO,) were used as an indicator of the chemical age of airmasses. The NO&O, ratio showed strong positive correlations with the photochemical oxidants HNO, (r = 0.76), PAN (r = 0.68) and 0, (r = 0.79) measured at the site. Positive correlations were found between surface wind direction and both the magnitude of NO, and the NO,/NO, ratio. These correlations suggest that synoptic meteorological conditions and transport of NO, are important in the distribution of NO, and its relationship with photochemical oxidants at the site. The ozone production efficiency was illustrated by correlation of 0, and NO, and compared with other published measurements made in the Southeast U.S., and published results from a 3D Eulerian model simulation. Key word index: Reactive nitrogen species, atmospheric budget, ozone, oxidants, modeling. INTRODUCTION Recent experiments and model calculations indicate that reactive species of oxides of nitrogen, NO, (NO, = NO + NOJ, play an important role in the photochemistry of the troposphere. They participate not only in the acidification of precipitation but also in the formation of tropospheric ozone. Throughout these reactions, the concentration of NO, plays an important role in the distribution of O3 and the radical balance in the troposphere. The primary pollutant, NO, is ultimately oxidized to HNOJ which is removed from the atmosphere by wet * Author to whom correspondence should be addressed. and dry deposition. Organic peroxy and hydroperoxy radicals are responsible for much of the oxidation of NO to NOz. In the lower troposphere, O3 is formed by photochemical processes involving the oxidation of nonmethane hydrocarbons (NMHCs) in the pres- ence of NO,. While the NMHCs are consumed in these processes, NO, acts as a catalyst. The only known photochemical reaction in the troposphere that produces ozone is the photolysis of NO2 yielding atomic oxygen (O(3P)), and its subsequent combina- tion with O2 to produce NO and ozone. For net ozone production to occur, the NO2 has to be pro- duced from NO by species other than ozone itself. Thus, the oxidation of NO by ozone and the photoly- sis of the resultant NO2 yields no net change in ozone, i.e. the photostationary state. However, the peroxy