Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

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Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Transcript of Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Page 1: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012

Air chemistry (outdoor and indoor)

Page 2: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

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The Atmosphere: Pressure and Temperature

Page 3: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

3

O O O O

O O

O

O O

O

UV

UV

Page 4: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

4 The Chapman Mechanism

In the 1930s Sidney Chapman devised a mechanism that accounted

for the ozone layer and the temperature structure.

O2 + h O* + O*

O* + O2 + M O3 + M

O3 + h O2 + O*

O3 + O 2O2

Page 5: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

5Until 1964 the Chapman reactions were thought to be the principal processes governing the ozone balance in the stratosphere. However, measurements indicated that the actual concentration of ozone is smaller than that predicted by about a factor of two to four.

Predictions of ozone concentrations by the Chapman mechanism compared with observations at Panama, 1970.

Page 6: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

6Catalytic Ozone Destruction.

For a chemical to significantly affect the overall concentration of ozone it

either must be present in great abundance or must be involved in a catalytic

cycle. Breakthroughs in the 1970’s identified a number of NATURAL catalytic

processes that all have the form:

X + O3 XO + O2

XO + O X + O2

net : O3 + O 2O2

Where X = H, OH, NO, Cl or Br.

Page 7: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

7 CFCs: Molina and Rowland Nature 249, 810-812 (1974)

Page 8: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

8 Importance of reservoirs

If the catalysts carried on unabated they would

themselves destroy the ozone layer, but happily

there are termination reactions that lead to the

formation of reservoir species e.g.

Cl + CH4 HCl + CH3

ClO + NO2 ClONO2

Active (radicals) Inactive (reservoirs)

Page 9: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

The ozone hole27th Anniversary

Farman et al. Nature 1985

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What might have happened if we did nothing about CFCs?

Newman et al. Atm. Chem. Phys., 9, 2113 (2009)

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What might have happened if we did nothing about CFCs?

Newman et al. Atm. Chem. Phys., 9, 2113 (2009)

Page 12: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

12 Take home message

17% of globally averaged ozone gone by 2020

67% by 2065

Collapse of lower strat. tropical ozone by 2060

UV levels double by 2060

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Page 14: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

14 Air Pollution and the Troposphere10 km

NO, NO2, VOC

VOCs

halocarbons

0 kmCompounds of both biogenic and anthropogenic origin

1 km

The Tropopause

The Boundary Layer

Page 15: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

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O3 + sunlight O * + O2 < ~ 330 nm

O* + H2O OH + OH

OH + R-H R + H2O

VOCs broken down by the OH radical,

generated by sunlight

Page 16: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

16 Ozone Chemistry- low NOx environment

Δ[O3]

[NOx]

Examples: Marine boundary layer, remote free troposphere

Page 17: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

17 Ozone Chemistry- low NOx environment

O3 + hν → O (1D) + O2 λ ≤ ~ 330 nm

O (1D) + M → O (3P) + M

O (1D) + H2O → 2 OH

CO + OH → CO2 + H

H + O2 + M → HO2 + M

HO2 + O3 → OH + 2O2

Net: CO + O3→ CO2 + O2

Δ[O3]

[NOx]

Page 18: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

18 Ozone Chemistry- higher NOx environment

Δ[O3]

[NOx]

Examples: Outflow from pollution centres and biomass

burning regions

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Ozone Chemistry- higher NOx environment

CO + OH → CO2 + H

H + O2 + M → HO2 + M

HO2 + O3 → OH + 2O2

NO + HO2 → NO2 + OH

NO2 + hν → NO + O(3P)

O(3P) + O2 + M → O3 + M

Net: CO + 2O2 → CO2 + O3

Δ[O3]

[NOx]

Page 20: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

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Ozone Chemistry- higher NOx environment

CO + OH → CO2 + H

H + O2 + M → HO2 + M

HO2 + O3 → OH + 2O2

NO + HO2 → NO2 + OH

NO2 + hν → NO + O(3P)

O(3P) + O2 + M → O3 + M

Net: CO + 2O2 → CO2 + O3

Δ[O3]

[NOx]

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Ozone Chemistry- higher NOx environment

CO + OH → CO2 + H

H + O2 + M → HO2 + M

HO2 + O3 → OH + 2O2

NO + HO2 → NO2 + OH

NO2 + hν → NO + O(3P)

O(3P) + O2 + M → O3 + M

Net: CO + 2O2 → CO2 + O3

Δ[O3]

[NOx]

Page 22: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

NOx Limiting Environment

Δ[O3]

[NOx]

NO2 + OH → HNO3

Page 23: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

What about the indoor environment?

Three differences

1. No meteorology – slower movement of air (in

general) ventilation rates important

2. More surfaces (surface:volume ratio) deposition

and emission of chemicals much more important

3. Light levels very different (less UV indoors but

may have higher total light levels than outdoors?)

Page 24: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

1.Different ventilation rates

Some ideas from experiments in London

Page 25: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Site features

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A BC

X2

X1D

KEY

Receptor Site 1-12

Receptor Site A-C

Tracer Release Points

Marylebone Rd.

Glo

ucester P

lace

DAPPLE #02– Summer 2004

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Comparison between rooftop and indoor site

0.0E+00

5.0E-06

1.0E-05

1.5E-05

2.0E-05

2.5E-05

3.0E-05

3.5E-05

4.0E-05

4.5E-05

5.0E-05

0 2 4 6 8 10

Bag No,

C/Q

Roo

ftop

.

0.0E+00

5.0E-07

1.0E-06

1.5E-06

2.0E-06

2.5E-06

3.0E-06

3.5E-06

4.0E-06

4.5E-06

5.0E-06

C/Q

Indo

or .

Rooftop

Indoor

Roof conc. approx 10 times greater than Indoor

Longer transport time to

Indoor position

Longer decay time

Results Indoor (2004)

Page 28: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Ventilation rates

Mechanically ventilated –

sealed building, air sucked in and pumped out, regulated by levels of CO2. Outdoor air pumped in

but filtered to remove particles.

Naturally ventilated –

leaky buildings (most dwellings and many offices),

too hot, open a window, too cold, close off room.

Inevitable ingress of outdoor air.

Page 29: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

2. Emissions and deposition

1. Many chemicals released indoors are also

released outdoors but depending on confinement

and ventilation, exposure levels indoors may be

much much higher and last for much longer.

2. Typical sources indoors include; fabrics,

varnishes, paint, cooking, heating systems, air

fresheners! Cleaning products (with added scents)

Page 30: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Some examples of chemicals indoors

• Paradichlorobenzene Moth crystals, room deodorants

• Methylene chloride Paint removers, solvent usage

• Formaldehyde Pressed wood products, foam

• Styrene Insulation, textiles, disinfectants, plastics, paints

• Acetaldehyde Glues, deodorants, fuels, preventives, mold

growth on leathers

• Acrolein Component of oak-wood, by-product of the

combustions of wood, kerosene and cotton

Page 31: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Some examples of chemicals indoors

• Toluene diisocyanate Polyurethane foam, aerosols

• Benzene Smoking

• Tetrachloroethylene Wearing or storing dry-cleaned

clothes

• Chloroform Chlorinated water (showering, washing

clothes, dishes)

• 1,1,1-trichloroethane Wearing or storing dry-cleaned

clothes, aerosols sprays, fabric protectors

• Carbon tetrachloride Industrial strength cleaners

Page 32: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Some examples of chemicals indoors

• Aromatic hydrocarbons (toluene, xylenes,

• ethylbenzene, trimethylbenzenes)

• Paints, adhesives, gasoline, combustion sources

• Aliphatic hydrocarbons

• (octane, decane, undecane)

• Paints, adhesives, gasoline, combustion products

• Terpenes (limoneme, α-pinene) Scented deodorizers,

polishes, fabrics, fabric softeners, cigarettes, food

beverages

Page 33: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

Some examples of chemicals indoors

• Alcohols Aerosols, window cleaners, paints, paint

thinners, cosmetics and adhesives

• Ketones Lacquers, varnishes, polish removers,

adhesives

• Ethers Resins, paints, varnishes, lacquers, dyes,

soaps, cosmetics

• Esters Plastics, resins, plasticizers, lacquers

solvents, flavours, perfumes

Page 34: Prof. Dudley Shallcross Atmospheric Chemistry Research Group 2012 Air chemistry (outdoor and indoor)

3. Light levels

1. Glass will cut off high energy UV light from the

Sun and will reduce visible light levels. General

shading by buildings will also reduce light levels in

general.

2. All this means that Chemistry is much slower

indoors than outdoors but the build up can be

greater because of the slow air movement.