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机构地区:[1]中国气象科学研究院灾害天气国家重点实验室&中国气象局大气化学重点开放实验室,北京100081 [2]北京大学物理学院大气与海洋科学系,北京100871
出 处:《科学通报》2017年第23期2666-2670,共5页Chinese Science Bulletin
基 金:公益性行业(气象)科研专项(GYHY201106033);中国气象科学研究院基本科研业务费(2017Y002);国家自然科学基金(41175004;41465001)资助
摘 要:2017年4月,中国共产党中央委员会和国务院决定在河北设立雄安新区,以推进京津冀协同发展,要将雄安新区打造为环境优美的生态城市.通过分析雄安新区2016年5月24日至2017年4月30日的空气质量数据和气象数据,对该地区的大气污染现状进行了研究,并揭示其与气象条件的关系,旨在为雄安新区的合理规划提供科学依据.研究发现雄安新区的主要大气污染物为PM_(2.5)和PM_(10),其重污染过程主要出现在秋、冬两季,污染程度与相对湿度呈正相关,与风速和温度呈负相关.尽管雄安新区目前的开发程度较低,但受本地排放和周边污染物输送的共同影响,大气污染问题不容忽视.在雄安新区的规划和建设过程中,需要考虑周边地区的协调发展,共同治理大气环境.In April 2017, the central government of China announced it would establish the Xiong'an New Area in Hebei Province, as part of measures to advance the coordinated development of the Beijing-Tianjin-Hebei(BTH) region. The area is expected to become an innovative, market-driven green city; thus, it is urgent to address its environmental issues before urban construction begins. This study involved a systematic analysis of atmospheric pollutants PM(2.5), PM(10), CO, SO2, NO2, and O3, and their relationship to meteorological parameters in the Xiong'an area for a continuous period from May 2016 to April 2017. It used observations of 2-m temperature, 2-m relative humidity, and 10-m wind speed along with measurements of the concentration of these six criteria pollutants in Anxin, Rongcheng, and Xiongxian taken on an hourly basis. Results revealed that the Xiong'an area experienced severe air pollution, with heavy aerosol loadings. The annual averaged concentrations of PM(2.5) and PM(10) were 101.3 and 144.2 mg m^(-3), respectively, significantly exceeding the Grade II standard of the Chinese Ambient Air Quality Standards. The maximum 24-h average concentrations of PM(2.5) and PM(10) were 540.1 and 642.1 mg m^(-3), respectively. Distinct seasonal trends were observed for PM(2.5) and PM(10), with the maximum concentrations occurring in winter and the minimum in summer. Other trace gaseous pollutants, including CO, SO2, and NO2 demonstrated similar seasonal variations. Contrarily, O3 demonstrated a reversed seasonal trend, with concentration peaking in summer, decreasing in spring and fall, and at its lowest in winter. Seasonal variations of atmospheric pollutants were modulated by the seasonal variations in pollutant emissions, but they were also strongly related to meteorological conditions. The relatively cool thermal conditions and low wind speeds in fall and winter can limit the development of the planetary boundary layer and the horizontal transport of pollutants. Suc
分 类 号:X51[环境科学与工程—环境工程]
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