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Air Pollution and Turbulence: Modeling and Applications
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Mô tả chi tiết
Air Pollution
and Turbulence
Modeling and Applications
© 2010 by Taylor and Francis Group, LLC
Air Pollution
and Turbulence
Modeling and Applications
Edited by
Davidson Moreira and
Marco Vilhena
CRC Press is an imprint of the
Taylor & Francis Group, an informa business
Boca Raton London New York
© 2010 by Taylor and Francis Group, LLC
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CRC Press
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© 2010 by Taylor and Francis Group, LLC
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Library of Congress Cataloging-in-Publication Data
Air pollution and turbulence : modeling and applications / edited by Davidson Moreira
and Marco Vilhena.
p. cm.
“A CRC title.”
Includes bibliographical references and index.
ISBN 978-1-4398-1144-3 (alk. paper)
1. Air--Pollution--Simulation methods. 2. Atmospheric turbulence--Simulation
methods. I. Moreira, Davidson. II. Vilhena, Marco.
TD890.A364 2010
628.5’3011--dc22 2009039105
Visit the Taylor & Francis Web site at
http://www.taylorandfrancis.com
and the CRC Press Web site at
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Dedication
We thank God for the opportunity given to mankind to uncover
the beauty and mystery of the masterpiece of creation: Nature.
To my daughter, Evelyn In memoriam to my father, Paulo
To my wife, Márcia To my mother, Ieda
I give my gratitude for
her loving patience
To my sister, Tânia
To my wife, Sônia
and support during this With all my love and gratitude,
episode of my life,
Davidson Martins Moreira Marco Túllio M. B. de Vilhena
© 2010 by Taylor and Francis Group, LLC
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vii
Contents
Foreword ...................................................................................................................ix
Preface....................................................................................................................xvii
Editors .....................................................................................................................xix
Contributors ............................................................................................................xxi
Chapter 1 Deposition, Transformation, and Remobilization of Soot and
Diesel Particulates on Building Surfaces .............................................1
Peter Brimblecombe and Carlota M. Grossi
Chapter 2 Atmospheric Boundary Layer: Concepts and Measurements ............ 15
Gilberto Fisch
Chapter 3 Turbulence and Dispersion of Contaminants in the Planetary
Boundary Layer .................................................................................. 33
Gervásio Annes Degrazia, Antonio Gledson Oliveira Goulart,
and Debora Regina Roberti
Chapter 4 Parameterization of Convective Boundary Layer Turbulence
and Clouds in Atmospheric Models ...................................................69
Pedro M. M. Soares, João Teixeira, and Pedro M. A. Miranda
Chapter 5 Mathematical Air Pollution Models: Eulerian Models .................... 131
Tiziano Tirabassi
Chapter 6 Analytical Models for the Dispersion of Pollutants in
Low Wind Conditions ...................................................................... 157
Pramod Kumar and Maithili Sharan
Chapter 7 On the GILTT Formulation for Pollutant Dispersion Simulation
in the Atmospheric Boundary Layer ................................................ 179
Davidson Martins Moreira, Marco Túllio M. B. de
Vilhena, and Daniela Buske
Chapter 8 An Outline of Lagrangian Stochastic Dispersion Models ...............203
Domenico Anfossi and Silvia Trini Castelli
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viii Contents
Chapter 9 Atmospheric Dispersion with a Large-Eddy Simulation:
Eulerian and Lagrangian Perspectives ............................................. 237
Umberto Rizza, Giulia Gioia, Guglielmo Lacorata,
Cristina Mangia, and Gian Paolo Marra
Chapter 10 Photochemical Air Pollution Modeling: Toward Better Air
Quality Management ........................................................................269
Carlos Borrego, Ana Isabel Miranda, and Joana Ferreira
Chapter 11 Inversion of Atmospheric CO2 Concentrations ................................287
Ian G. Enting
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ix
Foreword
Air pollution is inherently linked to human activities and was already mentioned as a
nuisance in antic Roman texts and in the middle ages. The industrial revolution in the
nineteenth century worsened its effects and increasingly turned it to a nonlocal problem. Parallel developments in physical sciences provided new tools to address this
problem. Understanding the rate and patterns of atmospheric dispersion is crucial for
environmental planning (location of industrial plants) and for forecasting high pollution episodes (above legislation thresholds inducing detrimental effects on human
health, ecosystems, and/or materials). Last but not least, local emissions are transported by air motions to create regional environmental problems, and, fi nally, the
accumulation of pollutants in the global atmosphere yield and interfere with climate
change processes. Consequently, there is a strong need for developing ever-better
models and assessment tools for air pollution concentration, dispersion, and effects.
These tools can span from simple analytical models for monitoring and predicting
short-range effects to regional or global three-dimensional models assimilating a
wide range of physical and chemical in situ and satellite observations. The breadth of
the different mathematical, physical, chemical, and biological processes and issues
has generated a lot of basic and applied research that should also take into account
the needs of environmental managers, physicians, and also of process engineers and
lawyers. No book can tackle all these issues in a balanced way; therefore, this book
mainly addresses issues of atmospheric dispersion modelling and their effects on
building surfaces.
To assess spatial and temporal distributions of pollutants and chemical species in
the air and their deposition on the Earth’s surface, atmospheric dispersion and chemical transport models are used at different scales, addressing different applications
from emergency preparedness, ecotoxicology, and air pollution effects on human
health to global atmospheric chemical composition and climate change. During the
last two decades, several basic aspects of air pollution modeling have been substantially developed, thanks to advances in computer technologies and numerical mathematics, as well as in the physics of atmospheric turbulence and the atmospheric
boundary layer (ABL).
Most air quality modeling systems consist of a meteorological model coupled
offl ine or online to emission and air pollution models, and, sometimes, also to a
population-exposure model. The meteorological model calculates three-dimensional
fi elds of wind, temperature, relative humidity, pressure, and, in some cases, turbulent diffusivity, clouds, and precipitation. The emissions model estimates the amount
and chemical composition of primary pollutants based on process information (e.g.,
traffi c intensity) and day-specifi c meteorology (e.g., temperature for biogenic emissions). The outputs of these emission and meteorological models are then inputs to
the air pollution model, which calculates concentrations and deposition rates of gases
and aerosols as a function of space and time. There are various mathematical
models that can be used to simulate meteorology and air pollution in a mesoscale
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x Foreword
domain (San Jose et al., 2008). Although models differ in their treatment of different
mechanisms and feedbacks, they all employ a similar framework and consist of the
same major modules:
• Transport and diffusion—calculating three-dimensional motion of gases
and aerosols in a gridded model domain
• Gas-phase chemistry—calculating changes in gaseous concentrations due
to chemical transformations
• Aerosol—calculating size distribution and chemical composition of aerosols accounting for chemical and physical transformations
• Cloud/fog meteorology—calculating physical characteristics of clouds
and fog based on the information from the meteorological model (or from
observations)
• Cloud/fog chemistry—calculating changes in chemical concentrations in
clouds/fog water
• Wet deposition—calculating the rates of deposition due to precipitation
(and, possibly, cloud impaction and fog settling) and the corresponding
changes in chemical concentrations
• Dry deposition—calculating the rates of dry deposition for gases and
aerosols and the corresponding changes in their concentrations
Consequently, the quality of the air pollution forecasts using such systems critically
depends on the adequacy in mapping emissions, representing meteorological fi elds,
and modeling the transport, dispersion, and transformation of chemicals/pollutants.
Various scientifi c developments now allow models to reasonably predict simple fl ow
situations within a factor of 2 or so.
What is more challenging is to predict episodes of high pollutant concentrations,
which may cause dramatic impacts on human health. Such situations, moreover, are
often induced by special situations, such as complex terrains, low winds, and very
stable stratifi cation causing shallow ABLs with low level of turbulent mixing. These
situations create problems for current methods and models to realistically reproduce
meteorological input fi elds.
The key physical mechanisms controlling concentrations of pollutants in the
atmosphere are advection, turbulent diffusion, wet and dry deposition, and gravitational settling. Their representation requires 3D fi elds of the wind velocity and direction, static stability (lapse rate), the ABL height (often called “mixing height”), basic
characteristics of turbulence (eddy diffusivities and velocity variances across the
atmosphere, and turbulent fl uxes of momentum, buoyancy, and scalars at the surface
and at the ABL outer boundary), and precipitation. Additionally, boundary conditions described by the basic physical and geometric characteristics of the surface (in
particular, the roughness lengths for momentum and scalars, and the displacement
heights) are very critical.
Most of the emissions are situated and most of the pollutants are dispersed within
the ABL, whose upper boundary (the layer at which the intensity of turbulence
strongly drops down) serves as a kind of a semi-impervious lid. Hence the mechanisms controlling concentrations strongly depend on the ABL turbulence, and, fi rst
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Foreword xi
of all, on the ABL height. The temporal and spatial variations in the ABL height
and the entrainment processes at the ABL upper boundary lead to the penetration of
pollutants from the ABL to the free troposphere, and, vice versa, to the intrusion of
some chemical compounds (e.g., ozone) from the upper atmospheric layers down to
the surface. Physical processes controlling the ABL height and the turbulent entrainment (e.g., Zilitinkevich, 1991; Zilitinkevich et al., 2007a; and references therein)
are, therefore, of crucial importance for the air-pollution applications.
Furthermore, some physical processes at the ABL upper boundary, crucially
important for air pollution modelling, are still insuffi ciently understood, e.g., turbulent entrainment in rapidly deepening convective ABLs and nonsteady interactions
between the stable ABLs and the free fl ow. The latter are comparatively simple at
mid-latitudes where nocturnal stable ABLs develop on the background of almost
neutrally stratifi ed residual layers, whereas at high latitudes, long-lived stable ABLs
develop against very stable stratifi cation typical of the free troposphere, yielding
the formation of strong capping inversions and making the theory much more
complicated (e.g., Zilitinkevich and Esau, 2007).
For short-range dispersion of simple cases or targeted plumes, one classical modeling
approach is based on using the so-called statistical technique or the eddy diffusivity
concept. Several chapters in this book address new developments with these techniques. Therefore, new developments in turbulence theory and ABLs will have a direct
impact on these techniques as well. For instance, one typical long-lasting issue has
been the turbulence closure for very stable stratifi cation (including the turbulent diffusion formulations), whereby the energetics of turbulence is modeled using solely the
turbulent kinetic energy budget equation, leading to a cut off in turbulence at “supercritical” stratifi cation, though observations showed the presence of turbulence in typical atmospheric and oceanic sheared fl ows. The problem was treated heuristically by
prescribing a “minimal diffusivity”—just to avoid the total decay of turbulence. New
insight might come from recent work based on the concept of total turbulent energy and
applicable to “supercritical” fl ows with no cut off (Mauritsen et al., 2007; Zilitinkevich
et al., 2007b; Canuto et al., 2008). Another area of potential development is the generalization of the Monin–Obukhov similarity theory, taking into account the nonlocal
effect of free-fl ow stability on stably stratifi ed ABLs and also nonlocal mixing due to
large-scale, organized eddies in the shear-free convection (Zilitinkevich et al., 2006;
Zilitinkevich and Esau, 2007). Further work is also needed to extend the ABL theory
to the sheared convection and to ABLs over complex and sloping terrains.
During the last decade, meso-scale modeling of pollution dispersion and air
quality employing the integrated modelling approach together with advances in ABL
physics reported above have been developed in both research and operational modes
(see an overview of European models in COST-WMO, 2007).
Short-term pollution episodes occurring during adverse meteorological conditions and causing strong short-term exceedances of air quality standards in ambient
air are presently one of the major concerns for the protection of human health, ecosystems, and building materials, especially in cities. Reliable urban-scale forecasts
of meteorological fi elds are, therefore, of primary importance for urban emergency
management systems, addressing accidental or terrorist releases, and fi res, of chemical, radioactive, or biological substances.
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xii Foreword
The urban environment presents challenges to atmospheric scientists—
theoreticians, experimentalists, and modellers—because of very high roughness
elements penetrating deeply into the ABL (thus requiring the revision of such classical concepts as the surface layer, roughness length, and displacement height; see
Zilitinkevich et al., 2008), the heterogeneous distribution of surface features, and the
strong spatial and temporal variabilities of surface fl uxes of heat, moisture, momentum, and pollutants. Additionally, the structure of the conurbation may enhance vertical motions, changing the residence times of atmospheric compounds (Hidalgo
et al., 2008) and triggering local meteorological circulations (e.g., caused by “heat
islands”), and the production of condensation nuclei, thus affecting cloud formation,
precipitation patterns, and the radiation balance. The increased relevance of urban
meteorology is refl ected in the number of experimental campaigns performed in
urban areas in Europe and America during the last decade, e.g., BUBBLE (Rotach
et al., 2005), ESCOMPTE (Mestayer et al., 2005), CAPITOUL (Masson et al., 2009),
and MILAGRO (Molina et al., 2007).
The incorporation of urban effects into air pollution models is generally carried out through the “urbanization” of meso-meteorological or numerical weather
prediction (NWP) models (which act as driver models), or using special urban
meteo-pre-processors to improve non-urbanized NWP input data (COST-715,
2005).
The persistently increasing resolution in NWP models allows to reproduce more
realistically urban air fl ows and air pollution, and triggers interest in further experimental and theoretical studies in urban meteorology. Recent works performed by a
consortium of an European project, EMS-FUMAPEX 2005, on integrated systems
for forecasting urban meteorology and air pollution, and by the U.S. EPA and NCAR
communities employing the models MM5 (Dupont et al., 2004; Taha, 2008) and
WRF (Chen et al., 2006), as well as other relevant works (see COST-728, 2009),
have disclosed many options for the urbanization of NWP and meso-meteorological
models.
It goes without saying that no single book could cover the entire range of problems listed above. The scope of this book does not intend such a grand task. It rather
refl ects and summarizes some recent developments relevant to the key issues in modeling atmospheric turbulence and air pollution. Chapter 1 deals with the modelling
of deposition, transformation and remobilization of soot and diesel particulates on
building surfaces, damage to facades and decoration by air pollution, and the human
health aspect of air pollution (Brimblecombe and Grossi, 2005). Chapter 2 describes
observational studies of convective ABLs over pastures and forests in Amazonia
(Fisch et al., 2004). Chapter 3 discusses the theoretical studies of turbulence and
turbulent diffusion in convective ABLs (Degrazia and Anfossi, 1998; Goulart
et al., 2003). Chapter 4 describes the parameterization of convective turbulence and
clouds in atmospheric models based on the combination of the eddy-diffusivity and
mass-fl ux approaches (Soares et al., 2004; Siebesma et al., 2006). Chapter 5 contains a general discussion of analytical solutions to the advection-diffusion equations (Tirabassi, 1989, 2003). Chapter 6 describes analytical models for air pollution
including those for low wind conditions (Sharan et al., 1996; Sharan and Modani,
2005). Chapter 7 deals with the analytical solutions to the advection-diffusion equations using the generalized integral Laplace transform technique (GILTT) and the
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Foreword xiii
decomposition method (Moreira et al., 2005, 2006, 2009). Chapter 8 describes the
Lagrangian stochastic dispersion models with applications for airborne dispersion in
the ABL (Anfossi et al., 1997, 2006). Chapter 9 deals with the large eddy simulation
(LES) of dispersion within ABLs using the Lagrangian and the Eulerian approaches
(Rizza et al., 2003, 2006). Chapter 10 describes the modelling of photochemical air
pollution for better air quality management (Borrego et al., 2000; Monteiro et al.,
2005). Finally, Chapter 11 describes the analysis of the transport of a trace gas (CO2)
at the global scale and overviews the inverse-problem techniques for deducing emissions from known concentrations (Enting, 2002, 2008).
The book is of interest for the entire boundary-layer meteorology and atmospheric
turbulence communities, including both students and researchers, especially those
interested in the nature, theory, and modeling of air pollution. For a deeper acquaintance with these fi elds, we recommend the following monographs and collections of
papers on boundary-layer meteorology: Sorbjan (1989), Zilitinkevich (1991), Garratt
(1992), Kraus and Businger (1994), Holtslag and Duynkerke (1998), Kantha and Clyson
(2000), Baklanov and Grisogono (2007); turbulent diffusion: (Pasquill and Smith,
1983; Arya, 1999); and air pollution (Seinfeld and Pandis, 2006; Jacobson, 2005).
A. A. Baklanov
S. M. Joffre
S. S. Zilitinkevich
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