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Atmospheric chemistry

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Title: Atmospheric chemistry


1
Atmospheric chemistry
  • Day 3
  • Tropospheric chemistry

2
Global tropospheric chemistry
  • Questions to be addressed
  • Many organic compounds emitted to the atmosphere
    are oxidised, eventually forming CO2 and H2O.
    What determines the oxidising capacity of the
    atmosphere?
  • Methane is a greenhouse gas, whose atmospheric
    concentration has more than doubled since the
    industrial revolution. What governs it
    concentration?
  • Tropospheric oxidation is strongly influenced by
    NOx, whose lifetime is 1 day. How is NOx
    transported to regions with no NOx emissions?
  • Ozone is a secondary pollutant. In the boundary
    layer it affects human health, growth of
    vegetation and materials. It is also a greenhouse
    gas. What governs its concentration?

3
Methane oxidation
  • CH4 OH (O2) ? CH3O2 H2O
  • CH3O2 NO ? CH3O NO2
  • CH3O O2 ? HO2 HCHO
  • HO2 NO ? OH NO2
  • HCHO OH (O2) ? HO2 CO H2O
  • HCHO hn ? H2 CO
  • HCHO hn (2O2) ? 2HO2 CO
  • Note
  • 2 x(NO ? NO2) conversions
  • HCHO formation provides a route to radical
    formation.

4
General oxidation scheme for VOCs
  • O3 h? ? O1D O2
  • O1D H2O ? 2OH
  • OH RH (O2) ? RO2 H2O
  • RO2 NO ? NO2 RO
  • RO ?? HO2 (RCHO)
  • HO2 NO ? OH NO2
  • NO2 h? ? NO O O O2 ? O3
  • OVERALL
  • NOx VOC sunlight ? ozone
  • The same reactions can also lead to formation of
    secondary organic aerosol (SOA)

5
THE OH RADICAL MAIN TROPOSPHERIC OXIDANT
Primary source
O3 hn g O2 O(1D) (1) O(1D) M g O
M (2) O(1D) H2O g 2OH (3)
Sink oxidation of reduced species
CO OH g CO2 H CH4 OH g CH3 H2O HCFC
OH
Major OH sinks
g H2O
GLOBAL MEAN OH 1.0x106 molecules cm-3
6
Other oxidising species
  • NO3
  • NO2 O3 ? NO3 O2
  • NO2 NO3 M N2O5
  • NO3 is rapidly lost in the day by photolysis and
    reaction with NO (? NO2), so that its daytime
    concentration is low. It is an important night
    time oxidant. It adds to alkenes to form
    nitroalkyl radicals which form peroxy radicals in
    the usual way.
  • O3
  • Ozone reacts with alkenes to form a carbonyl
    an energised Criegee biradical. The latter can be
    stabilised or decompose. One important reaction
    product is OH O3 reactions with alkenes can act
    as a source of OH, even at night.

7
Removal of organic compounds from the atmosphere
by reaction with OH
  • Lifetime 1/kOH 1/1x106k s
  • Rate coefficients at 298 K/10-12 cm3 molecule-1
    s-1
  • CH4 7x10-3 CO 0.24 isoprene 110 ethane
    0.25
  • Atmospheric distribution depends on lifetime. NH
    is major source of anthropogenic pollutants. CH4
    is distributed globally with only a slight NH/SH
    difference. Isoprene is found only close to its
    (very extensive) sources.
  • The oxidising capacity of the atmosphere refers
    to its capacity to remove VOCs and depends on
    OH (and the concentrations of other oxidants
    O3, NO3

8
Global budget for methane (Tg CH4 yr-1)
  • Sources
  • Natural 160
  • Anthropogenic 375
  • Total 535
  • Natural Sources
  • wetlands, termites, oceans
  • Anthropogenic Sources
  • natural gas, coal mines, enteric fermentation,
    rice paddies,
  • Sinks
  • Trop. oxidation 445
  • by OH
  • Transfer to 40
  • stratosphere
  • Uptake by soils 30
  • Total 515
  • Notes
  • The rate of oxidation is k5CH4OH, where the
    concentrations
  • are averaged over the trop.
  • 2. Concentrations of CH4 have increased from 800
    to 1700 ppb since pre-industrial times
  • 3. Methane is a greenhouse gas.

9
HISTORICAL TRENDS IN METHANE
Historical methane trend
Recent methane trend
Recent measurements at Mace Head in W
Ireland. 1mg m-3 0.65 ppb NB seasonal
variation higher in winter
10
GLOBAL DISTRIBUTION OF METHANENOAA/CMDL surface
air measurements
  • Seasonal dependence higher in winter than
    summer (maximum in NH correlates with minimum in
    SH).
  • NH concentrations gt SH main sources are in SH
    slow transport across ITCZ.

11
GLOBAL BUDGET OF CO
12
GLOBAL DISTRIBUTION OF CONOAA/CMDL surface air
measurements
  • Compare CH4. What are the differences and why?
  • (Rate coefficients at 298 K/10-12 cm3 molecule-1
    s-1 CH4 7x10-3
  • CO 0.24)

13
Global VOC emissions (Tg yr-1)
  • Anthropogenic
  • fuel production and distribution 17 fuel
    consumption 49 road transport 36 chemical
    industry 2 solvents 20 waste burning 8, other
    10. Total 142 Tg yr-1
  • Biogenic
  • isoprene 503 monoterpenes 127 other reactive
    VOCs 260, unreactive VOCs 260 Total 1150 Tg yr-1
  • Typical atmospheric lifetimes (for OH 1x106
    molecule cm-3)
  • t 1/kOH
  • CH4 6 yr isoprene 2.7 h
  • CO 48 days ethane 46 days
  • benzene 6 days ethene 30 h

14
Global budget for NOx
  • Global sources (Tg N yr-1)
  • Fossil fuel combustion 21 Biomass burning 12
  • Soils 6 Lightning 3
  • Ammonia oxidation 3 Aircraft 0.5
  • Transport from strat 0.1
  • Coupling (rapid - 1 minute in the day
  • NO O3 ? NO2 O2
  • NO2 Light ? NO O O O2 M ? O3 M
  • Also HO2 NO ? NO2 OH
  • Loss
  • OH NO2 M ? HNO3 M
  • Rainout of HNO3
  • Lifetime of NOx is about 1 day. NOx is a key
    component in ozone formation. Can it be
    transported to regions where it is not strongly
    emitted?

15
PEROXYACETYLNITRATE (PAN) AS RESERVOIR FOR
LONG-RANGE TRANSPORT OF NOx
16
NO2 as an air pollutant. UK NOx emissions, 1970 -
2000
Recent road transport data for the UK
17
Spatial distribution of NOx emissions
18
EU Air quality objectives limit valueslegally
binding
  • NO2
  • 1 hour mean
  • 200 mg m-3 (105 ppb) (not to be exceeded gt18
    times per year)
  • annual mean
  • 40 mg m-3 (21 ppb)
  • To be achieved by 2010. Possible to apply for
    derogation to 2015

19
Maps of annual mean background NO2 concentrations
UK 2010
UK 2001
Key AQ objective is annual mean of 40 mg m-3 to
be achieved by 2010 (EU Directive)
20
Annual mean NO2 concentrations, London
London 2010 670 road links out of 1888 exceed 40
mg m-3
London 1999 1407 road links out of 1888 exceed 40
mg m-3
21
Hungarian air quality networkhttp//www.kvvm.hu/o
lm/index.php
22
NO2 in Budapest and Hungary in 2005
23
MAPPING OF TROPOSPHERIC NO2FROM THE GOME
SATELLITE INSTRUMENT (July 1996)
Martin et al. 2002
24
Global budget for ozone (Tg O3 yr-1)
  • Ozone is a secondary pollutant and is not
    directly omitted.
  • Chemical production 3000 4600
  • HO2 NO 70
  • CH3O2 NO 20
  • RO2 NO 10
  • Transport from stratosphere 400 1100
  • Chemical loss 3000 4200
  • O1D H2O 40
  • HO2 O3 40
  • OH O3 10
  • others 10
  • Dry deposition 500 - 1500
  • Ozone is a greenhouse gas. It affects human
    health, plant growth and materials

25
GLOBAL BUDGET OF TROPOSPHERIC OZONE
GEOS-CHEM model budget terms, Tg O3 yr-1
Chem prod in troposphere 4920 Chem loss in troposphere 4230
Transport from stratosphere 475 Deposition 1165
O2
hn
O3
STRATOSPHERE
8-18 km
TROPOSPHERE
hn
NO2
NO
O3
hn, H2O
OH
HO2
H2O2
Deposition
CO, VOC
26
Sources of ozone in W Ireland
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