down and bottom up source studies to evaluate and co benefits · gurgaon faridabad greater noida...
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Using Top‐down and Bottom‐up Source Apportionment Studies to Evaluate
Benefits and Co‐Benefits
Dr. Sarath Guttikunda
Founder @ UrbanEmissions.Info, New Delhi, IndiaAffiliate Assistant Research Professor, Desert Research Institute, Reno, USA
Workshop on Vehicular Air Pollution and Its Impact on Human HealthJointly Organized by MOEF / CPCB / EPCA / ICCT
New Delhi, IndiaSeptember 2nd, 2011
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• the sources of air pollution
• the source apportionment methods
• using results for evaluations and decisions
Let’s talk about..
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Sources?
….. what we need to know for better
evaluations and efficient decision making
Impacts
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Sources and their Contributions
industries
vehicle exhaust
power plants
road dust
domestic fuels
garbage burning
construction
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CO2 H2O CH4 CO CO2 SO2
Hydrosphere Human Activity
N2OCFCs
Stratosphere
H2SO4H2SO4
BCBC
OHO(1D)
OH
HNO3HNO3
O3
HO2
OH
NO2
NOUV O2
O2
O2
UV
OH
Greenhouse GasesPrimary PollutantsAbsorbing Aerosols (BC)
Reactive Free RadicalsLess Reactive RadicalsReflective Aerosols
Courtesy : John Reilly, MIT
VOC
Lightning
PM
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NOx
Ammonia
VOCs
Primary Particles(directly emitted)
Secondary Particles(from precursor gases)
Other(sea salt)
Other(sea salt)
Crustal(soil,dust)
Crustal(soil,dust)
OrganicCarbonOrganicCarbonCarbon(Soot)
Carbon(Soot)
SO2
AmmoniumSulfate
AmmoniumSulfate
AmmoniumNitrate
AmmoniumNitrate
MetalsMetals
Chemical composition gives an indication of the sources
Gas
ParticleParticle
PM
Source: J. Chow, DRI
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Results, using..Monitoring dataChemistry of the pollutantsGeographical knowledgeMeteorology Modeling
industries
vehicle exhaust
power plants
road dust
domestic fuels
garbage burning
construction
%
%%
%
%%
%
Consolidated decisions
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60 km
% Emissions ≠ % Ambient Pollution
A simulation of sulfur dioxide emissions from power plant stacks
monitorcarpower plant
more
less
more
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Source Apportionment
• Top‐down approach• Bottom‐up approach
Reference:
Johnson TM, Guttikunda SK, Wells G, Artaxo P, Bond T, Russell T, Watson J, and West J (2011)
“Tools for Improving Air Quality Management – A Review of Top‐Down Source Apportionment Techniques and their Applications in the Developing World”
ESMAP publications, The World Bank, Washington DC, USAhttp://www.esmap.org/esmap/node/1159
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MonitoringConcentrations
Receptor Modeling
Contributions
Source Profiles
Impacts
Evaluation
Decisions
EconomicTechnicalPolicy
Costs & BenefitsPollution
Control
Top‐Down Approach
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Emissions
Dispersion Modeling
Concentrations
PM, SO2, NOx, CO,
Ozone, VOC
Monitoring
Impacts
Evaluation
Decisions
EconomicTechnicalPolicy
Costs & BenefitsPollution
Control
Contributions
Bottom‐Up Approach
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PM2.5 Delhi 2001D
18%
G4%
RD21%
CB3%
BB20%
O19%
SA15%
PM2.5 Mumbai 2001D
19%
G4%
RD22%
C B4%
BB21%
O14%
SA16%
PM2.5 Ko lkata 2001
D20%
G5%
RD21%
CB4%
BB21%
O12%
SA17%
PM2.5 Beijing 2002
BB11%
SA31%
CB19%
MV6%
RD9%
I6%
O18%
PM10 Sao Paulo 1998
T26%
RD28%
O L20%
I6%
SA20%
PM10 Santiago 2000
SD42% SA
11%
BC9%
T36%
O2%
PM2.5 Mex ico C ity 2000
O L2%
Cu6%
SD39%
BB8%
SA33%
I9%
H3%
PM2.5 Qalabotjha 1997
RS61%
BB14%
SD1%
SA9%
I1%
O14%
PM2.5 Xian Winter 2003
G44%
D3%
CB44%
BB9%
PM2.5 Hanoi 1999- 01
LRT45%
CB28%
SD4%
T5%SA
10%
MA8%
PM2.5 Cairo Summer 2002SD8%
I12%
T31%
O B29%
MA2%
SA18%
PM2.5 Shanghai 2000-01
I32%
PP22%
RD3%
T16%
FD1%
MA26%
2002 PM2.5 Dhaka (Univ ersity)
MA1%
2StE9%
MV39%
BB/BK12% I
10%
SD10%
RD19%
PM2.5 Bangkok 2002
T35%BB
29%
OL2%
SD7%
SA25%
C2%
PM2.5 Manila 2001-02
T32%
I22%
COM20%
MIX16%
LRT10%
Top‐down Case Studies
Johnson & Guttikunda et al., 2011
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Top‐down vs. Bottom‐up
Rohini
Gurgaon
Faridabad
GreaterNoida
NOIDA
Ghaziabad
Outer Ring Road
Inner ring road
SouthDelhi
An example over Delhi, India
Top‐down results are limited to sampling locations
B20%
D20%
E20%A
20%
C20%
B25%
D10%
E25%A
10%
C30%E
45%
D10%
B5%
A30%
C10%
E5%
D30%
B45%
A10%
C10%
50 km
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0 5 10 15 20 25 30 35 40 45 500
5
10
15
20
25
30
35
40
45
50
PM2.5 Emissionsper grid
0.00 to 0.06 0.06 to 0.28 0.28 to 1.47 1.47 to 10.88 10.88 to 104.10
BK3%IND
11%
VEH57%
DOM6%
WST5%
GS8%
CON0.5%
DST10%
IND = industries; PP = power plants; DOM = domestic; VEH = transport; DST = road dust; WST = waste burning; CON = construction activities; BK = brick kilns; GS = generator sets
gridded transport emissions only % PM2.5 ground emissionsin the box
Top‐down vs. Bottom‐up
Bottom‐up results for all areas
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0 5 10 15 20 25 30 35 40 45 500
5
10
15
20
25
30
35
40
45
50
PM2.5 Emissionsper grid
0.00 to 0.06 0.06 to 0.28 0.28 to 1.47 1.47 to 10.88 10.88 to 104.10
BK1%
IND23%
DST8%
CON3.6%
GS8%
WST7%
DOM4%
VEH45%
gridded transport emissions only % PM2.5 ground emissionsin the box
Top‐down vs. Bottom‐up
IND = industries; PP = power plants; DOM = domestic; VEH = transport; DST = road dust; WST = waste burning; CON = construction activities; BK = brick kilns; GS = generator sets
Bottom‐up results for all areas
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0 5 10 15 20 25 30 35 40 45 500
5
10
15
20
25
30
35
40
45
50
PM2.5 Emissionsper grid
0.00 to 0.06 0.06 to 0.28 0.28 to 1.47 1.47 to 10.88 10.88 to 104.10
BK46%
IND8%
DST6%
CON1.5%
GS2%
WST4%DOM
3%
VEH30%
gridded transport emissions only % PM2.5 ground emissionsin the box
Top‐down vs. Bottom‐up
IND = industries; PP = power plants; DOM = domestic; VEH = transport; DST = road dust; WST = waste burning; CON = construction activities; BK = brick kilns; GS = generator sets
Bottom‐up results for all areas
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0 5 10 15 20 25 30 35 40 45 500
5
10
15
20
25
30
35
40
45
50
PM2.5 Emissionsper grid
0.00 to 0.06 0.06 to 0.28 0.28 to 1.47 1.47 to 10.88 10.88 to 104.10
BK3%
VEH45%
DOM5%
WST8%
GS4%
CON1.3%
DST9%
IND25%
gridded transport emissions only % PM2.5 ground emissionsin the box
Top‐down vs. Bottom‐up
IND = industries; PP = power plants; DOM = domestic; VEH = transport; DST = road dust; WST = waste burning; CON = construction activities; BK = brick kilns; GS = generator sets
Bottom‐up results for all areas
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Information
monitoring
data collection
Analysis
hot spots
apportionment
emissions
dispersion
impacts
Options
institutional
policy
technical
economic
impacts
Dialogue
stakeholders
options
cost & benefits
prioritization
Evaluating Benefits & Co‐Benefits
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August 31st 2008, API = 24
Photo Diary of Air Pollution in Beijing
August 24th 2009, API = 97
August 13th 2010, API = 83
50% drop in the NOx concentrations, during the 2 months of Olympic interventions.
Beijing’s Olympic Effort, 2008
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- PM
- C
+ PM
+ C
Public transportNon‐motorized transportEnergy efficiencyRenewables
Natural gas buses (leaks)
Increased motorizationIncreased fuel use
Generator sets
Using biomass
Co‐benefits approach
Cornie Huizenga, CAI‐Asia
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Coal Unloading onto Conveyor BeltNorth Chennai PP
Freight activity
Brick Kilns
Landfill
DOM4%
BK6%
IND2%
CON6%
WB5%
RD36%
GS2%
TR18%
PP21%
DOM6%
BK8%
GS5%
TR61%
IND20%
2010 ‐ PM10~56,000 tons/yr
2010 ‐ CO2~25 mil tons/yr
Chennai, India, 2010
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80 80.05 80.1 80.15 80.2 80.25 80.3 80.35 80.4
12.9
12.95
13
13.05
13.1
13.15
13.2
13.25 g/m3Brick Kilns
Brick Kilns
Bay
of B
enga
l
Chennai Port
Power Plant
IITAirport
Industries
Industries
0
10
20
30
40
50
60
70
80
100
80 80.05 80.1 80.15 80.2 80.25 80.3 80.35 80.4
12.9
12.95
13
13.05
13.1
13.15
13.2
13.25
2010 Annual Average PM10 Concentrations
VEH9%
DST15%
DOM4%
WST3%
GEN1%
IND3%
BK60%
CON4%
OTH0%PP1%
VEH9%
DST14%
DOM6%
WST4%
GEN1%
IND19%
BK4%
CON8%
OTH1%
PP34%
VEH10%
DST16%
DOM5%
WST3%
GEN1%
IND7%
BK54%
CON4%
OTH0%PP0%
VEH14%
DST19%
DOM9%
WST7% GEN
5%
IND22%
BK13%CON
4%OTH1%
PP6%
VEH16%
DST24%
DOM11%
WST8%
GEN11%
IND12%
BK6%
CON5%
OTH2%
PP5%
VEH18%
DST27%
DOM10%
WST7%
GEN6%
IND8%
BK15%CON
5%
OTH4%
PP0%
56 g/m3
73 g/m3
89 g/m3
37 g/m3
76 g/m3
40 g/m3
Chennai, India, 2010
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Health Impacts in 6 Cities
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• What is the role of domestic and construction sectors?
• What is the role of sustainable transport interventions?
• How can we improve monitoring?• Where are the co‐benefits?
• Urban vs. Rural• Outdoor vs. Indoor• Sector by Sector
• How to raise public awareness?
Questions to ask?
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Co‐Benefits in 6 Cities
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Reconciling Approaches
• Validating emission factors with measurements during source profiling
• Identifying missing sources using top‐down results
• Identifying hot‐spots for monitoring via dispersion modeling
• Using monitoring data for validating dispersion modeling results
• Establishing an pollution control strategy
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October 10th, 2010Mobile lidar monitoring provided spatial and temporal evolution of pollution during the games.
Pollution due to high congestion is reflected in the results
Emissions
Concentrations
Delhi, India, 2010
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Thank you
Questions?Dr. Sarath Guttikunda
@ www.urbanemissions.infoNew Delhi, India
September, 2011