Department of Natural Resources and Environmental Science, University of Nevada-Reno, Reno, NV, USA.
Department of Natural Resources and Environmental Science, University of Nevada-Reno, Reno, NV, USA.
Sci Total Environ. 2015 Oct 15;530-531:471-482. doi: 10.1016/j.scitotenv.2014.12.027. Epub 2014 Dec 26.
Ozone (O3) has been measured at Great Basin National Park (GBNP) since September 1993. GBNP is located in a remote, rural area of eastern Nevada. Data indicate that GBNP will not comply with a more stringent National Ambient Air Quality Standard (NAAQS) for O3, which is based upon the 3-year average of the annual 4th highest Maximum Daily 8-h Average (MDA8) concentration. Trend analyses for GBNP data collected from 1993 to 2013 indicate that MDA8 O3 increased significantly for November to February, and May. The greatest increase was for May at 0.38, 0.35, and 0.46 ppb yr(-1) for the 95th, 50th, and 5th percentiles of MDA8 O3 values, respectively. With the exception of GBNP, continuous O3 monitoring in Nevada has been limited to the greater metropolitan areas. Due to the limited spatial detail of O3 measurements in rural Nevada, a network of rural monitoring sites was established beginning in July 2011. For a period ranging from July 2011 to June 2013, maximum MDA8 O3 at 6 sites occurred in the spring and summer, and ranged from 68 to 80ppb. Our analyses indicate that GBNP, in particular, is ideally positioned to intercept air containing elevated O3 derived from regional and global sources. For the 2 year period considered here, MDA8 O3 at GBNP was an average of 3.1 to 12.6 ppb higher than at other rural Nevada sites. Measured MDA8 O3 at GBNP exceeded the current regulatory threshold of 75 ppb on 7 occasions. Analyses of synoptic conditions, model tracers, and air mass back-trajectories on these days indicate that stratospheric intrusions, interstate pollution transport, wildfires, and Asian pollution contributed to elevated O3 observed at GBNP. We suggest that regional and global sources of ozone may pose challenges to achieving a more stringent O3 NAAQS in rural Nevada.
自 1993 年 9 月以来,臭氧(O3)一直在大盆地国家公园(GBNP)进行测量。GBNP 位于内华达州东部偏远的农村地区。数据表明,GBNP 将不符合更严格的臭氧国家环境空气质量标准(NAAQS),该标准基于年度第 4 高最大日 8 小时平均(MDA8)浓度的 3 年平均值。对 1993 年至 2013 年收集的 GBNP 数据进行的趋势分析表明,11 月至 2 月和 5 月的 MDA8 O3 显著增加。最大的增加是在 5 月,MDA8 O3 的第 95、50 和 5 个百分位数的增长率分别为 0.38、0.35 和 0.46 ppb yr(-1)。除 GBNP 外,内华达州的连续臭氧监测仅限于大都市区。由于内华达州农村地区臭氧测量的空间细节有限,因此从 2011 年 7 月开始建立了一个农村监测站点网络。在 2011 年 7 月至 2013 年 6 月期间,6 个站点的最大 MDA8 O3 出现在春季和夏季,范围为 68 至 80ppb。我们的分析表明,特别是 GBNP,非常适合拦截来自区域和全球来源的臭氧含量升高的空气。在考虑的 2 年期间,GBNP 的 MDA8 O3 平均比其他内华达州农村站点高 3.1 至 12.6 ppb。GBNP 的 MDA8 O3 有 7 次超过当前 75ppb 的监管阈值。这些日子的天气条件分析、模型示踪剂和空气团后向轨迹表明,平流层入侵、州际污染传输、野火和亚洲污染导致了 GBNP 观测到的臭氧升高。我们认为,臭氧的区域和全球来源可能对内华达州达到更严格的臭氧 NAAQS 构成挑战。