|本期目录/Table of Contents|

[1]沈利娟,王红磊*,赵天良,等.第十四届全运会大气污染物减排措施对西安市气溶胶中水溶性离子和含碳组分的影响[J].地球科学与环境学报,2024,46(01):38-53.[doi:10.19814/j.jese.2023.05064]
 SHEN Li-juan,WANG Hong-lei*,ZHAO Tian-liang,et al.Influence of Air Pollutant Reduction Measures on Aerosol Water-soluble Ions and Carbonaceous Components During the 14th National Games in Xi'an City of Shaanxi, China[J].Journal of Earth Sciences and Environment,2024,46(01):38-53.[doi:10.19814/j.jese.2023.05064]
点击复制

第十四届全运会大气污染物减排措施对西安市气溶胶中水溶性离子和含碳组分的影响(PDF)
分享到:

《地球科学与环境学报》[ISSN:1672-6561/CN:61-1423/P]

卷:
第46卷
期数:
2024年第01期
页码:
38-53
栏目:
环境与可持续发展
出版日期:
2024-01-15

文章信息/Info

Title:
Influence of Air Pollutant Reduction Measures on Aerosol Water-soluble Ions and Carbonaceous Components During the 14th National Games in Xi'an City of Shaanxi, China
文章编号:
1672-6561(2024)01-0038-16
作者:
沈利娟1王红磊2*赵天良2施双双1武自豪2可 玥2刘焕武3
(1. 无锡学院 大气与遥感学院,江苏 无锡 214105; 2. 南京信息工程大学 中国气象局气溶胶云-降水重点开放实验室,江苏 南京 210044; 3. 西安市环境监测站,陕西 西安 710119)
Author(s):
SHEN Li-juan1 WANG Hong-lei2* ZHAO Tian-liang2 SHI Shuang-shuang1 WU Zi-hao2 KE Yue2 LIU Huan-wu3
(1. School of Atmosphere and Remote Sensing, Wuxi University, Wuxi 214105, Jiangsu, China; 2. Key Laboratory for Aerosol-cloud-precipitation of China Meteorological Administration, Nanjing University of Information Science & Technology, Nanjing 210044, Jiangsu, China; 3. Xi'an Environmental Monitoring Station, Xi'an 710119, Shaanxi, China)
关键词:
水溶性离子 有机碳 元素碳 日变化 PM2.5 臭氧 第十四届全运会 西安
Keywords:
water-soluble ion organic carbon elemental carbon diurnal variation PM2.5 O3 the 14th National Games Xi'an
分类号:
X513
DOI:
10.19814/j.jese.2023.05064
文献标志码:
A
摘要:
人为源密集的城市是空气污染影响的主要区域,厘清城市地区排放源的变化与大气污染物浓度之间的影响作用机制,有助于协调我国大气污染防控与城市社会经济发展之间的关系。为研究第十四届全运会期间大气污染物减排措施对西安市大气污染物(PM2.5、PM10、SO2、NO2、O3和CO)的影响,于2021年8月6日至10月1日使用在线监测仪器观测了环境六要素、气象要素和PM2.5中的气溶胶化学组分(有机碳、元素碳和水溶性离子)。结果表明:大气污染物减排措施对主要污染物O3和PM2.5浓度日变化的影响不同,主要由温度对光化学过程的影响和扩散条件差异导致。O3在减排措施实施期间晴天峰值浓度更高、持续时间更长、浓度变化更迅速。PM2.5在减排措施实施前晴天白天的峰值浓度较高,并在减排措施实施期间晴天夜间的峰值浓度较高。大气污染物减排措施对PM2.5中化学组分的影响不同,尤其是对有机碳的组成影响较大。与减排措施实施前晴天相比,减排措施实施期间晴天NO-3、SO2-4、NH+4、Cl-、Ca2+、Na+和NO-2浓度降低了17.9%~71.8%,K+、Mg2+和元素碳浓度增加了1.9%~13.6%,有机碳浓度仅降低了1.0%,但是一次有机碳浓度增加了13.6%,二次有机碳浓度降低了4.7%。NO-3/SO2-4值在减排措施实施期间晴天(0.53)远低于减排措施实施前晴天(1.66),表明减排措施实施期间交通源的贡献显著降低。降雨对NO-3和NH+4的清除较弱,反而会增加其浓度,但对K+、Mg2+、Ca2+和Na+的清除作用较强。NO-3、SO2-4和NH+4在减排措施实施前后均是水溶性离子最重要的组成,在水溶性离子中的占比为90.8%(减排措施实施前的晴天)~95.8%(减排措施实施期间的雨天)。二次有机碳是有机碳的主要组成,占比为75.5%(减排措施实施期间的雨天)~79.9%(减排措施实施前的晴天)。不同阶段的水溶性离子和含碳气溶胶浓度日变化特征不同。NO-3、SO2-4和NH+4浓度晴天的日变化为单峰型分布,雨天为多峰型分布。
Abstract:
In order to study the influence of air pollutant reduction measures on aerosol water-soluble ions, and organic carbon(OC)and element carbon(EC)during the 14th National Games in Xi'an city of Shaanxi, China, real-time observation instruments were used to motor the hourly concentration of the atmospheric pollutants(PM2.5, PM10, SO2, NO2, O3 and CO), meteorological elements, and chemical composition(OC, EC and water-soluble ions)of PM2.5 from August 6 to October 1, 2021. The results show that the air pollutant reduction measures have different effects on the diurnal variations of concentrations of O3 and PM2.5, mainly caused by the influence of temperature on photochemical processes and differences in diffusion conditions. The peak concentration of O3 on sunny days during the implementation of air pollutant reduction measures is higher, last longer, and the concentration changes more rapidly. The peak concentration of PM2.5 is higher in the daytime of the sunny days before the implementation of air pollutant reduction measures, while the peak concentration is higher at night of sunny days during the implementation of air pollutant reduction measures. The air pollutant reduction measures have different effects on the chemical components in PM2.5, especially the composition of OC. On sunny days during the implementation of air pollutant reduction measures, the concentrations of NO-3, SO2-4, NH+4, Cl-, Ca2+, Na+ and NO-2 decrease by 17.9%-71.8%, and the concentrations of K+, Mg2+ and EC increase by 1.9%-13.6%, the concentration of OC on sunny days only decreases by 1.0%, but the primary organic carbon(POC)increases by 13.6%, and the secondary organic carbon(SOC)decreases by 4.7%. The NO-3/SO2-4 ratio on sunny days during the implementation of air pollutant reduction measures(0.53)is much lower than that on sunny days before the implementation of air pollutant reduction measures(1.66), indicating that the contribution of traffic source emission is significantly reduced during the implementation of air pollutant reduction measures. Rainfall has a weak scavenging effect on NO-3 and NH+4, and increases their concentrations, but it has a strong scavenging effect on K+, Mg2+, Ca2+ and Na+. NO-3, SO2-4 and NH+4 are the essential components of water-soluble ions, accounting for 90.8% of the water-soluble ions(sunny days before the implementation of air pollutant reduction measures)to 95.8%(rainy days during the implementation of air pollutant reduction measures). The diurnal variations of water-soluble ions and carbonaceous aerosols differ at different stages.The diurnal variations of NO-3, SO2-4 and NH+4 present unimodal distributions on sunny days and multimodal distributions on rainy days.

参考文献/References:

[1] HAN R,WANG S X,SHEN W H,et al.Spatial and Temporal Variation of Haze in China from 1961 to 2012[J].Journal of Environmental Sciences,2016,46:134-146.
[2] FAN H,ZHAO C F,YANG Y K.A Comprehensive Analysis of the Spatio-temporal Variation of Urban Air Pollution in China During 2014-2018[J].Atmospheric Environment,2020,220:117066.
[3] ZHUANG X L,WANG Y S,HE H,et al.Haze Insights and Mitigation in China:An Overview[J].Journal of Environmental Sciences,2014,26(1):2-12.
[4] 刘光瑾,苏方成,徐起翔,等.河南省18个城市大气污染物分布特征、区域来源和传输路径[J].环境科学,2022,43(8):3953-3965.
LIU Guang-jin,SU Fang-cheng,XU Qi-xiang,et al.One-year Simulation of Air Pollution in Central China,Characteristics,Distribution,Inner Region Cross-transmission,and Pathway Research in 18 Cities[J].Environmental Science,2022,43(8):3953-3965.
[5] DANG R J,LIAO H.Radiative Forcing and Health Impact of Aerosols and Ozone in China as the Conse-quence of Clean Air Actions over 2012-2017[J].Geophysical Research Letters,2019,46(21):12511-12519.
[6] 熊江荷,孔少飞,郑 煌,等.排放和气象对疫情前后武汉不同类型点位大气污染物的影响[J].环境科学,2023,44(2):670-679.
XIONG Jiang-he,KONG Shao-fei,ZHENG Huang,et al.Impacts of Emission and Meteorological Conditions on Air Pollutants at Various Sites Around the COVID-19 Lockdown in Wuhan[J].Environmental Science,2023,44(2):670-679.
[7] MA T,DUAN F K,HE K B,et al.Air Pollution Cha-racteristics and Their Relationship with Emissions and Meteorology in the Yangtze River Delta Region During 2014-2016[J].Journal of Environmental Sci-ences,2019,83:8-20.
[8] 王红磊,刘思晗,孙杰娟,等.机动车源和民用燃料源颗粒物中有机碳和元素碳的排放特征[J].环境科学,2023,44(4):1890-1898.
WANG Hong-lei,LIU Si-han,SUN Jie-juan,et al.Emission Characteristics of Organic Carbon and Elemental Carbon in PM10 and PM2.5 from Vehicle Exhaust and Civil Combustion Fuels[J].Environmental Science,2023,44(4):1890-1898.
[9] 沈利娟,王红磊,赵天良,等.青藏高原东缘气溶胶粒径分布特征及其来源[J].地球科学与环境学报,2023,45(1):80-92.
SHEN Li-juan,WANG Hong-lei,ZHAO Tian-liang,et al.Size Distributions and Sources Apportionment of Aerosol Number Concentrations over the Eastern Qinghai-Tibet Plateau,China[J].Journal of Earth Sci-ences and Environment,2023,45(1):80-92.
[10] 徐振麒,尚 玥,丁 峰,等.南京亚微米级颗粒物化学组成的季节变化、粒径分布和来源[J].环境科学,2023,44(3):1310-1318.
XU Zhen-qi,SHANG Yue,DING Feng,et al.Seasonal Variations,Size Distributions,and Sources of Che-mical Components of Submicron Particulate Matter in Nanjing[J].Environmental Science,2023,44(3):1310-1318.
[11] 牛笑笑,钟艳梅,杨 璐,等.2015~2020年中国城市PM2.5-O3复合污染时空演变特征[J].环境科学,2023,44(4):1830-1840.
NIU Xiao-xiao,ZHONG Yan-mei,YANG Lu,et al.Spatiotemporal Evolution Characteristics of PM2.5-O3 Compound Pollution in Chinese Cities from 2015 to 2020[J].Environmental Science,2023,44(4):1830-1840.
[12] ZENG Y Y,CAO Y F,QIAO X,et al.Air Pollution Reduction in China:Recent Success but Great Challenge for the Future[J].Science of the Total Environment,2019,663:329-337.
[13] 卢亚灵,范朝阳,蒋洪强,等.北京市“大气十条”实施的空气质量改善效益[J].环境科学,2021,42(6):2730-2739.
LU Ya-ling,FAN Zhao-yang,JIANG Hong-qiang,et al.Economic Benefit of Air Quality Improvement During Implementation of the Air Pollution Prevention and Control Action Plan in Beijing[J].Environmental Science,2021,42(6):2730-2739.
[14] 耿冠楠,肖清扬,郑逸璇,等.实施《大气污染防治行动计划》对中国东部地区PM2.5化学成分的影响[J].中国科学:地球科学,2020,50(4):469-482.
GENG Guan-nan,XIAO Qing-yang,ZHENG Yi-xuan,et al.Impact of China's Air Pollution Prevention and Control Action Plan on PM2.5 Chemical Composition over Eastern China[J].Science China:Earth Sciences,2020,50(4):469-482.
[15] GUO B,WU H J,PEI L,et al.Study on the Spatiotemporal Dynamic of Ground-level Ozone Concentrations on Multiple Scales Across China During the Blue Sky Protection Campaign[J].Environment International,2022,170:107606.
[16] 程育恺,戴海夏,张蕴晖,等.长三角地区2017~2020年臭氧浓度时空分布与人群健康效益评估[J].环境科学,2023,44(2):719-729.
CHENG Yu-kai,DAI Hai-xia,ZHANG Yun-hui,et al.Spatial and Temporal Distribution Characteristics of Ozone Concentration and Population Health Benefit Assessment in the Yangtze River Delta Region from 2017 to 2020[J].Environmental Science,2023,44(2):719-729.
[17] 刁一伟,王红磊,沈利娟,等.2015~2021年南京市大气污染特征及污染个例研究[J].环境科学研究,2023,36(2):260-272.
DIAO Yi-wei,WANG Hong-lei,SHEN Li-juan,et al.Analysis of Air Pollution Characteristics and Associated Compound Air Pollution Case in Nanjing from 2015 to 2021[J].Research of Environmental Scien-ces,2023,36(2):260-272.
[18] 陈 楠,陈 立,王莉莉,等.2015~2020年湖北省PM2.5和臭氧复合污染特征演变分析[J].环境科学研究,2022,35(3):659-672.
CHEN Nan,CHEN Li,WANG Li-li,et al.Characte-ristic and Trend Analysis of PM2.5 and Ozone in Air Compound Pollution in Hubei Province During 2015-2020[J].Research of Environmental Sciences,2022,35(3):659-672.
[19] 张宇静,赵天良,殷翀之,等.徐州市大气PM2.5与O3作用关系的季节变化[J].中国环境科学,2019,39(6):2267-2272.
ZHANG Yu-jing,ZHAO Tian-liang,YIN Chong-zhi,et al.Seasonal Variation of the Relationship Between Surface PM2.5 and O3 Concentrations in Xuzhou[J].China Environmental Science,2019,39(6):2267-2272.
[20] 宋小涵,燕 丽,刘 伟,等.2015~2021年京津冀及周边地区PM2.5和臭氧复合污染时空特征分析[J].环境科学,2023,44(4):1841-1851.
SONG Xiao-han,YAN Li,LIU Wei,et al.Spatiotemporal Distribution Characteristics of Co-pollution of PM2.5 and Ozone over BTH with Surrounding Area from 2015 to 2021[J].Environmental Science,2023,44(4):1841-1851.
[21] 徐丹妮,王瑾婷,袁自冰,等.汾渭平原复杂地形影响下冬季PM2.5污染分布特征、来源及成因分析[J].环境科学学报,2021,41(4):1184-1198.
XU Dan-ni,WANG Jin-ting,YUAN Zi-bing,et al.Temporal-spatial Variations,Source Apportionment,and Formation Mechanisms of PM2.5 Pollution over Fenwei Plain,China[J].Acta Scientiae Circumstantiae,2021,41(4):1184-1198.
[22] 黄小刚,邵天杰,赵景波,等.汾渭平原PM2.5浓度的影响因素及空间溢出效应[J].中国环境科学,2019,39(8):3539-3548.
HUANG Xiao-gang,SHAO Tian-jie,ZHAO Jing-bo,et al.Influence Factors and Spillover Effect of PM2.5 Concentration on Fenwei Plain[J].China Environmental Science,2019,39(8):3539-3548.
[23] 黄小刚,赵景波,孙从建,等.汾渭平原PM2.5空间分布的地形效应[J].环境科学,2021,42(10):4582-4592.
HUANG Xiao-gang,ZHAO Jing-bo,SUN Cong-jian,et al.Orographic Influences on the Spatial Distribution of PM2.5 on the Fenwei Plain[J].Environmental Science,2021,42(10):4582-4592.
[24] CHEN Q C,HUA X Y,LI J W,et al.Diurnal Evolutions and Sources of Water-soluble Chromophoric Aerosols over Xi'an During Haze Event,in Northwest China[J].Science of the Total Environment,2021,786:147412.
[25] 刘威杰,胡天鹏,毛 瑶,等.汾渭平原临汾市2019年春节期间大气污染特征与来源解析[J].环境科学,2021,42(11):5122-5130.
LIU Wei-jie,HU Tian-peng,MAO Yao,et al.Characteristics and Origin Analysis of Air Pollution During the Spring Festival in Linfen,Fenwei Plain[J].Environmental Science,2021,42(11):5122-5130.
[26] 刘旻霞,李 亮,于瑞新,等.汾渭平原吸收性气溶胶时空演化及潜在源区分析[J].环境科学,2021,42(6):2634-2647.
LIU Min-xia,LI Liang,YU Rui-xin,et al.Spatio-temporal Patterns and Potential Sources of Absorbing Aerosols in the Fenwei Plain[J].Environmental Science,2021,42(6):2634-2647.
[27] 黄含含,王羽琴,李升苹,等.西安市PM2.5中水溶性离子的季节变化特征[J].环境科学,2020,41(6):2528-2535.
HUANG Han-han,WANG Yu-qin,LI Sheng-ping,et al.Seasonal Variation of Water-soluble Ions in PM2.5 in Xi'an[J].Environmental Science,2020,41(6):2528-2535.
[28] SHEN L J,ZHAO T L,WANG H L,et al.Importance of Meteorology in Air Pollution Events During the City Lockdown for COVID-19 in Hubei Province,Central China[J].Science of the Total Environment,2021,754:142227.
[29] BERMAN J D,EBISU K.Changes in U.S. Air Pollution During the COVID-19 Pandemic[J].Science of the Total Environment,2020,739:139864.
[30] PEI Z P,HAN G,MA X,et al.Response of Major Air Pollutants to COVID-19 Lockdowns in China[J].Science of the Total Environment,2020,743:140879.
[31] WANG H L,TAN Y,ZHANG L X,et al.Characte-ristics of Air Quality in Different Climatic Zones of China During the COVID-19 Lockdown[J].Atmospheric Pollution Research,2021,12(12):101247.
[32] 赵 刚,张亚宾,赵明升,等.2022年冬奥会期间减排措施对北京颗粒物浓度分布特征及新粒子生成的影响研究[J].中国环境科学,2023,DOI:10.19674/j.cnki.issn1000-6923.20230116.001.
ZHAO Gang,ZHANG Ya-bin,ZHAO Ming-sheng,et al.Study on the Influence of Emission Reduction Measures on the Distribution Characteristics of Particulate Matter Concentration and New Particle Gene-ration in Beijing During 2022 Winter Olympic Games[J].China Environmental Science,2023,DOI:10.19674/j.cnki.issn1000-6923.20230116.001.
[33] 侯 露,朱媛媛,刘 冰,等.冬奥会期间京津冀及周边区域空气质量时空特征、气象影响和减排效果评估[J].环境科学,2023,44(11):5899-5914.
HOU Lu,ZHU Yuan-yuan,LIU Bing,et al.Analysis on Air Quality of Spatio-temporal Characteristics,Meteorological Impact,and Emission Reduction Effect During the Winter Olympics in Beijing-Tianjin-Hebei and Its Surrounding Areas[J].Environmental Scien-ce,2023,44(11):5899-5914.
[34] STREETS D G,FU J S,JANG C J,et al.Air Quality During the 2008 Beijing Olympic Games[J].Atmospheric Environment,2007,41(3):480-492.
[35] WANG Y,LIAO H.Effect of Emission Control Mea-sures on Ozone Concentrations in Hangzhou During G20 Meeting in 2016[J].Chemosphere,2020,261:127729.
[36] SHEN L J,WANG H L,LÜ S,et al.Influence of Pollution Control on Air Pollutants and the Mixing State of Aerosol Particles During the 2nd World Internet Conference in Jiaxing,China[J].Journal of Cleaner Production,2017,149:436-447.
[37] 刁一伟,杨 孟,沈利娟,等.沙尘过程中汾渭平原气溶胶化学组分及含水量的演变特征研究[J].环境科学研究,2023,36(9):1654-1664.
DIAO Yi-wei,YANG Meng,SHEN Li-juan,et al.Evolution Characteristics of Aerosol Chemical Components and Water Content During Sandstorms in the Fenwei Plain[J].Research of Environmental Scien-ces,2023,36(9):1654-1664.
[38] GB 3095—2012,环境空气质量标准[S].
GB 3095—2012,Ambient Air Quality Standards[S].
[39] CHOW J C,WASTON J G,LU Z Q,et al.Descriptive Analysis of PM2.5 and PM10 at Regionally Representative Locations During SJVAQS/AUSPEX[J].Atmospheric Environment,1996,30(12):2079-2112.
[40] TURPIN B J,HUNTZICKER J J.Identification of Secondary Organic Aerosol Episodes and Quantification of Primary and Secondary Organic Aerosol Concentrations During SCAQS[J].Atmospheric Environment,1995,29(23):3527-3544.
[41] CASTRO L M,PIO C A,HARRISON R M,et al.Carbonaceous Aerosol in Urban and Rural European Atmospheres:Estimation of Secondary Organic Carbon Concentrations[J].Atmospheric Environment,1999,33(17):2771-2781.
[42] XU H M,CAO J J,CHOW J C,et al.Inter-annual Variability of Wintertime PM2.5 Chemical Composition in Xi'an,China:Evidences of Changing Source Emissions[J].Science of the Total Environment,2016,545/546:546-555.
[43] 罗 干,王体健,赵 明,等.基于在线监测的南京仙林PM2.5组分特征与来源解析[J].中国环境科学,2020,40(5):1857-1868.
LUO Gan,WANG Ti-jian,ZHAO Ming,et al.Chemical Composition and Source Apportionment of Fine Particulate Matter in Xianlin Area of Nanjing Basing On-line Measurement[J].China Environmental Scien-ce,2020,40(5):1857-1868.
[44] 李朝阳,袁 亮,张小玲,等.成都碳质气溶胶变化特征及二次有机碳的估算[J].中国环境科学,2022,42(6):2504-2513.
LI Zhao-yang,YUAN Liang,ZHANG Xiao-ling,et al.Characteristics of Carbonaceous Aerosols and Estimation of Secondary Organic Carbon in Chengdu[J].China Environmental Science,2022,42(6):2504-2513.
[45] DUAN J C,TAN J H,CHENG D X,et al.Sources and Characteristics of Carbonaceous Aerosol in Two Largest Cities in Pearl River Delta Region,China[J].Atmospheric Environment,2007,41(14):2895-2903.
[46] 田鹏山,曹军骥,韩永明,等.关中地区冬季PM2.5中碳气溶胶的污染特征及来源解析[J].环境科学,2016,37(2):427-433.
TIAN Peng-shan,CAO Jun-ji,HAN Yong-ming,et al.Pollution Characteristics and Sources of Carbonaceous Aerosol in PM2.5 During Winter in Guanzhong Area[J].Environmental Science,2016,37(2):427-433.
[47] 徐宏辉,徐婧莎,何 俊,等.杭甬地区大气中含碳气溶胶特征及来源分析[J].环境科学,2018,39(8):3511-3517.
XU Hong-hui,XU Jing-sha,HE Jun,et al.Characteri-stics and Source Analysis of Atmospheric Carbonaceous Aerosols in the Cities of Hangzhou and Ningbo[J].Environmental Science,2018,39(8):3511-3517.

相似文献/References:

[1]王 瑞,兰恒星*,刘世杰,等.森林火灾对岩土体物理力学特性的影响[J].地球科学与环境学报,2022,44(01):114.[doi:10.19814/j.jese.2021.08026]
 WANG Rui,LAN Heng-xing*,LIU Shi-jie,et al.Influence of Forest Fire on Physical and Mechanical Properties of Rock and Soil[J].Journal of Earth Sciences and Environment,2022,44(01):114.[doi:10.19814/j.jese.2021.08026]
[2]严维兵,饶文波*,栗天宁,等.江苏沿海沉积物有机磷含量、总有机碳、总氮与同位素特征及有机质来源解析[J].地球科学与环境学报,2024,46(01):67.[doi:10.19814/j.jese.2023.06026]
 YAN Wei-bing,RAO Wen-bo*,LI Tian-ning,et al.Organic Phosphorus Contents, Total Organic Carbon, Total Nitrogen and Their Isotopic Characteristics from Sediments in Jiangsu Coast, China and Source Identification of Organic Matter[J].Journal of Earth Sciences and Environment,2024,46(01):67.[doi:10.19814/j.jese.2023.06026]

备注/Memo

备注/Memo:
收稿日期:2023-05-30; 修回日期:2023-10-30投稿网址:http:∥jese.chd.edu.cn/
基金项目:国家重点研发计划项目(2022YFC3701204); 国家自然科学基金项目(42275196); 无锡学院引进人才科研启动专项项目(2023r035); 江苏省自然科学基金项目(BK20231300)
作者简介:沈利娟(1987-),女,江苏启东人,讲师,理学博士,E-mail:shenlj@cwxu.edu.cn。
*通信作者:王红磊(1988-),男,山东蒙阴人,副教授,理学博士,E-mail:hongleiwang@nuist.edu.cn。
更新日期/Last Update: 2024-01-25