Title: M. Amann, I. Bertok, J. Cofala, F. Gyarfas, C. Heyes. Z. Klimont, W. Sch
1M. Amann, I. Bertok, J. Cofala, F. Gyarfas, C.
Heyes. Z. Klimont, W. Schöpp, W. Winiwarter
The CAFE baseline scenarios Air quality and
impacts
2Air quality impactsanalyzed for the CAFE
baseline scenario
- Health
- Loss in life expectancy attributable to PM2.5
- Premature deaths attributable to ozone
- Vegetation
- Ozone damage to forests (AOT40)
- Excess acid deposition to forests
- Excess acid deposition to semi-natural ecosystems
- Excess acid deposition to lakes
- Excess nitrogen deposition
- All impacts shown for no further climate
measures scenario, average results of 1997,
1999, 2000 2003 meteorological conditions
3Inter-annual meteorological variabilityfor PM2.5
1999
1997
Rural concentrations,annual mean µg/m3 from
known anthropog. sources excluding sec. org.
aerosols. Calculations with emissions for the
year 2000
2000
2003
4Anthropogenic contribution to PM2.5
2000 2010
2020
Rural concentrations, annual mean µg/m3 from
known anthropogenic sources excluding sec. org.
aerosols Average of calculations for 1997, 1999,
2000 2003 meteorologies
5Anthropogenic contribution to PM2.52020
Rural concentrations, annual mean µg/m3 from
known anthropogenic sources excluding sec. org.
aerosols Average of calculations for 1997, 1999,
2000 2003 meteorologies
6Loss in life expectancyattributable to
anthropogenic PM2.5 months
2000 2010
2020
Loss in average statistical life expectancy due
to identified anthropogenic PM2.5Average of
calculations for 1997, 1999, 2000 2003
meteorologies
7Loss in life expectancy 2020attributable to
anthropogenic PM2.5 months
Loss in average statistical life expectancy due
to identified anthropogenic PM2.5Average of
calculations for 1997, 1999, 2000 2003
meteorologies
8Loss in life expectancy attributable to
anthropogenic PM2.5 months
9Premature mortality attributable to ozonerelated
to excess of daily max. 8 hour means gt 35 ppb
(SOMO35)
Applied relative risk factor 1.003 / 10 µg/m3
increase in daily max 8 h mean
10Health-relevant ozone concentrationsSOMO35,
ppb.days
2000 2010
2020
Rural concentrations Average of calculations for
1997, 1999, 2000 2003 meteorologies
11Premature deaths attributable to
ozonecases/year
Provisional calculations with 5050 km resolution
12Vegetation-relevant ozone concentrationsAOT40
ppm.hoursm
2000 2010
2020
Critical level for forests 5 ppm.hours Average
of calculations for 1997, 1999, 2000 2003
meteorologies
13Vegetation-relevant ozone concentrations
2020AOT40 ppm.hours
Critical level for forests 5 ppm.hours Average
of calculations for 1997, 1999, 2000 2003
meteorologies
14Acid deposition to forests
2000 2010
2020
Percentage of forest areawith acid deposition
above critical loads, using ecosystem-specific
deposition, Average of calculations for 1997,
1999, 2000 2003 meteorologies
15Acid deposition to forests2020
Percentage of forest areawith acid deposition
above critical loads, using ecosystem-specific
deposition, Average of calculations for 1997,
1999, 2000 2003 meteorologies
16Percent of forest area with acid deposition
above critical loads
17Acid deposition to semi-natural ecosystems
including HABITAT areas
2000 2010
2020
Percentage of area of semi-natural
ecosystemswith acid deposition above critical
loads, using ecosystem-specific deposition.
Average of calculations for 1997, 1999, 2000
2003 meteorologies
18Acid deposition to semi-natural ecosystems
including HABITAT areas, 2020
Percentage of area of semi-natural
ecosystemswith acid deposition above critical
loads, using ecosystem-specific deposition.
Average of calculations for 1997, 1999, 2000
2003 meteorologies
19Semi-natural ecosystemswith acid deposition
above critical loads km2
20Acid deposition to freshwater bodies
2000 2010
2020
Percentage of catchments area with acid
deposition above critical loads, using
ecosystem-specific deposition. Average of
calculations for 1997, 1999, 2000 2003
meteorologies
21Acid deposition to freshwater bodies2020
Percentage of catchments area with acid
deposition above critical loads, using
ecosystem-specific deposition. Average of
calculations for 1997, 1999, 2000 2003
meteorologies
22Percent of lake catchments area with acid
deposition above critical loads
23Excess of critical loads for eutrophication
2000 2010
2020
Percentage of ecosystems area with nitrogen
deposition above critical loads, using
grid-average deposition. Average of calculations
for 1997, 1999, 2000 2003 meteorologies
24Excess of critical loads for eutrophication 2020
Percentage of ecosystems area with nitrogen
deposition above critical loads, using
grid-average deposition. Average of calculations
for 1997, 1999, 2000 2003 meteorologies
25Percent of ecosystems area with nitrogen
deposition above critical loads for eutrophication
26Conclusions
- With decreasing pollution, also impacts are
expected to decline in the future. - However, problems will not be entirely resolved
- PM remains serious (5 months life expectancy
loss in 2020) - Ozone
- Remains a significant cause for premature deaths
(Several 1000 cases in 2020) - Vegetation damage Wide-spread violations of
AOT40 critical level will prevail - Acidification Will not disappear, mainly due to
NH3 - Eutrophication remains unresolved