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Update on Asian Studies Related to Emissions and Modeling. Topics Covered. Reminder of MICS study Progress related to RAINS-Asia activities What has taken place since last meeting Emerging Activities. How Robust Are The Source-Receptor Relationships?. - PowerPoint PPT Presentation
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Update on Asian Studies Related to Emissions and Modeling
•Reminder of MICS study
•Progress related to RAINS-Asia activities
•What has taken place since last meeting
•Emerging Activities
Topics Covered
•The MICS-ASIA Study: Model InterComparison of Long-Range Transport and Sulfur Deposition in East Asia
How Robust Are The Source-Receptor Relationships?
Many different models with important similarities and differences:Lagrangian, Eulerian, Hybrid, etc.
Participant(s) Organization Model name Model type
Main model focus
S.-B. Kim,T.-Y. Lee, K-Y. Ma
Dept of Atmospheric Sciences, Yonsei University, Seoul (Korea)
YU-SADM (Yonsei Univ.-
Sulfur Acid Dep. Model)
3D Eulerian
Long-term period or episodic estimation of sulfur sources contributions
H. Hayami, Y. Ichikawa
CRIEPI (Japan) CRIEPI trajectory model
Lagrangian
1-layer
Long-term evaluation
H. Hayami, O. Hertel,Y. Ichikawa
CRIEPI (Japan) and National Env. Research Institute (Denmark)
ACDEP ASIA Lagrangian
1-layer
Long-term evaluation
I. Uno,E.S. Jang
Research Institute for Applied Mech., Kyushu Univ, Fukuoka (Japan)
RIAM version of RAMS on-line tracer model
3D Eulerian
Episodic and long-term simulation for chemical climate studies
Y. Ikeda, R. Yasuda, H. Nakaminami
Osaka Prefecture University (Japan)
OPU-Model (Osaka
Prefecture Univ.)
3D Eulerian
Long-term deposition
S.Y. Cho, G. Carmichael
CGRER, University of Iowa
STEM 3D Eulerian
Episodic and long-term studies
G. Calori, G. Carmichael
CGRER, University of Iowa
ATMOS-2 Lagrangian
multi-layer
Long-term conc. and depositions of sulfur in Asia. Source-receptor relationships.
M. Engardt Swedish Meteorological and Hydrological Institute
MATCH 3D Eulerian
Long-term concentrations and depositions of ozone and acidifying substances
SO2 concentrations - 11-20 January
0
5
10
15
20
ppb
SO4 concentrations - 11-20 January
0
5
10
15
20
ug/m
3
SO4 wet depositions - 11-20 January
1
10
100
1000
ug/m
2
Comparison with monitoring data for the 11-20 January period.
0.2
0.3
0.4
0.5
0.6
0.7
0.8
C China E China S Korea C Japan
Regionl
Model 1
Model 2
Model 5
Model 6
Model 7
Model 8
Wet to total sulfur ratio in depositions for both months (January and May together) over the target regions.(Task
A)
Uncertainty in the Source-Receptor Relationships
Receptor 4 - Komae (Japan)
0%
20%
40%
60%
80%
100%
1 2 3 4 5 6 7 8
NW ASIA
SE ASIA
TAIWAN
S CHINA
C-E CHINA
NE CHINA
N & S KOREA
JAPAN
Inter-model VariabilityReceptor 16 - Nanjing (China)
0%
20%
40%
60%
80%
100%
1 2 3 4 5 6 7 8
Receptor 17 - Taichung (Taiwan)
0%
20%
40%
60%
80%
100%
1 2 3 4 5 6 7 8
•Need to assess inter-annual variability.
How Robust Are The Source-Receptor Relationships?
Uncertainty in the Source-Receptor Relationships
0
10
20
30
40
50
60
0 10 20 30 40 50 60 70 80 90 100
Contribution (%)
Variability
(%
)
INDI -> LAOS
VOLC -> INDO
KORN -> KORS
CHIN -> J APA
THAI -> CAMB
INDI -> BANG
INDI -> MYAN
FSU -> MONGCHIN -> CAMB
INDI -> BHUT
INDI -> INDI
CHIN -> CAMB
Interannual Variability (25-yrs)
Journal Global Environmental Engineering, 2002
Transboundary Pollution Issues Contunue to be of Importance
Japan
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
1975 1980 1985 1990 1995 2000
Year
De
po
sitio
n c
on
trib
utio
ns
0
50
100
150
200
250
300
350
400
450
To
tal d
ep
. (G
g S
/yr)
JAPA
CHIN
VOLC
KORS
SEAL
Tot
S-Deposition
RAINS-Asia –Carmichael et al., (2001)
Republic of Korea
0
50
100
150
200
250
300
1975 1980 1985 1990 1995 2000
Year
To
tal d
ep
ositio
n (
Gg
S/y
r)
7 0 8 0 9 0 1 0 0 1 1 0 1 2 0 1 3 0 1 4 0
L o n
- 2 0
- 1 0
0
1 0
2 0
3 0
4 0
Lat
-50
0
50
100
200
300
10000
%
Total S depositions: 1975-2000 % change
Em issions as of 7.3.2000
Change in Sulfur Deposition between 1975 and 2000.
-100%
0%
100%
200%
300%
400%
500%
1975 1980 1985 1990 1995 2000
Year
Emis
sion
% c
hang
e
P.R. China
India
Japan
Malaysia
Pakistan
Republic of Korea
Singapore
Sea lanes
Japan
0
50
100
150
200
250
300
350
400
450
1975 1980 1985 1990 1995 2000
YearT
ota
l d
ep
ositio
n (
Gg
S/y
r)
0
2000
4000
6000
8000
10000
12000
1975 1980
Volcanoes Sea lanes Taiwan
Hong Kong Malaysia Singapore
Indonesia P.R. Korea Rep. of Korea
Japan P.R. ChinaES&T, Dec., 2002
Effect of Interannual Meteorological Variability
on Sulfur Deposition can be Much Larger than
Changes in Emissions!China
-30%-20%-10%
0%10%20%30%
85 90 91 92 93 94 95 96 97 98 99
Year
Japan
-30%-20%-10%
0%10%20%30%
85 90 91 92 93 94 95 96 97 98 99
Year
Is there climate feedback link?
Passive Sampler Network – one way to increase coverage and participation
Passive Sampler Phase II Study Completed
SO2 Results – Annual Averages
NH3 Results – Annual Averages
O3 Results – Annual Averages
Atmos. Env., in press, 2003
Regional Air Pollution Issues
• Long-range transport: Northern China Korea Japan North America (?!) Intercontinental
• Regional visibility impairment, reduced insolation--compounded by dust from western deserts, climate implications
• Acid rain, sulfur deposition, nitrogen deposition (NH3 involvement from fertilizer use), eutrophicaion of surface waters
• Regional ozone formation, caused by organics + NOx with the involvement of CO and CH4
• Trace elements from coal combustion, particularly Hg• Aerosols, including BC, OC
ACE-Asia (NSF) & TRACE-P (NASA)
Spring 2001 Experiments
NASA/GTE DC-8
Shanghai
y = 0.008x - 1.3186R2 = 0.799
y = 0.0072x - 0.8R2 = 0.6453
0
0.5
1
1.5
2
2.5
3
0 200 400 600 800 1000 1200
CO Concentration
HC
HO
Co
ncen
trati
on
Hong Kong
y = 0.0049x + 0.3503R2 = 0.6273
y = 0.0043x + 0.4041R2 = 0.537
0
0.5
1
1.5
2
2.5
3
0 100 200 300 400 500 600
CO Concentration
C2H
6 C
on
cen
trati
on
Beijing
y = 0.0079x - 1R2 = 0.4348
y = 0.0074x - 1R2 = 0.9076
0
0.2
0.4
0.6
0.8
1
1.2
1.4
75 125 175 225 275 325
CO Concentration
BC
Con
cent
ratio
n
Comparing Modeled and Measured Ratios
We extract all points associated with a specified city and plot measured ratios and plot modeled ratios.
Comparison of Modeled and Observed Results from China’s Mega Cities
Shanghai model
measured
Shanghai emissions
Hong Kong model
measured
Hong Kong emissions
Beijing model
measured
Beijing emissions
HCHO/CO .0072 .008 0.00249 0.0045 0.0018 0.0096 0.007 0.0072 0.00251
C2H6/CO .0106 .0101 0.00456 0.0043 0.0049 0.01143 0.0058 0.0051 0.00452
SO2/C2H2 4.613 3.71 16.26 2.251 1.150 38.672 4.07 4.10 8.076
SO2/CO .0179 .0195 0.1049 0.0031 0.0031 0.2618 0.0236 0.0214 0.0575
N0x/SO2 .222 .229 0.997 0.468 0.416 2.705 0.299 0.296 0.884
C2H6/C2H2 1.18 1.14 0.7057 1.657 0.736 1.689 1.21 1.22 0.634
BC/CO .0105 .0112 0.00838 0.0058 0.0055 0.01 0.0074 0.0079 0.0080
BC/SO2 .245 .30 0.0799 1.299 1.301 0.06 0.138 0.186 0.14
Urban Photochemistry
NOx-VOC Sensitivity to O3 Production
VOC sensitive
NOx sensitive
Loss(N
)/(L
oss(N
)+Loss(R
))
Model NOx (ppbv)
Model results along the flight path
Megacity points from back trajectories
Klienman et al., 2000Klienman et al., 2000
Less than 2 day old plumes
Results from Trace-P Intercomparison Study
The Importance of Fossil, Biofuels and Open Burning Varies by Region
Using Measurements and Model – We Estimate Contributions of Fossil, Biofuel and Open Burning Sources
Ron Brown –Ace-Asia: Note differences between surface and aloft
Asian Brown Cloud – A New UNEP Study
Where do we go from here?Example of Use of 3-D CFORS modeling system at TRACE-P Information Day in Hong Kong
Considerations for Future MICS Studies
• Many regional modeling efforts in East Asia (Models 3 Community Modeling, Hong Kong EPA, ChinaMap, etc.) How to include them? And Chinese models?
• Nitrate, NH3 & longer-term have been identified as important next steps
• I also see the importance of such studies for dust, PM2.5/10, BC/OC, AOD – real need here as removal processes not well understood, big differences emerge
• and even extending to ozone.
Considerations for Future MICS Studies
Many source receptor like problems remain:• Region to region• Continent to continent• Source contribution
Another related direction is to study connection between what’s observed at the surface and what is in the column above it.
How are results dependent on the Met products?
Upcoming Activities
• ASAAQ Modeling workshop
• NATO/ITM
• ABC Study
• IGAC/CAD
• Others