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干旱区地理 >

2024 , Vol. 47 >Issue 8: 1358 - 1366

DOI: https://doi.org/10.12118/j.issn.1000-6060.2023.428

气候与水文

西宁市夏季居民区空气负离子浓度变化特征及其影响因子分析

  • 马红璐 ,
  • 祁栋林 ,
  • 赵彤 ,
  • 曹晓云 ,
  • 赵全宁 ,
  • 张睿
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  • 1.青海省气象科学研究所，青海 西宁 810001
    2.青海省防灾减灾重点实验室，青海 西宁 810001
马红璐（1996-），女，硕士研究生，助理工程师，主要从事生态环境气象研究. E-mail: hl20230413@163.com
祁栋林（1967-），男，学士，高级工程师，主要从事大气环境和气候变化研究. E-mail: qidl007@163.com

收稿日期: 2023-08-14

  修回日期: 2023-10-10

  网络出版日期: 2024-09-02

基金资助

青海省科技厅项目(2021-SF-141);青海省气象局面上科研项目(QXMS2023-51)

收起

Variation characteristics and influencing factors of air negative ion concentration in summer residential areas of Xining City

  • MA Honglu ,
  • QI Donglin ,
  • ZHAO Tong ,
  • CAO Xiaoyun ,
  • ZHAO Quanning ,
  • ZHANG Rui
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  • 1. Institute of Qinghai Meteorological Science Research, Xining 810001, Qinghai, China
    2. Qinghai Key Laboratory of Disaster Preventing and Reducing, Xining 810001, Qinghai, China

Received date: 2023-08-14

  Revised date: 2023-10-10

  Online published: 2024-09-02

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摘要

利用2022年5—10月在青海省西宁市典型居民区观测的空气正、负离子浓度，分析空气负离子浓度时间分布特征、评价空气清新度和清洁度，结合同期气象条件和空气污染物浓度探究其相关性。结果表明：（1） 西宁市典型居民区上午的空气负离子浓度高于下午及晚上，8—10月空气负离子浓度高于5—7月。（2） 西宁市居民区空气负离子浓度变化跟监测时的天气状况密切相关，空气负离子浓度变化遵循“雨天>阴天>多云>晴天”的规律。（3） 空气负离子浓度高说明空气清新却不代表空气清洁，高原地区城市晴天空气负离子浓度不高，空气清新度一般，而空气清洁度较高。（4） 影响西宁市居民区空气负离子浓度波动的主要气象因素为相对湿度、日照时数、水汽压、降水量和风速，抑制西宁市居民区空气负离子浓度升高的主要空气污染物为NO2、PM10、CO和PM2.5。研究结果可为高原地区居住环境、旅游健康管理以及生态环境保护提供科学数据支撑。

关键词： 居民区; 空气负离子; 气象要素; 空气质量; 青藏高原; 西宁市

本文引用格式

马红璐 , 祁栋林 , 赵彤 , 曹晓云 , 赵全宁 , 张睿 . 西宁市夏季居民区空气负离子浓度变化特征及其影响因子分析[J]. 干旱区地理, 2024 , 47(8) : 1358 -1366 . DOI: 10.12118/j.issn.1000-6060.2023.428

Abstract

Positive and negative air ion concentrations were monitored in a typical residential area of Xining City, Qinghai Province, China, from May to October 2022. The temporal distribution characteristics of negative air ion concentration were analyzed, and air freshness and cleanliness were evaluated. The correlation between negative air ion concentration and concurrent meteorological conditions and air pollutant concentrations was investigated. The following are the study findings: (1) The negative air ion concentration in a typical residential areas of Xining City is higher in the morning than in the afternoon and night. The negative air ion concentrations from August to October are higher than those from May to July. (2) The change in the negative air ion concentrations in the Xining residential area is closely related to weather conditions during monitoring, following the pattern of “rainy>cloudy>sunny”. (3) High concentrations of negative air ions indicate that air is fresh but do not necessarily mean that air is clean. On sunny days, the negative air ion concentration in plateau cities are not high and air freshness is moderate; however, air cleanliness is high. (4) Relative humidity, sunshine hours, water vapor pressure, precipitation, and wind speed mainly affect the change in negative air ion concentration. Concentrations of NO2, PM10, CO, and PM2.5 inhibit the increase of negative air ion concentration. The results provide scientific data supporting living environment improvement, tourism health management, and ecological environmental protection in plateau areas.

Key words： residential areas; negative air ions; meteorological elements; air quality; Qinghai-Tibet Plateau; Xining City

参考文献

[1] 余娟, 高占冬, 王德远, 等. 天缘洞空气负离子时空分布特征及影响因素分析[J]. 环境化学, 2021, 40(4): 1078-1087.
  [Yu Juan, Gao Zhandong, Wang Deyuan, et al. Analysis of temporal and spatial distribution characteristics and influencing factors of air anions in Tianyuan cave[J]. Environmental Chemistry, 2021, 40(4):1078-1087.]
[2] 王薇, 余庄, 凤全. 基于空气负离子浓度的城市环境空气清洁度评价[J]. 生态环境学报, 2013, 22(2): 298-303.
  [Wang Wei, Yu Zhuang, Feng Quan. Evaluation of air cleanness degree of the urban environment based on negative air ion concentration[J]. Ecology and Environmental Sciences, 2013, 22(2): 298-303.]
[3] Liu S, Li C, Chu M T, et al. Associations of forest negative air ions exposure with cardiac autonomic nervous function and the related metabolic linkages: A repeated-measure-panel study[J]. Science of the Total Environment, 2022, 850: 158019, doi: 10.1016/j.scitotenv.2022.158019.
[4] Liu S, Huang Q Y, Wu Y, el al. Metabolic linkages between indoor negative air ions, particulate matter and cardiorespiratory function: A randomized, double-blind crossover study among children[J]. Environment International, 2020, 138: 105663, doi: 10.1016/j.envint.2020.105663.
[5] 刘燕, 王业成, 王让会, 等. 南京浦口区大气负离子的时空特征及其与气象条件的关系[J]. 长江流域资源与环境, 2017, 26(5): 706-712.
  [Liu Yan, Wang Yecheng, Wang Ranghui, et al. Spatiotemporal characteristics of negative air ions and its relationship with meteorological conditions in Pukou, Nanjing[J]. Resources and Environment in the Yangtze Basin, 2017, 26(5): 706-712.]
[6] 王一荃, 周璋, 李意德, 等. 不同热带森林空气负离子浓度评价研究[J]. 生态环境学报, 2021, 30(5): 898-906.
  [Wang Yiquan, Zhou Zhang, Li Yide, et al. The spatial-temporal pattern and influencing factors of negative air ions in tropical forests, Hainan, China[J]. Ecology and Environmental Sciences, 2021, 30(5): 898-906.]
[7] 彭巍, 李明文, 王慧, 等. 空气负离子国内外研究进展及其在森林康养方面的积极作用综述[J]. 温带林业研究, 2020, 3(3): 11-14, 54.
  [Peng Wei, Li Mingwen, Wang Hui, et al. A review of the research progress of negative air ion at home and abroad and its positive role in forest health[J]. Journal of Temperate Forestry Research, 2020, 3(3): 11-14, 54.]
[8] Niu X, Li Y, Li M N, et al. Understanding vegetation structures in green spaces to regulate atmospheric particulate matter and negative air ions[J]. Atmospheric Pollution Research, 2022, 13: 101534, doi: 10.1016/j.apr.2022.101534.
[9] Yan X J, Wang H R, Hou Z Y, et al. Spatial analysis of the ecological effects of negative air ions in urban vegetated areas: A case study in Maiji, China[J]. Urban Forestry & Urban Greening, 2015, 14: 636-645.
[10] 李少宁, 李嫒, 鲁绍伟, 等. 北京西山国家森林公园中空气负离子浓度与气象因子的相关性研究[J]. 生态环境学报, 2021, 30(3): 541-547.
  [Li Shaoning, Li Yuan, Lu Shaowei, et al. Correlation between air anion concentration and meteorological factors in Beijing Xishan National Forest Park[J]. Ecology and Environmental Sciences, 2021, 30(3): 541-547.]
[11] 冯鹏飞, 于新文, 张旭. 北京地区不同植被类型空气负离子浓度及其影响因素分析[J]. 生态环境学报, 2015, 24(5): 818-824.
  [Feng Pengfei, Yu Xinwen, Zhang Xu. Variations in negative air ion concentrations associated with different vegetation types and influencing factors in Beijing[J]. Ecology and Environmental Sciences, 2015, 24(5): 818-824.]
[12] 刘晴, 高鹏, 李成, 等. 泰安市典型生态功能区空气负离子的时空分布及影响因素分析[J]. 环境化学, 2019, 38(1): 169-176.
  [Liu Qing, Gao Peng, Li Cheng, et al. Spatial-temporal distribution of negative air ions and its influencing factors in the typical ecological functional zones of Tai’an City[J]. Environmental Chemistry, 2019, 38(1): 169-176.]
[13] 张毓涛, 李吉玫. 新疆主要城市不同生态功能区夏季空气负离子特征[J]. 干旱区地理, 2012, 35(6): 864-874.
  [Zhang Yutao, Li Jimei. Characteristics of air anion concentration in different ecological functional zones in summer in main cities of Xinjiang[J]. Arid Land Geography, 2012, 35(6): 864-874.]
[14] Li A B, Li Q L, Zhou B Z, et al. Temporal dynamics of negative air ion concentration and its relationship with environmental factors: Results from long-term on-site monitoring[J]. Science of the Total Environment, 2022, 832: 155057, doi: 10.1016/j.scitotenv.2022.155057.
[15] Wang H, Wang B, Niu X, et al. Study on the change of negative air ion concentration and its influencing factors at different spatio-temporal scales[J]. Global Ecology and Conservation, 2020, 23: e01008, doi: 10.1016/j.gecco.2020.e01008.
[16] 袁相洋, 孙迎雪, 田媛, 等. 北京市不同功能区空气负氧离子及影响因素研究[J]. 环境科学与技术, 2014, 37(6): 97-102.
  [Yuan Xiangyang, Sun Yingxue, Tian Yuan, et al. Experimental research of air negative oxygen ion and their affecting factors in different ecological functional areas of Beijing[J]. Environmental Science & Technology, 2014, 37(6): 97-102.]
[17] 韦朝领, 王敬涛, 蒋跃林, 等. 合肥市不同生态功能区空气负离子浓度分布特征及其与气象因子的关系[J]. 应用生态学报, 2006, 17(11): 2158-2162.
  [Wei Chaoling, Wang Jingtao, Jiang Yuelin, et al. Air negative charge ion concentration and its relationships with meteorological factors in different ecological functional zones of Hefei City[J]. Chinese Journal of Applied Ecology, 2006, 17(11): 2158-2162.]
[18] QX/R 380-2017. 中华人民共和国气象行业标准: 空气负(氧)离子浓度等级[S]. 北京: 气象出版社, 2017.
  [QX/R 380-2017. Meteorological Industry Standard of the People’s Republic of China: Grade of air negative (oxygen) ion concentration[S]. Beijing: China Meteorological Press, 2017.]
[19] 郁珍艳, 李正泉, 樊高峰, 等. 浙江省气象及环境因子对负氧离子浓度的影响分析[J]. 中国环境科学, 2023, 43(2): 514-524.
  [Yu Zhenyan, Li Zhengquan, Fan Gaofeng, et al. Effects of meteorological and environmental factors on negative oxygen ions concentration in Zhejiang Province[J]. China Environmental Science, 2023, 43(2): 514-524.]
[20] 王薇, 余庄. 中国城市环境中空气负离子研究进展[J]. 生态环境学报, 2013, 22(4): 705-711.
  [Wang Wei, Yu Zhuang. Research progress on negative air ions in urban environment in China[J]. Ecology and Environmental Sciences, 2013, 22(4): 705-711.]
[21] 耿生莲, 王志涛, 辛永清, 等. 西宁市城市典型绿地空气负氧离子浓度特征研究[J]. 山西林业科技, 2016, 45(4): 4-9.
  [Geng Shenglian, Wang Zhitao, Xin Yongqing, et al. Characteristics study on atmospheric negative oxygen ions concentration of typical urban green space in Xining City[J]. Shanxi Forestry Science and Technology, 2016, 45(4): 4-9.]
[22] 卢振礼, 杨成芳, 崔广暑, 等. 雷雨天气对负氧离子浓度的影响[J]. 气象科技, 2021, 49(2): 284-290.
  [Lu Zhenli, Yang Chengfang, Cui Guangshu, et al. Effect of thunderstorms on negative oxygen ion concentration[J]. Meteorological Science and Technology, 2021, 49(2): 284-290.]
[23] 施光耀, 桑玉强, 张劲松, 等. 不同光照强度下植物电信号变化特征及其与空气负离子的关系[J]. 应用生态学报, 2022, 33(2): 439-447.
  [Shi Guangyao, Sang Yuqiang, Zhang Jinsong, et al. Variation characteristics of plant electrical signal and their relationship with negative air ion under different light intensities[J]. Chinese Journal of Applied Ecology, 2022, 33(2): 439-447.]
[24] 侯秀娟, 闫晓云, 王波, 等. 夏季干旱半干旱城市公园绿地空气负离子与空气颗粒物变化特征[J]. 南京林业大学学报(自然科学版), 2022, 46(4): 212-220.
  [Hou Xiujuan, Yan Xiaoyun, Wang Bo, et al. Variation characteristics of the air anion and air particulate matter in arid and semi-arid urban park green spaces during summer[J]. Journal of Nanjing Forestry University (Natural Sciences Edition), 2022, 46(4): 212-220.]
[25] Nadali A, Arfaeinia H, Asadgol Z, et al. Indoor and outdoor concentration of PM10, PM2.5 and PM1 in residential building and evaluation of negative air ions (NAIs) in indoor PM removal[J]. Environmental Pollutants and Bioavailability, 2020, 32(1): 47-55.
[26] 黄向华, 王健, 曾宏达, 等. 城市空气负离子浓度时空分布及其影响因素综述[J]. 应用生态学报, 2013, 24(6): 1761-1768.
  [Huang Xianghua, Wang Jian, Zeng Hongda, et al. Spatiotemporal distribution of negative air ion concentration in urban area and related affecting factors: A review[J]. Chinese Journal of Applied Ecology, 2013, 24(6): 1761-1768.]
[27] 王薇, 陈明. 城市绿地空气负离子和PM2.5及其与微气候关系——以合肥天鹅湖为例[J]. 生态环境学报, 2016, 25(9): 1499-1507.
  [Wang Wei, Chen Ming. Distribution characteristics of negative air ion and PM2.5 and their relationships with the microclimate in different urban greenlands: Case study of Hefei Swan Lake[J]. Ecology and Environment Science, 2016, 25(9): 1499-1507.]
[28] Peng J X, Wei Z H, Li X, et al. Towards control strategies of particulate matter concentration in subway platforms: A case study in Beijing[J]. Atmospheric Pollution Research, 2023, 14(4): 101702, doi: 10.1016/j.apr.2023.101702.
[29] 曹建新, 张宝贵, 张友杰. 海滨森林环境中空气负离子分布特征及其与环境因子的关系[J]. 生态环境学报, 2017, 26(8): 1375-1383.
  [Cao Jianxin, Zhang Baogui, Zhang Youjie. Characteristics of air anion distribution in beach and forest environment and the correlation between air anion and the environmental factors[J]. Ecology and Environmental Sciences, 2017, 26(8): 1375-1383.]
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