1. 中山大学智能工程学院,广东,广州,510006
2. 广东省交通环境智能监测与治理工程技术研究中心,广东,广州,510275
3. 广东省智能交通系统重点实验室,广东,广州,510275
4. 深圳市城市交通规划设计研究中心股份有限公司,广东,深圳,518021
纸质出版日期:2020,
网络出版日期:2020-1-25,
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罗银萍, 陈同, 丁卉, 等. 2014-2018年春节期间北京交通站PM2.5及NO2污染特征分析[J]. 中山大学学报(自然科学版)(中英文), 2020,59(1):50-63.
LUO Yinping, CHEN Tong, DING Hui, et al. Characteristics analysis of PM2.5 and NO2 pollution at Beijing traffic stations during the Spring Festival from 2014 to 2018#br# #br#[J]. Acta Scientiarum Naturalium Universitatis SunYatseni, 2020,59(1):50-63.
罗银萍, 陈同, 丁卉, 等. 2014-2018年春节期间北京交通站PM2.5及NO2污染特征分析[J]. 中山大学学报(自然科学版)(中英文), 2020,59(1):50-63. DOI: 10.13471/j.cnki.acta.snus.2020.01.007.
LUO Yinping, CHEN Tong, DING Hui, et al. Characteristics analysis of PM2.5 and NO2 pollution at Beijing traffic stations during the Spring Festival from 2014 to 2018#br# #br#[J]. Acta Scientiarum Naturalium Universitatis SunYatseni, 2020,59(1):50-63. DOI: 10.13471/j.cnki.acta.snus.2020.01.007.
利用2014-2018年北京市春节前后交通污染监测站的
PM2.5和NO
2
浓度数据,采用浓度特征对比、
PM2.5
/CO比值等方法,初步评估春节期间烟花禁燃措施和机动车减排的效果,探讨烟花燃放及气象条件对空气质量的影响。结果表明:
PM2.5
和
NO
2
浓度变化特征不同,春节期间
PM2.5
平均浓度为103.6 μg/m
3
高于非春节期间25.3%;而
NO
2
平均浓度为53.8 μg/
m
3
低于非春节期间19.5%,主要受到机动车减排的影响。2014年春节期间
PM2.5
浓度最低,2015-2018年
PM2.5
浓度呈逐年下降趋势
NO
2
浓度无明显年际变化特征。烟花爆竹燃放对
PM2.5
浓度影响显著,对
NO
2
浓度影响较小,除夕期间对
PM2.5
浓度的最大贡献值达283.4~704.1 μg/
m
3
。2018年北京市五环内禁燃烟花措施对交通站
PM2.5
污染改善明显
PM2.5
浓度较前4年均值下降25.2%
NO
2
浓度仅下降24%;禁燃对燃放高峰期
PM2.5
浓度有明显削峰作用,无有利扩散气象条件下,除夕期间烟花燃放对
PM2.5
浓度的最大贡献值仍较前4年下降45.0%。气象条件对春节期间
PM2.5
浓度变化的影响作用较
NO
2
显著,有利扩散气象条件是2014年春节期间
PM2.5
污染较非春节期间明显改善的主要原因。
Based on hourly observation data of
PM2.5
and
NO
2
concentrations at Beijing traffic stations during the Spring Festival from 2014 to 2018
the effects of vehicle emission reduction and fireworks forbidden and the impacts of emissions from fireworks and meteorological conditions on air quality were analyzed by comparing concentration characteristics and ratio of
PM2.5
to CO The results showed that characteristics of
PM2.5
and
NO
2
concentrations were different during the Spring Festival. The average
PM2.5
concentrations from 2014-2018 were 103.6 μg/
m
3
and 25.3% higher than those before and after the Spring Festival. Significantly affected by vehicle emission reduction at traffic stations
the
NO
2
concentration was 53.8 μg/
m
3
and 19.5% lower than those before and after the Spring Festival. The concentrations of
PM2.5
during the Spring Festival was lowest in 2014
and decreased year by year from 2015-2018. The burning of fireworks had relatively greater impacts on
PM2.5
than
NO
2
During the New Years Eve
the maximum contribution of hourly
PM2.5
concentration from burning fireworks was 283.4-704.1 μg/
m
3
Compared with the average of the previous four years
the concentrations of
PM2.5
decreased by 25.2% and
NO
2
reduced by only 2.4%
which implied
PM2.5
pollution was improved significantly by the measures of banning fireworks within the Fifth Ring Road in 2018. Under the meteorological conditions unfavorable to atmospheric diffusion
the maximum contribution of
PM2.5
concentration during the New Year’s Eve was still 45.0% lower than that of the previous four years
indicating great reduction effect of fireworks prohibition measures. The effect of meteorological conditions on the
PM2.5
during the Spring Festival was more significant than those of
NO
2
. The meteorological condition favorable for atmospheric diffusion was the main reason for the great improvement of
PM2.5
pollution in 2014.
春节期间交通站污染物烟花爆竹气象条件
Spring Festival periodtraffic stationspollutantsfireworksmeteorological condition
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