绿-蓝-灰基础设施减少空气污染。

Prashant Kumar, Karina Corada, Sisay E Debele, Ana Paula Mendes Emygdio, K V Abhijith, Hala Hassan, Parya Broomandi, Richard Baldauf, Nerea Calvillo, Shi-Jie Cao, Sylvane Desrivières, Zhuangbo Feng, John Gallagher, Thomas Rodding Kjeldsen, Anwar Ali Khan, Mukesh Khare, Sri Harsha Kota, Baizhan Li, Shelagh K Malham, Aonghus McNabola, Anil Namdeo, Arvind Kumar Nema, Stefan Reis, S M Shiva Nagendra, Abhishek Tiwary, Sotiris Vardoulakis, Jannis Wenk, Fang Wang, Junqi Wang, Darren Woolf, Runming Yao, Laurence Jones
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引用次数: 0

摘要

绿蓝灰基础设施(GBGI)在城市地区提供了环境效益,但其对空气污染的影响尚未得到充分研究,相关文献也很零散。本综述评估了GBGI缓解空气污染能力的定量研究,比较了它们具体的污染物去除过程,并确定了进一步调查的领域。在评估的51个GBGI类型中,只有22个提供了定量的污染减少数据。行道树和混合GBGI是研究最多的GBGI,其效果受风、GBGI类型植被特征和城市形态的影响。负百分比表示空气质量恶化,而正百分比表示空气质量有所改善。22种不同的GBGI分为8大类,平均(±s.d)减少了16±21%的空气污染,其中线性特征(23±21%)、公园(22±34%)、建筑GI(14±25%)和其他非封闭城市地区(14±20%)的减少幅度较大。其他减少空气污染物的单独GBGI包括林地(21±38%)、树篱(14±25%)、绿墙(14±27%)、灌木(12±20%)、绿色屋顶(13±23%)、公园(9±36%)和混合GBGI(7±23%)。GBGI可使PM1、PM2.5、PM10、UFP和BC平均分别降低13±21%、1±25%、7±42%、27±27%和16±41%。GBGI还使气态污染物CO、O3和NOx平均分别降低10±21%、7±21%和12±36%。线性(如行道树和树篱)和构造(如绿墙)特征会根据建筑环境的配置和密度对当地空气质量产生积极或消极的影响。行道树通常在街道峡谷中表现出不利影响,在开阔道路条件下表现出有益效果。气候变化可能会加剧空气污染问题,并通过改变气候带影响GBGI的有效性。在欧洲和中国,气候变化预计将影响22个gbgi中的8个,其余地区预计将保持弹性。尽管GBGI具有改善空气质量的潜力,但荟萃分析强调了标准化报告结构的必要性,或者能够进行有意义的比较,并有效地将研究结果整合到城市污染和气候战略中。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Air pollution abatement from Green-Blue-Grey infrastructure.

Green-blue-grey infrastructure (GBGI) offers environmental benefits in urban areas, yet its impact on air pollution is under-researched, and the literature fragmented. This review evaluates quantitative studies on GBGI's capability to mitigate air pollution, compares their specific pollutant removal processes, and identifies areas for further investigation. Of the 51 GBGI types reviewed, only 22 provided quantitative pollution reduction data. Street trees and mixed-GBGI are the most studied GBGIs, with efficacy influenced by wind, GBGI type vegetation characteristics, and urban morphology. Negative percentages denote worsening air quality, while positive reflect improvement. The 22 different GBGI grouped into eight main categories provide an average (± s.d.) reduction in air pollution of 16 ± 21%, with substantial reduction shown by linear features (23 ± 21%), parks (22 ± 34%), constructed GI (14 ± 25%), and other non-sealed urban areas (14 ± 20%). Other individual GBGI reducing air pollutants include woodlands (21 ± 38%), hedges (14 ± 25%), green walls (14 ± 27%), shrubland (12 ± 20%), green roofs (13 ± 23%), parks (9±36%), and mixed-GBGI (7 ± 23 %). On average, GBGI reduced PM1, PM2.5, PM10, UFP and BC by 13 ± 21%, 1 ± 25%, 7 ± 42%, 27 ± 27%, and 16 ± 41%, respectively. GBGI also lowered gaseous pollutants CO, O3 and NOx by 10 ± 21%, 7 ± 21%, and 12 ± 36%, on average, respectively. Linear (e.g., street trees and hedges) and constructed (e.g., green walls) features can impact local air quality, positively or negatively, based on the configuration and density of the built environment. Street trees generally showed adverse effects in street canyons and beneficial outcomes in open-road conditions. Climate change could worsen air pollution problems and impact GBGI effectiveness by shifting climate zones. In Europe and China, climate shifts are anticipated to affect 8 of the 22 GBGIs, with the rest expected to remain resilient. Despite GBGI's potential to enhance air quality, the meta-analysis highlights the need for a standardised reporting structure or to enable meaningful comparisons and effectively integrate findings into urban pollution and climate strategies.

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