Ozone and other secondary photochemical pollutants: chemical processes governing their formation in the planetary boundary layer
Introduction
The emission of a variety of pollutant gases (e.g., nitrogen oxides, NOx, and volatile organic compounds, VOCs) into the troposphere may present a health risk either directly, or as a result of their oxidation. This can lead to a variety of secondary oxidised products, many of which are potentially more harmful than their precursors. Because much of the chemistry is driven by the presence of sunlight, the oxidised products are commonly referred to as secondary photochemical pollutants, and include photochemical oxidants such as ozone (O3). The production of elevated levels of O3 at ground level is of particular concern, since it is known to have adverse effects on human health, vegetation (e.g., crops) and materials (PORG, 1997). Established air quality standards for O3 are frequently exceeded, and the formulation of control policies is therefore a major objective of environmental policy (UNECE, 1992, UNECE, 1993, UNECE, 1994). Nevertheless, other pollutants that are formed on local or regional scales in the planetary boundary layer may also have direct health impacts (e.g. peroxy acetyl nitrate, PAN), and/or play wider roles in global atmospheric chemistry.
Photochemical air pollution, first identified in Los Angeles in the 1940s, is now a widespread phenomenon in many of the world's population centres (e.g., see NRC, 1991; PORG, 1997). Consequently, considerable attention has been given to identifying and quantifying chemical processes leading to the generation of O3 and other secondary photochemical pollutants in the planetary boundary layer. This has involved the laboratory study of many hundreds of chemical reactions, and a significant body of evaluated chemical kinetics and photochemical data has accumulated for elementary atmospheric reactions (e.g., Atkinson et al., 1997a, Atkinson et al., 1997b; DeMore et al., 1997). Computer models have provided a useful means of assembling these data, and of describing the likely behaviour and interconversion of various atmospheric pollutants, and such models play a central role in policy development and implementation. This work has been driven, of course, by the need to interpret the results of field studies of atmospheric chemical processes. In recent years, an enormous variety of observational data has become available for molecular and free radical species involved in atmospheric chemical processes in both polluted and clean environments.
The aim of this review is to provide a comparatively detailed description of our current understanding of the chemical mechanisms leading to the generation of secondary photochemical pollutants in the troposphere, with particular emphasis on chemical processes occurring in the planetary boundary layer. Much of the review is devoted to a discussion of the gas-phase photochemical transformations of nitrogen oxides and volatile organic compounds, and their role in the formation of O3. The chemistry producing a variety of other oxidants and secondary pollutants, which are often formed in conjunction with O3, is also described. Some discussion of nighttime chemistry and the formation and role of secondary organic aerosols (SOA) in tropospheric chemistry is also given, since these are closely linked to the gas-phase photochemical processes. Where possible, the relative importance of the various processes is discussed and illustrated by observational data, with emphasis generally placed on conditions appropriate to the UK and northwest continental Europe. Although some reference to heterogeneous reactions and aqueous uptake is made, multiphase chemical processes are not considered in detail, and the reader is referred to other texts (e.g., Jonson and Isaksen, 1993; Ravishankara, 1997) for further information on this important area of tropospheric chemistry.
Section snippets
Daytime interconversion of NO and NO2
Nitrogen oxides are released into the troposphere from a variety of biogenic and anthropogenic sources (Logan, 1983; IPCC, 1995; Lee et al., 1997). Approximately 40% of the global emissions, and the largest single source, results from the combustion of fossil fuels, which almost exclusively leads to emission directly into the planetary boundary layer, mainly in the form of NO. A small fraction (generally ⩽10%) may be released as NO2 (PORG, 1997), or is produced close to the point of emission
General description
It has been established for some decades (Haagen-Smit and Fox, 1954, Haagen-Smit and Fox, 1956; Leighton, 1961) that the formation of O3 in the troposphere is promoted by the presence of volatile organic compounds (VOCs), NOx and sunlight, and the mechanism by which this occurs is now well understood (e.g., Atkinson, 1990, Atkinson, 1994, Atkinson, 1998a, Atkinson, 1998b). The sunlight initiates the process by providing near ultra-violet radiation which dissociates certain stable molecules,
Nighttime chemistry
Although the major oxidation processes in the troposphere are initiated by the presence of sunlight, there are potentially significant chemical processes which can occur during the night. These processes cannot generate O3 (indeed, they lead to O3 removal), but potentially do produce a series of secondary pollutants, including H2O2. The chemistry also oxidises NOx and VOCs which, as described above, are precursors to the formation of O3 and other secondary photochemical pollutants during
Chemical processes leading to secondary organic aerosol (SOA) formation
The formation of aerosols in the atmosphere has an important influence on visibility, climate and chemical processes, and is of concern since fine particulate matter is inhalable. The reduction of visibility observed in power station plumes and during photochemical episodes is mainly due to the formation and growth of large numbers of particles or droplets, which are able to absorb and scatter radiation. Similarly, the scattering and absorption of incoming solar radiation by aerosols throughout
Conclusions
Considerable progress has been made in identifying chemical processes responsible for the generation of O3 and other secondary photochemical pollutants in the planetary boundary layer. This has been achieved by a combination of field observations, laboratory investigations and numerical modelling studies. However, further research in all three areas is necessary to improve our quantitative understanding of the impact of the chemical processing of pollutants emitted into the atmosphere.
The
Acknowledgements
MEJ gratefully acknowledges the support of the Department of the Environment, Transport and the Regions, both in the preparation of this review (under contract EPG 1/3/70), and for the some of the work described. KCC gratefully acknowledges financial support from the European Union (under contract ENV4-CT97-0404). Thanks are also due to members of the Photochemical Oxidants Review Group (PORG), in particular Tony Cox (University of Cambridge) and Dick Derwent (UK Meteorological Office) for
References (224)
- et al.
A DOAS study on the origin of nitrous acid at urban and non-urban sites
Atmospheric Environment
(1996) Gas-phase tropospheric chemistry of organic compounds: a review
Atmospheric Environment
(1990)- et al.
A winter NO2 smog episode in the UK
Atmospheric Environment
(1994) - et al.
Rate constants for the reaction OH+NO2+M→HNO3+M under atmospheric conditions
Chemical Physics Letters
(1999) - et al.
Gas-phase terpene oxidation products: a review
Atmospheric Environment
(1999) - et al.
Peroxy radical chemistry during FIELDVOC 1993 in Brittany
France. Atmospheric Environment
(1996) - et al.
Investigation and evaluation of the O3/NOx photochemical stationary state
Atmospheric Environment
(1998) Computer modelling of environmental chamber measurements of maximum incremental reactivities of volatile organic compounds
Atmospheric Environment
(1995)- et al.
Environmental chamber study of maximum incremental reactivities of organic compounds
Atmospheric Environment
(1995) - et al.
Cis-pinic acid, a possible precursor fron organic aerosol formation from ozonolysis of α-pinene
Atmospheric Environment
(1998)