at Flashcards

1
Q

Thermosphere

A

• Temperature (T) increases with altitude (z) (why?)
• Short wavelengths absorbed and photo-ionisation occurs
leading to energetic atoms and ions
• Low air density ~ heat capacity small

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
2
Q

Auroral emissions

A

• Atomic and molecular systems of O2
and N2 predominate
• especially in the auroral green line (O1S→1D) at 557.7nm
• Bombardment by solar particles from above causes ionisation
followed by dissociative recombination with electrons
O2
+ + e- O(1S) + O(3P)
• The red lines in the aurora result from the transition
O(1D) O(3Pj
) + hv (ʎ = 630.4 nm)
• Violet and blue arise from excited states of N2

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
3
Q

Mesosphere

A

The ‘mystery layer’ – heavy metal chemistry
• T falls with z to ~ -80oC at mesopause (P < 0.01 mb)
(why?)
• Lowest ever atmospheric T recorded at mesopause ~ -
140oC
• Polar mesospheric clouds (more on these later!)

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
4
Q

Stratosphere

A

Temperature increases with altitude (why?)
• Very stable and dry air – planes fly up here sometimes to
avoid turbulence
• Where the ozone layer is (we will discuss this in detail)
• Polar stratospheric clouds form here (more later!)

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
5
Q

The Troposphere

A

is the lowest region in the atmosphere, extending approximately
10km…up to 8km (poles) or 17km (equator).
Here, the temperature falls by about 6.5⁰C/km. Therefore, the air is unstable,
causing weather with rapid mixing, especially in the centre (equatorial plane)
where convective thunderstorms are common

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
6
Q

Concentration units for gases

A

bsolute: molecules per cm3 of air; partial pressure
• Computational modelling, calculations etc.
• Relative: Percent of molecules ( percent by mass); mole fraction (or
mixing ratio); and for minor components, ppmv
(number of molecules per
million molecules of air)
• Health guidelines, published data etc.
Pi Vi = niRT
We can convert relative and absolute via ideal gas formula..HOW?

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
7
Q

Explain the temperature changing in the different at. layers

A

Troposphere: As the altitude increases, the air temperature decreases.

The troposphere is hotter near the Earth’s surface because heat from the Earth warms this air. As the altitude increases the number of air molecules decreases, thus the average of their kinetic energy decreases. The results is a decrease in air temperature with an increase of altitude.

Stratosphere: As the altitude increases, the air temperature increases.

The Stratosphere has a layer of ozone, called the ozone layer. This layer absorbs most of the ultraviolet radiation from sunlight. This results in the stratosphere being warmer.

Mesosphere: As the altitude increases, the air temperature decreases.

The Mesosphere, like the troposphere layer, has a decrease in temperature with altitude because of the decreases in the density of the air molecules.

Thermosphere: As the altitude increases, the air temperature increases.

The Thermosphere is warmed by the absorption of solar X-rays by the nitrogen and oxygen molecules in this outer layer. Thus, the temperature of this layer increases with altitude.

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
8
Q

• Reservoirs:

A

Where any defined species is in significant quantities,
for significant periods. e.g. the atmosphere and ocean are both
reservoirs of carbon
where a defined species has accumulated.

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
9
Q

• Source:

A

The origin of a defined species. Biogenic (natural) or
anthropogenic (due to human activity)
where a defined species can be taken from…

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
10
Q

Sink

A

Destination of a substance. Where does it go to? What is its
fate?
where a defined species can accumulate.

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
11
Q

The ocean

A

both a sink (shallow) and reservoir (deep) of CO2

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
12
Q

Timescales of transport in the lower atmosphere

A

Horizontal flow in lower troposphere ~ 5 ms-1
• chemical species can travel 100’s km/day from emission point.
• Atmospheric winds move air parcels (and emissions) across entire
continents in few days
• Zonal winds in mid to upper troposphere move long-lived species far
from origin (across hemispheres)
• The concept of lifetime…important and highly contextual!

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
13
Q

Regional distribution
of pollutants
Depends on;

A
• Source location and type.
• Transport processes
spreading it around
• Chemical mechanisms
removing it from
atmosphere.
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
14
Q

The boundary layer

A
The troposphere consists of the
boundary layer and the free
troposphere.
• In the boundary layer, friction
with the surface (of earth)
causes highly turbulent mixing
close to the surface (wind).
The height of the boundary layer over
land varies between 0.5-3km during
the day and collapses to less than
0.5km at night when the ground cools
faster than the overlaying
atmosphere.
• Over the ocean the BL height is
usually about 1km and has less
diurnal variation. There is more
turbulent mixing at night because the
atmosphere cools faster than the
ocean
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
15
Q

Timelines of pollution diffusion

A

• Air mixes from the boundary layer to the free troposphere in about 2
days.
• E-W winds blow with an average of 10-30 m/s, so air is transported
around a line of latitude in 1-3 weeks.
• It takes at least 1 year for tropospheric air to cross between
hemispheres.
The distribution of pollutants around the world therefore is highly
dependent on the chemistry of those pollutants and the physical
nature of the environment in which they reside.

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
16
Q

What is ‘Air pollution’?… When is
a substance a ‘pollutant’?
Dependant on:

A
• Concentration
• Toxic effects on biological organisms
(including people!)
• Reactivity and timelines
• Context ( i.e. ozone in stratosphere vs
troposphere)
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
17
Q

Primary (1

o) pollutants:

A
Oxides of
nitrogen(NOx), hydrocarbons and/or
other volatile organic compounds
(VOCs)- vehicles, factories, towns, agriculture, shipping, volcanoes, wildfires 
Transform into secondary (2
o)
pollutants via photochemical
reactions (species formed thereafter
as a result of these reactions are
also referred to as secondary
pollutants)
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
18
Q

Formation of the Ozone (O3

) Layer

A
• 1 billion years ago, blue-green algae used Sun’s
energy to split H2O &amp; CO2
to form organics and O2
-
photosynthesis
• Some O2
reacted with C to form CO2 and the rest
accumulated - As O2 CO2
• IN the upper atmosphere, O2 absorbed sunlight to
form O radicals which recombined with O2
to form
O3
(more on this later!)
• O3 protects the planet from UV light &amp; allowed early
life to develop
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
19
Q

Present Day Atmosphere

A
• Relatively stable mixture of
several hundred gases from
different origins.
• Gaseous envelope surrounds the
planet and revolves with it.
• Mass of ~ 5.15 x 1015 tons held to
planet by gravity how does this influence
atmospheric composition?
Major components up to 80 km are ~ O2
(21%), N2
(78%), and Ar (1%) Small
amounts of other trace gases.
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
20
Q

Atmospheric scale - Troposphere

A
• The troposphere contains roughly 85%
by mass of the entire atmosphere.
• Characterized by decreasing
temperature with height and strong
convective mixing.
• The region that most biological activity,
weather processes &amp; chemistry
occurs.
How well did you know this?
1
Not at all
2
3
4
5
Perfectly
21
Q

Chemistry of the troposphere

A

• The tropospheric environment is oxidising: like a low temperature
combustor, hydrocarbons, CO and H2 get oxidised to CO2
and H2O
• Pollution, mainly in the form of NOx
(NO and NO2
) and hydrocarbons
contributes to photochemical smog, secondary product and aerosol
formation.
• This is dependant on weather conditions, sources, sinks and the
chemical characteristics of the pollutant.

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
22
Q

Hydrocarbons

A

Wide range of sources; can be both anthropogenic and biogenic.
• All species with carbon chain backbones, including unsaturated,
oxygenated and halogenated species.
• Many are highly reactive in the oxidative atmosphere and influence
the chemistry of the air.
• Species in the gas phase at STP are often referred to as VOC’s or
volatile organic compounds.
• Volatile Organic Compounds ( VOCs) contribute to the extreme
complexity of gas phase and aerosol chemistry in the atmosphere

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
23
Q

Nitrogen oxides in the troposphere

A

• NO and NO2
are rapidly interconverted into each other and are
therefore considered as NOx = NO and NO2
• The ratio of [NO]/[NOx
] is about 0.2 at the surface but increases at
higher altitudes.

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
24
Q

Lifetime of NOx

A

• The atmospheric life time of NOx
is short, at the boundary layer
(hours) and increases with altitude (days)
• Lifetime is longer in winter than summer (lower [OH])
• The short lifetimes results in limited transport (vertically and
horizontally) in the NOx
form but other forms are more stable (more
on this later)
distribution- shipping lanes, biomass burning, power plants

How well did you know this?
1
Not at all
2
3
4
5
Perfectly
25
Q

Why do we care? NOx

A
• NOx
is the key species in tropospheric ozone
formation.
• Dissolves in water to form HNO2
and therefore
acid rain.
• Behaves as a greenhouse gas.
• Acts indirectly through ozone formation to affect
climate.
• Can contribute to aerosol formation (haze).
26
Q

Fate of Trace gases in the atmosphere

A

• Emitted into atmosphere from natural and anthropogenic sources.
• Many in highly reduced form.
What happens?
• Rained out.
• Deposited as (or on) particles.
• Rise to the stratosphere.
• Chemically converted to other substances.
Most of these gases hang around long enough to be oxidised…

27
Q

Tropospheric vacuum cleaner

A

• Mechanism of oxidation reactions of trace gases usually do not
include reaction directly with O2
.
• Activation energy is high (strong O=O bond) and so reaction is too slow.
Instead; oxidation is initiated by hydroxyl (.OH) radicals
• The concentration of .OH in the atmosphere is exceedingly small
(~105
-107
radicals cm-3
).
• Residence time of only ~ 1 s since it reacts quickly with many
substances.
• Therefore, it’s significance was not realised until quite recently (1970’s)

28
Q

Measurement of OH

A

• FAGE experiment
• Lasers and electronic
control equipment

29
Q

The source of OH radicals in ‘clean’ tropospheric air

A

• Predominantly
O3
+ UV-b → O2
* + O*
O* + H2O → 2 .OH
• Then most trace gases are oxidised by a sequence of
steps beginning with reaction with OH radical

30
Q

Chemical fate of trace gases

A

1) Photodecomposition
e.g. aldehydes
H2C=O + UV-a → .H + H-C=O
2) .OH addition reaction to unsaturated molecules
3) Or Hydrogen abstraction
CH4
+ .OH → .CH3
+ H2O

31
Q

All processes generate radicals…..and their fate?

A

The predominant fate of radicals in the troposphere is reaction
with O2
(because of its abundance).
• Simple radicals undergo addition reaction with O2
to form peroxy
(RO2
) radicals
CH3
+ O2 → H3C-O-O.
(or CH3O2
)
• a non-peroxy oxygen atom often results in H-abstraction and
consequent formation of a hydroperoxy (HO2
) radical
H-C=O + O2 → CO + H-O-O.
Fate of radicals…cont.
a non-peroxy oxygen atom where it is not easy to abstract a
H atom, undergoes addition as for simple radicals. Here it
forms an acyl-peroxy radical (RCO3

32
Q

Fate of the peroxy (RO2

) radicals

A

Except in very clean air (e.g. over oceans) most common fate of
peroxy/ hydroperoxy radicals
H-O-O. + .NO → .OH + .NO2
H3C-O-O. + .NO → H3C-O. + .NO2
This is the mechanism pathway for the atmospheric oxidation of the
majority of NO to NO2
Note: these reaction have, in turn, regenerated more radicals
(including NO2
)
NEED TO KNOW

33
Q

Elevated O3 production mechanism

A
O + H2O → 2 OH Production of OH
OH + CH4 → H2O + CH3 Reaction of OH
CH3 + O2 → CH3O2 Peroxy radical formation
CH3O2 + HO2 → CH3OOH + O2 Reactions of peroxy radicals
in absence of NOx
CH3O2 + NO → CH3O + NO2 Reaction of peroxy radicals in
presence of NOx
i.e. conversion of NO to NO2
NO2 + hv → NO + O
Photolysis of NO2
leads to the
production of O3
O + O2→ O3
34
Q

Tropospheric oxidation of CH4

A

Methane is released into the troposphere by anaerobic biological
decay (i.e. rotting land fill) and the emission of natural gas.
The overall sum of processes;
CH4
+ 5 NO + 5 O2
+ UV-a → CO2
+ 5 NO2
+ H2O + 2 OH
NO2 + hv → NO + O
This demonstrates synergistic oxidation of CH4
and NO and an alternative production route of OH

35
Q

What is Smog?

A

Smog: derived from smoke + fog
• Episodes of concentrated air pollution where
meteorological conditions facilitate the production of
secondary pollutants.
• Physically and aesthetically undesirable, but the worst
consequences are health problems and mortality.

36
Q

Great London

Smog 1952

A
• Increased levels of SO2
,
particulate matter (PM), in
presence of dense fog and a
very low strong meteorological
inversion.
• ~4000 deaths directly
attributed during the episode
and up to 12,000 suspected.
• Subsequent clean air act to
reduce emission. Similar met.
conditions in 1962 had
dramatically reduced excess
deaths to 700.
37
Q

Characteristics of

Photochemical Smog

A
  • Reduced visibility
  • Respiratory and eye irritations (e.g. PAN)
  • High concentrations of ozone and peroxides
38
Q

What makes photochemical smog?

A

• Action of sunlight on the of the oxides of nitrogen (NOx) and
Volatile Organic Compounds (VOC).
• A photochemical smog is not formed unless both NOx and
VOCs are present in the same region.
• There are interacting oxidation processes that are photoinitiated
which produce secondary pollutants

39
Q

Conditions for formation

of photochemical smog

A
High concentrations of NOx, VOCs (heavy
traffic or industry- power plants)
• Sunlight for photochemical reactions, and
warm temperatures to accelerate reaction
rates.
• Little air movement (lateral or vertical) that
would cause dispersion of the reaction
mixture.
• Inversion layers can prevent chemicals
escaping the reaction mix and exacerbate
smog episodes.
40
Q

Other routes of ozone production…

A
By example of the most reactive VOCs:
unsaturated alkenes
OH radicals addition across the C=C bond, faster than H atom
abstraction (we know because we measured it by experiment.)
 The radical produced reacts with O2
by
addition to form a peroxy radical (RO2
).
• Peroxy radical oxidises NO to NO2
and forms
an oxy radical (RO)
Leads to O3
generation
• NO2
is photolysed (i.e. photochemical smog) by long-wavelength
UV light
NO2 + UV-a → NO + O
O + O2 → O3
O3 consequently builds up in the polluted region to higher levels
than are found in clean air.
41
Q

Smog: Its all about timing…

A

• Reactions of atomic O with other species cannot compete because
high [O2
] and fast reaction rate favours ozone formation;
O + O2 → O3
• The only significant source of O atoms is NO2
photolysis
NO2 + hv → NO + O
• [O3
] does not build up until most NO is oxidised to NO2
because NO
and O3 mutually self-destruct when significant concentrations are
reached.
NO + O3 → NO2
+ O

42
Q

Fate of oxy (RO) radicals? (the ones that were made in

the ozone production mechanism)

A
Varies depending on radical structure…
• Here cleavage of the C-C bond to form an
aldehyde and an alcohol radical
• The alcohol radical reacts with O2
(H-abstraction
= oxidation) to form another aldehyde
43
Q

Afternoon phase of Photochemical Smog

A
Characterised by build-up of;
• nitric acid, (HNO3
)
• hydrogen peroxide (H2O2
)
• peroxyacetyl nitrate (PAN)
• Ozone (O3
)
These are all products of
radical-radical reactions
44
Q

Radical-Radical reactions : Nitric/Nitrous Acid

main tropospheric sink for .OH is

A
radical-radical
reaction;
.OH + .NO2 → HNO3
Similarly, .OH + .NO → HONO (or HNO2
)
residence time is several days:
• dissolved in water or rained out,
• or photochemically decomposed (to .OH and .NO2
/
. NO)
45
Q

Radical-Radical reactions : Hydrogen Peroxide

A

Hydrogen peroxide can be formed by either of the following reactions:
2 .OH → H2O2
2 HOO. → H2O2
+ O2

46
Q

Why do we observe a peak in concentration of radical species such as
OH and NO first thing in the morning?
• Why after several days of hot, still weather do these peaks tend to
get progressively larger?

A

HONO is rapidly photolysed, but stable otherwise.
So, in cities affected by photochemical smog, HONO accumulates
during night.
This leads to a massive increase in the concentration of .OH and NO
radicals at dawn….
HONO + sunlight → .OH + .NO
…and starts the whole process again for a new day

47
Q

Radical-Radical reactions : PAN formation

A

peroxyacetylnitrate – PAN
• From a specific type of peroxy radical;
• The acyl peroxy radical
• (from last lecture) H atom abstraction by .OH from
aldehydes gives rise to acyl (RC=O.
) radicals
• These combine with O2
to form the acyl peroxy
radical
• When .NO is plentiful, acyl peroxy radical oxidises .NO to .NO2
• BUT in afternoon when [.NO] is very low, a radical-radical
reaction with NO2
forms peroxyacetylnitrate

48
Q

Environmental impact of

PAN species

A

• mucus membrane irritants and bronchial constrictors.
• Degrade rubber, paints and cloth.
• Interrupt plant function leading to reduced crop yields
and leaf damage.
• Lifetime of a few days thus facilitate regional transport of
NOx species.

49
Q

Particulates

A
solid or liquid particles suspended
in air
Dust, soot = solid particles.
Mist, fog = liquid particles.
Aerosol = solid and/or liquid particles dispersed in
air
Particles in a given sample differ in composition,
size &amp; shape.
Range of sizes:
100 m (0.1 mm) – 0.001 m (1 nm)
50
Q

Secondary Organic Aerosols

A

(SOAs) are key species produced
in the afternoon phase of
photochemical smog

51
Q

Distribution of particle sizes

A

Distribution = sum of 3 symmetrical distributions:
1) Nuclei and Aiken modes, d  0.01 m, produced by
condensation of pollutant vapours formed by chemical
reaction (see SOA later) and water vapour.
2) Accumulation mode, d  0.1 m, produced by coagulation
(aggregation?) of nuclei mode particles
3) Coarse particle mode, d  1 m, produced by mechanical
means, e.g. soot.

52
Q

Mass distribution fine particles

A

• Bimodal - negligible mass of nuclei mode
because particles so small.
• Biased to coarse particles in comparison to
number distribution (volume  d
3
)

53
Q

Particle residence times

A
• Residence time in
atmosphere is dependent
on particle size.
• Fine particles can remain
suspended for weeks.
• Eventually stick to large
object, aggregate or
‘rained out.
54
Q

Composition?

• Determining the composition of particulates is very difficult.

A

• A lot can be inferred about their composition fro their attributed sources,
however there are other important influencing factors.
• Other substances (e.g. trace gases in atmosphere) can be taken up by
particles. There are three mechanisms for this
• Adsorption
• Absorption
• Dissolution in aqueous surface film.
Health implications; mechanism by which other substances (toxics) can get into body

55
Q

Aerodyne – AMS (Aerosol Mass Spectrometer)

A

Only currently
available instrument capable of providing quantitative size and chemical
mass loading for sub-micron aerosol particles.
The AMS couples size-resolved particle sampling and
mass spectrometric techniques for chemical
composition into a single real-time measurement system
i.e. How much and what

56
Q

Particulates

A

in air are so small that they are individually invisible to
the naked eye.
Collectively, however, particulates form a haze that restricts visibility.
• On many summer days city skies appear milky white rather than blue,
due to scattering of sunlight by particulates in air whose diameter is
about the wavelengths of visible light (0.4 – 0.8 m) – related to SOA
as a result of photochemistry
• Haziness is sometimes used as a measure of concentration of
particulates of this size

57
Q

Air quality Indices (AQI)

A

Measures include (Units of g m-3
)
• Total suspended particulates (TSP)
• PM10: (PM = particulate matter) = concentration of all particles
with d < 10 m. ‘Inhalable’
• PM2.5: d < 2.5 m. ‘Respirable’
• Ultrafine: d < 0.05 m (limit variable)

58
Q

The effects of particulates

A

• Coarse vs. fine particles
• There has been lack of agreement about the possible effects of particulates.
• Most evidence based on statistical studies of death rates vs. particulate
concentrations.
• BUT World Health Organisation (WHO, 2014) – up to 7 million premature deaths
annually linked to air pollution,
• Chronic exposure to high PM linked to asthma, heart disease and lung cancer
• Outdoor air pollution and one of its major components, particulate matter (PM),
classified as carcinogenic

59
Q

AQI – What they mean

A
AQIs essentially represent the percentage of the National Environment
Protection (Ambient Air Quality) Standard (NEPM) reached for each
pollutant.
The NEPM standards used for the AQI’s are based on the averaging
times as mentioned above and are:
• 0.12 parts per million (ppm) for NO2
,
• 0.1 ppm for O3
,
• 0.2 ppm for SO2
,
• 9.0 ppm for CO,
• 50 micrograms per cubic metre (μg/m3
) for PM10
• 25 μg/m3
for PM2.5.
60
Q

Remediation strategies for PM?

A

• Since most fine particle air pollution results ultimately from
chemical reactions among gaseous molecules, the main remedy
is to control the emissions of the primary gaseous pollutants:
i.e. sulfur dioxide and the reactant NOx and many VOCs that
produce photochemical smog