hemispheric transport of ozone pollution and the nonlinearities

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Hemispheric transport of ozone pollution and the nonlinearities GMI meeting UC Irvine March 17, 2008 Shiliang Wu, Harvard Bryan Duncan, NASA / GSFC Arlene Fiore, NOAA / GFDL Daniel Jacob, Harvard Oliver Wild, University of Lancaster

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Hemispheric transport of ozone pollution and the nonlinearities. Shiliang Wu, Harvard Bryan Duncan, NASA / GSFC Arlene Fiore, NOAA / GFDL Daniel Jacob, Harvard Oliver Wild, University of Lancaster. GMI meeting UC Irvine March 17, 2008. EU. NA. EA. SA. - PowerPoint PPT Presentation

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Page 1: Hemispheric transport of ozone pollution and the nonlinearities

Hemispheric transport of ozone pollution and the nonlinearities

GMI meeting

UC Irvine

March 17, 2008

Shiliang Wu, Harvard

Bryan Duncan, NASA / GSFC

Arlene Fiore, NOAA / GFDL

Daniel Jacob, Harvard

Oliver Wild, University of Lancaster

Page 2: Hemispheric transport of ozone pollution and the nonlinearities

HTAP Multi-model approach to estimate intercontinental source-receptor (S-R) relationships for ozone

20% decreases in:

anthrop. emis. in HTAP regions for NOx, CO, NMVOC individually

anthrop. emis. of all O3 and aerosol precursors in HTAP regions

global CH4

Conduct base simulations with 3-D models horizontal resolution of 4°x5° or finer 2001 meteorology each group’s best estimate for emissions in 2001 methane set to a uniform value of 1760 ppb

Conduct sensitivity simulations (17 total)

NA EUSA

EA

(Slide from Arlene Fiore @ GFDL)

Page 3: Hemispheric transport of ozone pollution and the nonlinearities

Estimates of S-R relationships: Springtime surface O3 decrease in HTAP receptor regions from 20% reductions of O3 precursors

0

0.20.4

0.6

0.8

11.2

1.4

NOx VOC CO ALL

EU and NA ≥ SA

RECEPTOR = EAST ASIA

20% foreign emis.) -20% domestic emis. ≈ 85%

pp

bv

EA/EU contribute similarly

EU VOC at least as important as NOx

RECEPTOR = NORTH AMERICA

pp

bv

20% foreign emis.) -20% domestic emis. ≈ 55%

SOURCE REGIONS: 3 foreign regions

0

0.2

0.4

0.60.8

1

1.2

1.4

NOx VOC CO ALL

Larger uncertainty in role of foreign VOC

(Slide from Arlene Fiore @ GFDL)

Page 4: Hemispheric transport of ozone pollution and the nonlinearities

Some questions remaining

Why so large variations across models associated with the role of VOCs?

Can 20% emission perturbations be scaled to other magnitudes? (Do the perturbations show good linearity? – this could have implications for the relative importance of different precursors in impacting the regional ozone export)

Do different models have similar/consistent linearity/nonlinearity for various perturbations?

Page 5: Hemispheric transport of ozone pollution and the nonlinearities

Large variations in EU AVOC inventories across models lead to large variations in calculated ozone export from EU

y = 0.0028x + 0.0362

R2 = 0.5898

0

0.05

0.1

0.15

0.2

0.25

0 5 10 15 20 25 30 35 40 45 50

EU AVOC inventories (Tg C / yr)

An

nu

al m

ea

n s

urf

ac

e O

3 d

ec

rea

se

s o

ve

r N

A (

pp

b)

GMI

GEOS-Chem

Annual mean NA surface O3 decreases (ppb) in response to 20% EU anthro. NMVOC reductions in different models

Page 6: Hemispheric transport of ozone pollution and the nonlinearities

Changes in surface O3 due to changes in EU AVOC emissions(simulation results from GMI model for JJA)

EU AVOC -20%

Full perturb / (20% perturb x 5)EU AVOC = 0

Control (ppb)

VOC perturbations are strongly linear

Page 7: Hemispheric transport of ozone pollution and the nonlinearities

VOC perturbations show very good linearity for all seasons

-0.5

-0.45

-0.4

-0.35

-0.3

-0.25

-0.2

-0.15

-0.1

-0.05

0

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

pe

rtu

rba

tio

ns

in O

3 (

pp

b)

(EU AVOC -20%) x 5

EU AVOC -100%

Changes in surface O3 over North America due to perturbations in EU anthro. VOC emissions (GMI results)

How about NOx?

Page 8: Hemispheric transport of ozone pollution and the nonlinearities

Changes in surface O3 due to changes in EA NOx emissions (simulation results from GMI model for JJA)

EA NOx -20%

Full perturb / (20% perturb x 5)EA NOx = 0

Control (ppb)

NOx perturbations show non-linearity

Page 9: Hemispheric transport of ozone pollution and the nonlinearities

Sensitivity to NOx emissions for different intercontinental pairsEA --> EUEA --> NA

-2

-1.6

-1.2

-0.8

-0.4

0

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

per

turb

atio

ns

in O

3 (p

pb

)

EU --> EAEU --> NA

-2

-1.6

-1.2

-0.8

-0.4

0

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

pe

rtu

rba

tio

ns

in O

3 (

pp

b)

NA --> EANA --> EU

-4

-3

-2

-1

0

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

pe

rtu

rba

tio

ns

in O

3 (

pp

b)

- - - - (effects from -20% NOx) x 5 effects from -100%NOx

The nonlinearities for NOx perturbations are even larger for other seasons.

Distinctive seasonal pattern for the North America impacts on Europe?

Source region: EA

Source region: NA

Source region: EU

Page 10: Hemispheric transport of ozone pollution and the nonlinearities

Intercontinental influence on surface O3 for different precursors

Decrease in surface O3 (ppb) due to foreign emission reductions

0

0.5

1

1.5

2

2.5

3

3.5

4

20% reductions (HTAP models / MAM)

North America

Europe East Asia

South Asia

Fiore et al. [2008]Sensitivity to VOC comparable to NOx

0

1

2

3

4

5

6

VOC

NOx

100% reductions (GMI/MAM)

0

1

2

3

4

5

6

VOC

NOx

North America

Europe East Asia

100% reductions (GMI/JJA)

Much weaker sensitivity to

VOC compared to NOx with full reductions or in

summer

Page 11: Hemispheric transport of ozone pollution and the nonlinearities

Intercontinental influence on surface O3 for different regions

Fiore et al. [2008]

-4

-3.5

-3

-2.5

-2

-1.5

-1

-0.5

0

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

per

turb

atio

ns

in O

3 (p

pb

)

(EU-20%)x5EU-100%(NA-20%)x5NA-100%

-3

-2.5

-2

-1.5

-1

-0.5

0

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

pe

rtu

rba

tio

ns

in O

3 (

pp

b)

(EU-20%)x5

EU-100%

(EA-20%)x5

EA-100%

Foreign impact on NA (GMI)(HTAP)

(HTAP)

EU ~ EA?

NA ~ EU

Foreign impact on EA (GMI)

Page 12: Hemispheric transport of ozone pollution and the nonlinearities

Consistency and discrepancy across models(Changes in NA surface O3 due to changes in EU NOx emissions)

- - - ( perturbations from -20% EU anthro. NOx) x 5

__ perturbations from zeroing out EU anthro. NOx MZ = MOZART-v2 (from Arlene)FR = FRSGCUNI (from Oliver)

-1.5

-1.2

-0.9

-0.6

-0.3

0

0.3

0.6

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC

per

turb

atio

ns

in O

3 (p

pb

)

MZ_SR3EU * 5 MZ_SR3zEU

FR_SR3EU * 5 FR_SR3zEU

GMI_SR3EU*5 GMI_SR3zEU

Page 13: Hemispheric transport of ozone pollution and the nonlinearities

- - - ( perturbations from -20% all EU anthro. emis) x 5

__ perturbations from zeroing out EU anthro. emis (NOx & VOC & aerosols)

Consistency and discrepancy across models(Changes in NA surface O3 due to changes in EU anthropogenic emissions)

-2.5

-2

-1.5

-1

-0.5

0

JUL AUG SEP OCT NOV DEC JAN FEB MAR APR MAY JUN

pe

rtu

rba

tio

ns

in O

3 (

pp

b)

MZ_SR6EU * 5MZ_SR6zEUFR_SR6EU * 5FR_SR6zEU

GMI_SR6EU*5GMI_SR6zEU

Page 14: Hemispheric transport of ozone pollution and the nonlinearities

On the family definition of Ox

Ox = O3 + O + NO2 + 2 NO3 + 3 N2O5 + PANs + HNO3 + HNO4

Ox = O3 + O + NO2 + 2 NO3 + 3 N2O5 + PANs + 2 HNO3 + HNO4 + other nitrates

Ox = O3 + O + NO2 + 2 NO3 + 3 N2O5 + PANs + 2 HNO3 + 2 HNO4 + HO2 + OH

Inconsistency in the family definition of Ox in literature on ozone budgets, leading to ambiguities in model intercomparisons.

Page 15: Hemispheric transport of ozone pollution and the nonlinearities

O3

O

NO2NO3 N2O5 HNO3

RNOx

HNO4

OH

HO2/RO2

HONO

H2O2/ROOH

Transport from stratosphere

Deposition

Carbonyls

Emission

h

12

Ox family

H2O, O2

A new family definition of Ox

(Slide from Daniel Jacob)

0.51

1.523

Ox = O3 + O + NO2 + 2 NO3 + 3 N2O5 +

PANs + 1.5 HNO3 + HNO4 + 0.5 HOy

Page 16: Hemispheric transport of ozone pollution and the nonlinearities

Thank you!