Environment and Geography Department, University of York, Environment Building, Heslington, York, North Yorkshire YO10 5NG, UK.
Philos Trans A Math Phys Eng Sci. 2020 Oct 30;378(2183):20190327. doi: 10.1098/rsta.2019.0327. Epub 2020 Sep 28.
The damage and injury that ground level ozone (O) causes vegetation has become increasingly evident over the past half century with a large body of observational and experimental evidence demonstrating a variety of effects at ambient concentrations on crop, forest and grassland species and ecosystems. This paper explores the use of experimental data to develop exposure-response relationships for use in risk assessment studies. These studies have typically identified the USA mid-West, much of Europe, the Indo Gangetic Plain in South Asia and the Eastern coastal region of China as global regions where O is likely to threaten food supply and other ecosystems. Global risk assessment modelling estimates yield losses of staple crops between 3 to 16% causing economic losses of between US$14 to 26 billion in the year 2000. Changes in anthropogenic emissions of O precursors in recent decades have modified O concentration profiles (peaks versus background O) and global distributions with the Northern Hemisphere seeing increases in O levels of between 1 and 5 ppb/decade since the 1950s and the emergence of Asia as the region with the highest O concentrations. In the future, O mitigation could focus on methane (CH) and nitrogen oxide (NOx) emissions; these will differentially influence global and local/regional O concentrations and influence daily and seasonal profiles. The consequent effects on vegetation will in part depend on how these changes in O profile alter the exceedance of detoxification thresholds for plant damage. Adaptation options may play an important role in enhancing food supply while mitigation strategies are being implemented. An improved understanding of the mechanisms by which O affects plants, and how this might influence detoxification thresholds and interactions with other environmental variables such as water stress and nutrients, would help develop O deposition and impact models to support the development of crop, land-surface exchange and ultimately earth system models for holistic assessments of global change. This article is part of a discussion meeting issue 'Air quality, past present and future'.
地面臭氧(O)对植被造成的损害和伤害在过去半个世纪中变得越来越明显,大量的观测和实验证据表明,在环境浓度下,臭氧对作物、森林和草原物种和生态系统有多种影响。本文探讨了利用实验数据来开发暴露-反应关系,用于风险评估研究。这些研究通常确定了美国中西部、欧洲大部分地区、南亚的印度恒河平原和中国东部沿海地区是全球臭氧可能威胁粮食供应和其他生态系统的地区。全球风险评估模型估计,主要作物的产量损失在 3%至 16%之间,在 2000 年造成了 140 亿至 260 亿美元的经济损失。近几十年来,人为排放的臭氧前体的变化改变了臭氧浓度分布(峰值与背景臭氧)和全球分布,自 20 世纪 50 年代以来,北半球的臭氧水平增加了 1 至 5 ppb/十年,亚洲成为臭氧浓度最高的地区。在未来,臭氧缓解可以集中在甲烷(CH)和氮氧化物(NOx)的排放上;这些将不同地影响全球和局部/区域的臭氧浓度,并影响日和季节分布。对植被的影响将在一定程度上取决于臭氧分布的变化如何改变植物毒害的解毒阈值的超标情况。在实施缓解策略的同时,适应选项可能在增强粮食供应方面发挥重要作用。更好地了解臭氧影响植物的机制,以及这如何影响解毒阈值,并与其他环境变量(如水胁迫和养分)相互作用,将有助于开发臭氧沉积和影响模型,以支持作物、陆地表面交换模型的发展,最终支持地球系统模型,从而对全球变化进行整体评估。本文是关于“空气质量,过去、现在和未来”的讨论会议的一部分。