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Atmospheric Multiphase Chemistry
Atmospheric Multiphase Chemistry
Hajime Akimoto
National Institute for Environmental Studies
Tsukuba, Japan
Jun Hirokawa
Hokkaido University
Sapporo, Japan
This edition first published 2020
© 2020 John Wiley & Sons Ltd
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10 9 8 7 6 5 4 3 2 1
v
Contents
Preface xiii
Index 509
xiii
Preface
Reaction kinetics and mechanism are a significant part of the fundamentals of atmo-
spheric chemistry. The chemical reaction system in the atmosphere is composed of
homogeneous reactions in the gas and liquid phases and heterogeneous processes
involving particle surfaces. Among them, the study of gas-phase homogeneous reaction
system in the atmosphere has evolved since the Chapman theory in the 1930s to
explain the stratospheric ozone layer, and developed dramatically after 1970s with
photochemical air pollution as a trigger. It is now almost established and summarized
in many bibliographies, including a book by one of present authors (H.A.) discussed in
Chapter 3.
In contrast, although the heterogeneous reaction system in the atmosphere has
developed substantially with acid rain and stratospheric ozone hole as turning points,
the studies have long been confined mainly to inorganic species. The research field of
aerosols and heterogeneous kinetics has undergone dramatic changes since the 2000s,
when the importance of secondary organic aerosols as cloud condensation nuclei was
pointed out. Also, secondary organic aerosols have been recognized as important as
inorganic sulfate and nitrate as a constituent of PM2.5 , which is concerned from the
point of human health.
The formation mechanism of secondary organic aerosols involves condensation
of reaction products of homogeneous gas-phase reactions, uptake of the gas-phase
products onto the particle surface, complex formation and reaction at the interface,
homogeneous aqueous-phase reaction, and evaporation from a particle to the gas
phase. We call series of these processes multiphase reaction chemistry.
This book intends to serve as a reference book on fundamentals of atmospheric mul-
tiphase chemistry. Gas- and aqueous-phase reactions, heterogeneous oxidation pro-
cesses, and air–water interface and solid particle surface reactions related to secondary
organic aerosol formation are first described. After that, new particle formation, cloud
condensation nucleus activity, and field observation of organic aerosols are discussed.
The book can serve as a comprehensive reference for graduate students and profession-
als who are interested in homogeneous and heterogeneous atmospheric reactions of
organic species related to aerosols.
xiv Preface
1.1 Introduction
Trace components in the tropospheric atmosphere consist of gaseous molecules and
particulate matters. Most of gaseous molecules in the atmosphere do not have absorp-
tion bands in the visible region. Some species such as ozone and nitrogen dioxide have
the absorption, but they are invisible to the naked eye under the normal atmospheric
conditions because their absorbance are small. In contrast, since the particulate mat-
ters intercept sunlight and small particles scatter strongly the solar radiation, they are
captured easily by the naked eye as haze. Thus, particulate matters in the atmosphere
called atmospheric aerosols have been studied from relatively early days in relation to
air pollution historically.
These atmospheric aerosols are divided broadly into the primary species released
directly from emission sources and the secondary compounds formed by chemical
reactions in the atmosphere. Further, secondary particulate matter can be classified
into secondary inorganic aerosol and secondary organic aerosol (SOA).
This book aims at the understanding of chemical reactions forming secondary aerosols
in the gas phase, in the liquid phase, and at their interface, particularly focusing on
organic aerosols. Therefore, most of the descriptions are focused on organic species, and
inorganic species are addressed whenever necessary. As for the formation of secondary
inorganic aerosols, detailed discussion has been given by the textbook of Seinfeld and
Pandis (2016).
In this chapter, historical background of research on atmospheric secondary aerosols,
including inorganic aerosols, is described looking back before 1980s, when the atmo-
spheric chemistry was founded as one of the academic fields of the global environmental
sciences.
nineteenth century when Liebig (1835) advocated a theory that atmospheric nitrogen
compounds deposited on ground are essential to plant growth as nutrient salt absorbed
by roots, leading to a revolution of agricultural chemistry. Thus, atmospheric nitrate,
the main component of the plant nutrient, had been discovered from long ago as a
precipitation constituent (Miller 1905; Eriksson 1952a; Möller 2008). On the other
hand, the discovery of sulphate was delayed nearly 100 years after that of nitrate. From
the view point of air pollution in Manchester, UK, Smith (1852) described based on
the analysis of precipitation that three kinds of air can be found: (i) with carbonate of
ammonia in the remote field; (ii) with sulphate of ammonia in the suburbs; and (iii) with
sulfuric acid in the urban area (Cowling 1982). The described ammonium carbonate
((NH4 )2 CO3 ), ammonium sulfate ((NH4 )2 SO4 ), and sulfuric acid (H2 SO4 ) are formed
secondarily by the chemical reactions in the gas phase or in the fog water from atmo-
spheric trace gaseous species, CO2 , NH3 , and SO2 . These aerosols are water-soluble,
and recognized as major components of “acid rain” after taken into precipitation.
Incidentally, the term of acid rain was used for the first time in the monograph of Smith
(1872) as accredited by Cowling (1982). Since then, the measurement of nitrate and
ammonium had been made in many places in Europe in the latter half of nineteenth
century from the interest of agricultural chemistry, while sulfate had been measured in
the eastern part of United States since the 1910s (Cowling 1982).
Hydrogen ion concentration (pH) has been measured since the 1950s, started in
Europe and United States, over a wide area. Owing to these wide-area observations,
spatial distribution and temporal trends of pH and chemical components of precip-
itation became to be known well in Europe (Emanuelsson et al. 1954; Barrett and
Brodin 1955; Odén 1976) and North America (Junge and Werby 1958; Gorham and
Gordon 1960; Cogbill 1976). The acid rain causing acidification of lakes and rivers
and their impact on fishery was then brought up as a social problem internationally.
The quantitative research on the formation of sulfate and nitrate as secondary inorganic
aerosol had been developed rapidly as “acid rain” became social concern.
1.2.1 Sulfate
In the earlier studies on acid rain, it was thought that sulfur dioxide (SO2 ), primary air
pollutants whose atmospheric concentration had increased rapidly after the Industrial
Revolution, was taken up into fog water droplets and converted to sulfate by oxidation
in the aqueous phase (Junge and Ryan 1958; Junge 1963):
H2 O O2 NH4 +
SO2 −−−−→ SO3 2− −−−−n+−→ SO4 2− −−−−−→ (NH4 )2 SO4 (1.1)
M
The rate limiting stage of this process is the oxidation step of SO3 2− to SO4 2− , and the
oxidation by O2 had been studied for a long time (Fudakowski 1873; Backstrom 1934).
However, the oxidation rate of SO3 2− by O2 was found to be very slow (Fuller and Crist
1941; Brimblecombe and Spedding 1974). Therefore, this reaction is not important for
O2 alone as the oxidation reaction of SO2 in the atmosphere, but it was found that the
reaction is accelerated by the coexistence of trace metal ions such as Fe3+ , Cu2+ , and
Mn2+ (Reinders and Vles 1925; Junge and Ryan 1958; Brimblecombe and Spedding 1974;
Hegg and Hobbs 1978). The effects of transition metal ions on the SO2 oxidation in the
aqueous phase still leaves a lot of unknowns, and the studies are ongoing (Deguillaume
et al. 2005; Harris et al. 2013; Herrmann et al. 2015).
1.2 Secondary Inorganic Aerosols 3
1.2.2 Nitrate
The measurement of nitrate (NO3 − ) in precipitation has been reported in United
States early in 1920s from the interest in agricultural chemistry (Wilson 1926). Its
atmospheric concentrations increased rapidly, accompanying with the rapid increase
of fossil fuel combustion. It has been monitored since the 1950s as an important
secondary inorganic aerosol next to SO4 2− (Junge 1954; Lee and Patterson 1969). For
example, the equivalent-basis fractions of SO4 2− and NO3 − in precipitation in Eastern
United States in early 1960s are reported as ca. 60% and ca. 20%, respectively (Likens
and Bormann 1974). Particularly, large amounts of nitrates were reported, together
with sulfate and organic aerosols existing in photochemical smog mentioned in the
next section (Renzetti and Doyle 1959; Lundgren 1970; Appel et al. 1978).
Since the rate constant of the reaction:
OH + NO2 + M → HNO3 + M, (1.6)
4 1 Historical Background of Atmospheric Secondary Aerosol Research
is one order of magnitude larger than the reaction, OH + SO2 + M, under the atmo-
spheric conditions, and the Henry’s law constant of NO2 is two orders of magnitude
smaller than SO2 (Table 2.2), nitric acid (HNO3 ) in the atmosphere is thought to be
formed in the gas phase and then taken into the aqueous phase (Orel and Seinfeld 1977).
Meanwhile, a formation pathway other than (1.6) is considered to be the hydrolysis of
N2 O5 formed via NO3 by the reaction of O3 and NO2 (Orel and Seinfeld 1977):
NO2 + O3 → NO3 + O2 (1.7)
NO2 + NO3 + M → N2 O5 + M (1.8)
N2 O5 + H2 O → 2 HNO3 (1.9)
The rate constant of Reaction (1.9) in the gas phase as a homogeneous reaction is
very small, <2.0 × 10−21 cm3 molecule−1 s−1 (Burkholder et al. 2015), and the heteroge-
neous reaction on the particle surface is thought to be more important (Mozurkewich
and Calvert 1988). The NO3 radical involved in this reaction process has absorption
bands in the visible region and photolysed easily by sunlight, so that the formation of
HNO3 by this heterogeneous reaction process is thought to be important in the night-
time (Richards 1983; Heikes and Thompson 1983).
The gaseous nitric acid, ammonia, and ammonium nitrate formed from them are
thought to be in equilibrium:
NH3 (g) + HNO3 (g) ⇆ NH4 NO3 (s), (1.10)
and comparison between model estimate based on the thermodynamic parameters
(Stelson et al. 1979) and field observation for the formation of nitrate have been made
(Harrison and Pio 1983; Hildemann et al. 1984). Reaction (1.10) is reversible reaction,
and the particulate NH4 NO3 increases with the decrease of temperature, and thus the
concentration ratio of nitrate is known to increase in winter and at dawn. Multiphase
models that treat sulfuric and nitric acid simultaneously have been developed in 1980s
(Bassett and Seinfeld 1983; Saxena et al. 1983).
Gaseous HNO3 reacts with sea salt (NaCl) on the surface to give sodium nitrate by
releasing HCl:
NaCl(s) + HNO3 (g) → NaNO3 (s) + HCl(g). (1.11)
Although it has been presumed that the reaction causes the decrease of chlorine to
sodium ratio in the sea salt in the vicinity of continents and brings the nitrate in coarse
particles (Robbins et al. 1959), the reaction has been validated by laboratory experiments
only after the latter half of 1990s (De Haan and Finlayson-Pitts 1997; Wahner et al. 1998).
Thus, nitrates have the characteristics that they exist as NH4 NO3 in submicron parti-
cles in the inland and as NaNO3 in coarse particles (2–8 μm) in the coastal urban area
(Lee and Patterson 1969; Cronn et al. 1977).
However, the trigger to wide concern on the particulate organic compounds was the
discovery of carcinogenic polyaromatic hydrocarbons (PAHs) in the diesel exhaust and
urban atmosphere in the middle of twentieth century (e.g. Waller 1952; Kotin et al. 1954;
Stocks and Campbell 1955; Wynder and Hoffmann 1965). Further findings of many oxy-
genated compounds in the atmospheric aerosols were made in the photochemical smog.
showed that alcohols, carboxylic acids, and carbonyl compounds are included in the
aerosols by use of infrared absorption spectroscopy and mass spectrometry (Cukor
et al. 1972; Ciaccio et al. 1974; Cronn et al. 1977). Also, it was revealed that atmospheric
carbonaceous aerosol sampled in California consisted of elemental carbon (EC) and
organic carbon (OC) (Appel, Colodny and Wesolowski 1976).
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13
2.1 Introduction
Chemical reaction systems in the atmosphere are composed of homogeneous reactions
in the gas phase, homogeneous liquid-phase reactions in deliquescent aerosol particles
and water droplets, and heterogeneous reactions at the particle surface. Among them,
physicochemical fundamentals of photochemistry and kinetics in the homogenous gas
phase reactions have already been well established in principle, and detailed explana-
tion has been given in a previous book by one of the present authors (Akimoto 2016)
and many textbooks introduced therein. In contrast, many aspects of atmospheric mul-
tiphase chemical reactions, including uptake of chemical species from gas phase to par-
ticle surface, heterogeneous reactions at the surface, and homogeneous aqueous phase
reactions, have not yet been well established. In this chapter, fundamentals of physi-
cal chemistry relevant to the formation and transformation of atmospheric aerosols are
described. The values of physical constants appearing in this book and the conversion
factors of energy units between kJ, kcal, and eV are given in Tables 2.1 and 2.2.
In this chapter, fundamentals of optical properties, such as scattering of light and
photoabsorption by atmospheric fine particles, and the photochemistry related to the
photolysis at the surface of fine particles are not covered. The former topics are covered
by the textbook by Mishchenko et al. (2002) and Kokhanovsky (2008), but the system-
atic research on the latter topic has not been developed well and is still open to future
research.
Author: Iamblichus
Contributor: Porphyry
Language: English
ON
The Mysteries
OF THE
ASSYRIANS.
BY
THOMAS TAYLOR.
Second Edition.
LONDON:
BERTRAM DOBELL,
77 CHARING CROSS ROAD, W.C.
AND
REEVES AND TURNER,
5 WELLINGTON STREET, STRAND.
MDCCCXCV.
ADVERTISEMENT.
May, 1895.
INTRODUCTION.
But if we assert with certain persons, that the Gods are pure
intellects, but that dæmons, being psychical, participate of intellect;
in a still greater degree will pure intellects be incapable of being
allured, and will be unmingled with sensible natures. Supplications,
however, are foreign to the purity of intellect, and therefore are not
to be made to it. But the things which are offered [in sacred rites] are
offered as to sensitive and psychical essences.
Are, therefore, the Gods separated from dæmons, through the
former being incorporeal, but the latter corporeal? If, however, the
Gods are incorporeal alone, how will the sun and moon, and the
visible celestials, be Gods?
How, likewise, are some of the Gods beneficent, but others
malefic?
What is it that connects the Gods in the heavens that have bodies,
with the incorporeal Gods?
What is it that distinguishes dæmons from the visible and invisible
Gods, since the visible are connected with the invisible Gods?
In what do a dæmon, hero, and soul, differ from each other? Is it
in essence, or in power, or in energy?
What is the indication of a God, or angel, or archangel, or dæmon,
or a certain archon, or soul being present? For to speak boastingly,
and to exhibit a phantasm of a certain quality, is common to Gods
and dæmons, and to all the more excellent genera. So that the genus
of Gods will in no respect be better than that of dæmons.
Since the ignorance of, and deception about, divine natures is
impiety and impurity, but a scientific knowledge of the Gods is holy
and beneficial, the ignorance of things honourable and beautiful will
be darkness, but the knowledge of them will be light. And the former,
indeed, will fill men with all evils, through the want of erudition, and
through audacity; but the latter will be the cause to them of every
good. [I wish you, therefore, to unfold to me the truth respecting
these particulars.[18]]
[And, in the first place, I wish you to explain to me distinctly[19]]
what that is which is effected in divination? For we frequently obtain
a knowledge of future events through dreams, when we are asleep;
not being, at that time, in a tumultuous ecstasy, for the body is then
quiescent; but we do not apprehend what then takes place, in the
same manner as when we are awake.
But many, through enthusiasm and divine inspiration, predict
future events, and are then in so wakeful a state, as even to energize
according to sense, and yet they are not conscious of the state they
are in, or at least, not so much as they were before.
Some also of those who suffer a mental alienation, energize
enthusiastically on hearing cymbals or drums, or a certain
modulated sound, such as those who are Corybantically inspired,
those who are possessed by Sabazius, and those who are inspired by
the mother of the Gods. But some energize enthusiastically by
drinking water, as the priest of Clarius, in Colophon; others, by being
seated at the mouth of a cavern, as those who prophesy at Delphi;
and others by imbibing the vapour from water, as the prophetesses
in Branchidæ. Some also become enthusiastic by standing on
characters, as those that are filled from the intromission of spirits.
Others, who are conscious what they are doing in other respects, are
divinely inspired according to the phantastic part; some, indeed,
receiving darkness for a cooperator, others certain potions, but
others incantations and compositions: and some energize, according
to the imagination, through water; others in a wall, others in the
open air, and others in the sun, or in some other of the celestial
bodies. Some also establish the art of the investigation of futurity
through the viscera, through birds, and through the stars.
I likewise ask concerning the mode of divination, what it is, and
what the quality by which it is distinguished? All diviners, indeed,
assert, that they obtain a foreknowledge of future events through
Gods or dæmons, and that it is not possible for any others to know
that which is future, than those who are the lords of futurity. I doubt,
therefore, whether divinity is so far subservient to men, as not to be
averse to some becoming diviners from meal.
But, concerning the causes of divination, it is dubious whether a
God, an angel, or a dæmon, or some other power, is present in
manifestations, or divinations, or certain other sacred energies, as is
the case with those powers that are drawn down through you
[priests] by the necessities with which invocation is attended.
Or does the soul assert and imagine these things, and are they, as
some think, the passions of the soul, excited from small incentives?
Or is a certain mixed form of subsistence produced from our soul,
and divine inspiration externally derived?
Hence it must be said, that the soul generates the power which has
an imaginative perception of futurity, through motions of this kind,
or that the things which are adduced from matter constitute
dæmons, through the powers that are inherent in them, and
especially things adduced from the matter which is taken from
animals.
For in sleep, when we are not employed about any thing, we
sometimes obtain a knowledge of the future.
But that a passion of the soul is the cause of divination, is indicated
by this, that the senses are occupied, that fumigations are
introduced, and that invocations are employed; and likewise, that
not all men, but those that are more simple and young, are more
adapted to prediction.
The ecstasy, also, of the reasoning power is the cause of divination,
as is likewise the mania which happens in diseases, or mental
aberration, or a sober and vigilant condition, or suffusions of the
body, or the imaginations excited by diseases, or an ambiguous state
of mind, such as that which takes place between a sober condition
and ecstasy, or the imaginations artificially procured by
enchantment.