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The GAINS (Greenhouse gas - Air Pollution
INteractions and Synergies) Model
Pallav PUROHIT (E-mail: purohit@iiasa.at)
IIASA - Air Quality and Greenhouse Gases (AIR) Program
GAINS IGP Training Session
19 October 2020
National emission ceilings
Decision making on
air quality
management
Policy
targets
Optimization
Emissions
Emission control options:
~2000 measures,
co-control of 10 air
pollutants and 6 GHGs)
Atmospheric dispersion
Costs
Health, ecosystems and
climate impact indicators
The GAINS Model
Energy activity
projections
• Global
• IEA/WEO, IEA/ETP,
POLES, MESSAGE,
LEAP, etc.
• Regional
• PRIMES, AIMS
• National
• IIMA – AIMS,
GCAM/IIMA,
MARKAL;
• TERI – MARKAL;
• IRADe – CGE model;
• CEEW - GCAM/IIMA;
• NITI Aayog –
MESSAGEix
• CSTEP
GAINS India: 23
Administrative
regions
ANPR: Andhra Pradesh (including Telangana);
ASSA: Assam; BENG: West Bengal; BIHA: Bihar;
CHHA: Chhattisgarh; DELH: Delhi NCT; EHIM: North
East (excl. Assam); GOA: Goa; GUJA: Gujarat; HARY:
Haryana; HIPR: Himachal Pradesh; JHAR:
Jharkhand; KARN: Karnataka; KERA: Kerala; MAHA:
Maharashtra; MAPR: Madhya Pradesh; ORIS:
Odisha; PUNJ: Punjab; RAJA: Rajasthan; TAMI:
Tamil Nadu; UTAN: Uttarakhand: UTPR: Uttar
Pradesh; WHIM: Jammu and Kashmir.
EHIM: Arunachal Pradesh, Manipur, Meghalaya,
Mizoram, Nagaland, Sikkim and Tripura.
Model linkage
CD-LINKS fuel ←
Biomass ← OS1 OS2
Coal ← HC1 HC2 HC3 BC1 BC2 DC
Gases ← GAS
Liquids ← MD GSL LPG HF
Electricity ← ELE
Heat ← HT
Geothermal ← GTH
Solar ← STH
Biomass ← OS1 OS2
Coal ← HC1 HC2 HC3 BC1 BC2 DC
Gases ← GAS
Liquids ← MD GSL LPG HF
Electricity ← ELE
Heat ← HT
Other ← GTH
Other ← STH
Biomass ← OS1 OS2
Coal ← HC1 HC2 HC3 BC1 BC2 DC
Gas ← GAS
Oil ← MD GSL LPG HF
Nuclear ← NUC
Hydro ← HYD
Geothermal ← GTH
Solar ← SPV STH
Wind ← WND
Biomass ← (included in mineral oil products)
Coal ← HC1 HC2 HC3 BC1 BC2 DC
Gases ← GAS
Oil ← MD GSL LPG HF
Electricity ← ELE
Hydrogen ← H2
CD-LINKS sector GAINS fuel GAINS sector
Final Energy
Residential
(DOM_RES)
Services
(DOM_COM)
Domestic others
(DOM_OTH)
Chemical
industry boilers
(IN_CHEM_BO)
Conversion
Sector Boilers
(IN_CON_BO)
Other Industry
Boilers
(IN_OTH_BO)
Final Energy
Paper & Pulp
(IN_PAP_OC)
Paper & Pulp
Boilers
(IN_PAP_BO)
Non-Metalic
Minerals
(IN_NMM_OC)
IGCCplants
(PP_IGCC)
Inland navigation
(TRA_OT_INW)
Maritime
(TRA_OTS)
Domestic
aviation
(TRA_OT_AIR)
Primary
Energy
Existing power
plants
(PP_EX_OTH)
New plants
(PP_NEW)
Advanced plants
(PP_MOD)
Final energy
Off-road 2-&4-
stroke sources
(TRA_OT_LD,
TRA_OT_LB)
Off-road
machinery and
construction
(TRA_OT_CNS)
Agriculture
(TRA_OT_AGR)
Engines/DG-sets
(PP_ENG)
Transport
Iron & Steel
(IN_ISTE_OC)
Chemical
industry
(IN_CHEM_OC)
Non-Ferrous
Metals
(IN_NFME_OC)
Other Industry
(IN_OTH_OC)
Rail
(TRA_OT_RAI)
Two-wheelers 2-
&4-stroke
(TRA_RD_LD2,
TRA_RD_M4)
Cars
(TRA_RD_LD4C)
Light-duty cars
(TRA_RD_LD4T)
Buses
(TRA_RD_HDB)
Heavy-duty
trucks
(TRA_RD_HDT)
Residential and
Commercial
Industry
Input to Power
sector incl. CCS
Mapping
to
the
GAINS
structure:
Example
Household energy end-use activities Fuel use for household cooking
• Cooking
• Heating (water + space)
• Lighting (electricity/kerosene)
• Heating and cooling
• Air conditioners/Desert cooler/Fan
• Refrigerators/Freezer
• Electric heaters
• Ironing (cloths)
• Other
• Washing machines
• Radio/VCR/VCD Player/TV/Laptop/Mobile, etc.
• Solid fuels
• Fuelwood, agri-residues, cow dung, lignite/coal,
charcoal
• Liquid fuels
• Kerosene, LPG
• Gaseous fuels
• NG, Biogas, Producer gas
• Electricity
• Solar (thermal)
• Box/Concentrator type
Household energy
 Annual primary energy requirement for cooking
• APEcooking = 365*Afw*CVfw
 Annual useful energy requirement for cooking
(annual)
• AUEcooking = 365*Afw*CVfw*ηstove,fw
• (5*18*13.5% = 12.15)
o Calorific value of fuelwood (MJ/kg)
o Efficiency of traditional cookstove (%)
o Average fuelwood consumption (kg/HH/day)
Household energy
consumption
for cooking
 Daily useful energy requirement
for cooking was 12.13
MJ/HH/Day (ABE, 1984)
 An average of 138 kg of LPG is
required per household per
annum to meet their cooking
energy needs
• ≈9–10 LPG cylinders of 14.2 kg
each in a year (IISD/IRADe,
2016)
• ≈11.3 to 12.5 MJ/HH/Day
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
INDIA
JAMMU
&
KASHMIR
HIMACHAL
PRADESH
PUNJAB
CHANDIGARH
UTTARAKHAND
HARYANA
NCT
OF
DELHI
RAJASTHAN
UTTAR
PRADESH
BIHAR
SIKKIM
ARUNACHAL
PRADESH
NAGALAND
MANIPUR
MIZORAM
TRIPURA
MEGHALAYA
ASSAM
WEST
BENGAL
JHARKHAND
ODISHA
CHHATTISGARH
MADHYA
PRADESH
GUJARAT
DAMAN
&
DIU
DADRA
&
NAGAR
HAVELI
MAHARASHTRA
ANDHRA
PRADESH
KARNATAKA
GOA
LAKSHADWEEP
KERALA
TAMIL
NADU
PUDUCHERRY
A.
&
N.
ISLANDS
RURAL
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
INDIA
JAMMU
&
KASHMIR
HIMACHAL
PRADESH
PUNJAB
CHANDIGARH
UTTARAKHAND
HARYANA
NCT
OF
DELHI
RAJASTHAN
UTTAR
PRADESH
BIHAR
SIKKIM
ARUNACHAL
PRADESH
NAGALAND
MANIPUR
MIZORAM
TRIPURA
MEGHALAYA
ASSAM
WEST
BENGAL
JHARKHAND
ODISHA
CHHATTISGARH
MADHYA
PRADESH
GUJARAT
DAMAN
&
DIU
DADRA
&
NAGAR
HAVELI
MAHARASHTRA
ANDHRA
PRADESH
KARNATAKA
GOA
LAKSHADWEEP
KERALA
TAMIL
NADU
PUDUCHERRY
A.
&
N.
ISLANDS
URBAN
State-wise distribution of households by type of fuel used
for cooking in rural and urban areas in India
Source: Census (2011)
 Annual primary energy demand for cooking
(APEcooking)
𝐴𝑃𝐸𝑐𝑜𝑜𝑘𝑖𝑛𝑔 = 365
𝑖=𝑗=1
𝑚,𝑛
𝑁𝑖,𝑗𝜉𝑖,𝑗𝑈𝐸𝑐𝑜𝑜𝑘𝑖𝑛𝑔− 𝑖,𝑗
𝜂𝑠𝑡𝑜𝑣𝑒,𝑖
Where
Ni,j = Number of households using ith fuel in jth State/UT
ξi,j = % of households using ith fuel in jth State/UT
ηstove,i = Efficiency of utilization of ith fuel
 Data sources
 Census of India;
 NSSO;
 CSO;
 NCAER;
 Demographic and Health Survey
(DHS)/IIPS
Household energy demand for cooking in India
o Annual kerosene consumption (AKClighting) for lighting in GAINS region “i” in year “y” is
estimated by using the following ex-pression:
𝐴𝐾𝐶𝑙𝑖𝑔ℎ𝑡𝑖𝑛𝑔 =
𝑃𝑂𝑃𝑖.𝑦
𝐻𝐻𝑆𝑖.𝑦
(1 − 𝐸𝐿𝐸𝑖.𝑦)365
𝑗=1
𝑛
𝑁𝑖,𝑗,𝑦ℎ𝑖,𝑗,𝑦𝐶𝑉𝑘𝑓𝑖,𝑗,𝑦 𝑆𝐶𝑗
o where
• POP = population,
• HHS = household size,
• ELE = electrification rate,
• f = share of device type “j” (either wick lamps or hurricane lanterns),
• N = number of kerosene lamps,
• h = daily operating hours,
• SC = specific kerosene consumption of a device
• CVk = calorific value of kerosene
Kerosene lighting
Diesel generators
 Fossil fuel-burning backup generators in
developing countries produce as much
energy as 700-1,000 coal-fired power
stations, consume US$50 billion in annual
spending, and emit dangerous chemicals
into homes and businesses.
 Data and Information gaps
 Number of diesel generators
(residential, commercial, industry,
agriculture, etc.)
 Capacity factor
 Age (New/Old)
 Type (Large/small)
Application rates of abatement measures: % of capacity/activity
0
20
40
60
80
100
2010 2020 2030 2040 2050
JAPAN - Heavy Duty Diesel
Vehicles control (%)
EURO I EURO II EURO III
EURO IV EURO V EURO VI
EURO VII
0
20
40
60
80
100
2010 2020 2030 2040 2050
CHINA - Power sector - SO2
control (%)
High efficiency flue gases desulphurisation
Wet flue gases desulphurisation
Wet flue gases desulphurisation (retrofitted)
In-furnace control - limestone injection
Low sulphur coal (0.6 %S)
0
20
40
60
80
100
2010 2020 2030 2040 2050
INDIA - Power sector - PM2.5
control (%)
High efficiency deduster
Electrostatic precipitator: 2 fields
Electrostatic precipitator: 1 field
What is a GAINS control strategy?
• A set of numbers (weighted averages) that tell you for each emission
source to what extent which control technology is being applied
Represents what kind of technologies are used
Represents what policies are planned or implemented, and how this changes over time
• For each technology: value is between 0% and 100%
• Sum over all technologies (incl. ‘no control’) = 100%
o Total activity is either controlled or not
o % is always relative to activity
o For power plants activity means energy input
How do I calculate a control strategy?
Example: Coal-fired power plants
500 MWel
250 MWel
STEP 1: Start with capacities: Total = 800 MWel
50 MWel
How do I calculate a control strategy?
500 MWel
250 MWel
50 MWel
Step 2: Calculate fuel input per year, using
• Operating hours per year
• Conversion efficiency
4,000 hours/yr, 35% efficiency
2,000 hours/yr, 30% efficiency
6,000 hours/yr, 32% efficiency
20.6 PJ/yr = 69%
6.0 PJ/yr = 20%
3.4PJ/yr = 11%
How do I calculate a control strategy?
Step 3: Determine control technology in operation
20.6 PJ/yr = 69%
6.0 PJ/yr = 20%
3.4PJ/yr = 11%
e.g. flue gas desulfurization
e.g. lime stone injection
e.g. no control
How do I calculate a control strategy?
1
500
20.6
1
250 6.0
1
50
3.4
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Number of plants Capacity Fuel input
Plant C
Plant B
Plant A
Apply control strategy here
How do I calculate a control strategy?
1
500
20.6
1
250 6.0
1
50
3.4
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Number of plants Capacity Fuel input
Plant C
Plant B
Plant A
Flue gas desulphurization = 69%
Lime stone injection = 20%
No control = 11%
Pathways towards clean air in India
Pallav PUROHIT (E-mail: purohit@iiasa.at)
IIASA - Air Quality and Greenhouse Gases (AIR) Program
GAINS IGP Training Session
19 October 2020
Air Pollution & Health
• Air pollution poses a major threat to human health and climate. The combined effects of
ambient and household air pollution cause about 7 million premature deaths every year
(UN, 2019), largely as a result of increased mortality from stroke, heart disease, chronic
obstructive pulmonary disease, lung cancer and acute respiratory infections.
• Exposure to ambient particulate matter is a leading risk factor for environmental public
health in India. It is estimated that only about 1% of the Indian population is exposed to
less than the global WHO guideline level of 10 μg/m3 annual mean PM2.5 (IEA, 2016), and
the majority of the population faces exposure of more than 35 μg/m3, i.e., above the highest
Target Level 1 defined by the World Health Organization (WHO).
• If no additional measures are taken to change the ongoing regular air pollution crises,
deaths from air pollution in India will rise from 1.1 million in 2015 to 1.7 million deaths
annually in 2030 and 3.6 million deaths annually by 2050 (HEI, 2019).
Exposure to air pollution costs the world’s economy some 5.1
trillion USD per year in welfare losses
INDIA: 2013 welfare losses equivalent to 7.7% of GDP
Source: World Bank (2016)
India has the most polluted cities on earth
Average level of fine particulate matter (PM2.5) pollution in 2018
94 93
87 90 89 87
131
143
172
149
120
105
98
173
138
120
101
144 146
92
0
20
40
60
80
100
120
140
160
180
µg/m
3
Source: WHO Global Ambient Air Quality Database (update 2018)
India has the most polluted cities on earth
Average level of fine particulate matter (PM2.5) pollution in 2018
94 93
87 90 89 87
131
143
172
149
120
105
98
173
138
120
101
144 146
92
0
20
40
60
80
100
120
140
160
180
µg/m
3
Source: WHO Global Ambient Air Quality Database (update 2018)
NAAQS
WHO
guideline
The Methodological Approach: Soft linking GCAM-IIMA and GAINS
Buildings Industry Transport
Air quality management needs to address urban and rural areas
• While current ambient PM2.5 monitoring in India reveals high levels in urban areas, remote sensing, comprehensive
air quality modelling and emission inventories suggest large-scale exceedances of the NAAQS also in rural areas.
• Household fuel combustion, small industries, burning of garbage and agricultural waste, etc., cause high emissions in
rural areas too.
• Pollution from rural areas is transported into the cities (and vice versa), where it constitutes a significant share of
pollution.
Emission densities of PM2.5, 2015
Source: IIASA/GAINS
Computed ambient levels of PM2.5
Satellite-derived PM2.5
Source: NASA Source: IIASA/GAINS
PM
2.5
(kt/year)
Effective solutions require regional cooperation
between cities and States
• A large share of PM2.5 in ambient
air originates from sources outside
of cities and from other States,
which are beyond the immediate
jurisdictions of cities.
• Cost-effective strategies require
regionally coordinated approaches,
and need to address urban and
rural emission sources.
0
20
40
60
80
100
120
PM
2.5
(µg/m³)
Natural sources Outside India Other India Neighboring States This State
NAAQS
WHO
guideline
Origin of (population-weighted) PM2.5 concentrations in ambient air 2015
Source: IIASA/CEEW – Purohit et al. (2019)
Source-apportionment of PM2.5 in Delhi NCT
0
20
40
60
80
100
120
140
µg/m
3
PM2.5
Origin
Diesel soot
Road dust, tyr
Fireworks, cre
Trash burning
Cookstoves
Small industri
High stacks po
Secondary ino
Agricultural N
Agricultural w
Soils and vege
0
20
40
60
80
100
120
140
µg/m
3
PM2.5
Diesel soot
Road dust, tyre wear, brakes
Fireworks, cremation, etc.
Trash burning, BBQ, smoking
Cookstoves
Small industries
High stacks power & industry
Secondary inorganic PM:
Agricultural NH3 with SO2/NOx
Agricultural waste burning
Soils and vegetation
Emission controls:
• Bharat IV from 2010
• CNG for buses and three-wheelers
• Enhanced penetration of natural gas
• Improved public transport
Source: IIASA/NEERI – Amann & Purohit et al. (2017); Bhanarkar & Purohit et al. 2018
Effective solutions must address all sources that contribute to PM2.5 formation
0
20
40
60
80
100
120
Delhi
West
Bengal
Haryana
Uttar
Pradesh
Jharkhand
Bihar
Punjab
Gujarat
Odisha
Rajasthan
Chattisgarh
Maharashtra
Madhya
Pradesh
Uttarakhand
North
East
Andhra
Pradesh**
Goa
Assam
Karnataka
Kerala
Tamil
Nadu
Jammu,
Kashmir
Himachal
Pradesh
PM
2.5
(µg/m³)
Natural sources Secondary PM2.5* Power stations
Other high stacks Households Transport
Waste Agriculture Other
NAAQS
WHO
guideline
• A significant share of emissions still
originates from sources associated with
poverty and underdevelopment (i.e.
solid fuel use in households and waste
management practices).
• Any effective reduction of PM2.5 levels in
ambient air and the resulting health
burden needs to balance emission
controls across all these source sectors.
• A focus on single sources alone will not
deliver effective improvements and is
likely to waste economic resources to
the detriment of further economic and
social development.
*Secondary particles formed in the atmosphere from agricultural NH3 emissions
through chemical reactions with SO2 and/or NOx emissions;
**Including Telangana
Source: IIASA/CEEW – Purohit et al. (2019)
Macro-economic development and energy consumption
0%
200%
400%
600%
800%
1000%
2010 2020 2030 2040 2050
relative
to
2015
GDP Primary energy consumption
GDP/Capita Population
CO2 emissions CO2 emissions/Capita
0
20
40
60
80
100
120
2010 2020 2030 2040 2050
EJ/year
Coal Oil Gas Biomass Renewables (excl. biomass) Nuclear
Compliance with current legislations will be essential
for stabilizing pollution levels as the economy grows
2015 2030 with
current
legislations
Computed ambient levels of PM2.5
• Current emission controls are effective, but their impacts are compensated by rapid economic growth.
• By 2030, effective implementation and enforcement of the 2018 legislation could allow a three-fold increase in
GDP without further deteriorating air quality.
Source: IIASA/CEEW – Purohit et al. (2019)
Policies and measures are available that could bring air quality more
in compliance with the NAAQS
-Advanced Emission Control Technology Scenario
2015 2030 with
current
legislations
Computed ambient levels of PM2.5
• Advanced technical emission controls can deliver additional air quality improvements, but will not be
sufficient to achieve the NAAQS everywhere
– NAAQS-compliant air quality to 60% of the Indian population
2030 with
advanced
controls
Source: IIASA/CEEW – Purohit et al. (2019)
Policies and measures are available that could bring air quality
more in compliance with the NAAQS
-Sustainable Development Scenario
2015 2030 with
current
legislations
Computed ambient levels of PM2.5
2030 with
development
measures
• A package of development measures that are usually taken for other policy priorities can deliver
significant co-benefits on air quality.
– NAAQS-compliant air quality to about 85% of the Indian population.
Source: IIASA/CEEW – Purohit et al. (2019)
Policies and measures are available that could bring air quality
more in compliance with the NAAQS (Contd…)
Source: IIASA/CEEW – Purohit et al. (2019)
Air pollutant emission control costs
0.0%
0.2%
0.4%
0.6%
0.8%
1.0%
1.2%
1.4%
1.6%
1.8%
0
50
100
150
200
250
2015
2015
measures
2018
legislation
Advanced
technology
Development
measures
2015
measures
2018
legislation
Advanced
technology
Development
measures
%
of
GDP
Billion
Euro/year
Power sector Industry Residential Mobile sources Others % of GDP
2030 2050
• Air pollution emission control costs
accounted for about 0.7% of the
GDP in 2015. This share will
increase to 1.4-1.7% of GDP in
2030. More than 80% of total costs
emerged for mobile sources.
• In 2050, with an almost 10-fold
increase in GDP, air pollution
controls will consume 1.1-1.5% of
the GDP.
Source: IIASA/CEEW – Purohit et al. (2019)
0.0%
0.2%
0.4%
0.6%
0.8%
1.0%
1.2%
Uniform application of
advanced end-of-pipe
technologies
Same health impacts,
GAINS cost-effectiveness
optimization
Costs
of
future
air
pollution
measures
in
2030
(%
of
GDP)
Power generation Industry Domestic Transport Other
• Full application of
advanced emission control
technologies can reduce
health impacts in India by
53% in 2030
• The GAINS optimization
can identify the most cost-
effective portfolio of
measures – these achieve
the same health
improvements at 45% of
the costs
Emission control costs for reducing
PM health impacts in India by 53%
With GAINS
optimization
The GAINS cost-effectiveness approach can reduce costs
for improving air quality by up to 55%
Source: IIASA/TERI – Purohit et al. (2010)
Sustainable development measures can deliver a wide range of benefits
0%
50%
100%
150%
200%
250%
300%
350%
2015 2030 2050 2015 2030 2050 2015 2030 2050 2015 2030 2050
CO₂ CH₄ All GHGs BC
relative
to
2015
emissions
2018 legislation Advanced technology Development measures
• In the sustainable development
scenario, India’s CO2 emissions
would be about 60% lower in
2050 than in the baseline case.
• Even without dedicated
measures focused on methane,
CH4 emissions would be 40%
lower in 2050 compared to the
baseline case.
• Black carbon emissions would
decline by 80% in the
development scenario in 2050
compared to 2015.
Source: IIASA/CEEW – Purohit et al. (2019)
Priority measures
• Access to clean fuels and technologies for cooking (e.g., promotion of LPG/electric stoves)
• Effective implementation of current policy measures (e.g., FGD in power plants, BS-VI from 2020)
• Improved waste management and agricultural production practices
• Substituting coal with natural gas and renewables (solar/wind) in power generation and industry
• Improvements in energy efficiency (power, industry, transport and residential/commercial)
• Advanced emission controls (e.g., HED and ESP Stage-II for PM and SCR for NOx control in power plants)
• Enhanced public transport (e.g., metro) and increased incentives for greater adoption of electric vehicles
• Emission control on non-industrial sources (e.g., road dust)
• Coordination of urban, rural and inter-State responses
The GAINS tool is available online to explore cost-effective strategies
that maximize multiple benefits
Access on the Internet:
http://gains.iiasa.ac.at
Thank you!
purohit@iiasa.ac.at

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purohit_igp_19.10.2020_v1.pptx

  • 1. The GAINS (Greenhouse gas - Air Pollution INteractions and Synergies) Model Pallav PUROHIT (E-mail: purohit@iiasa.at) IIASA - Air Quality and Greenhouse Gases (AIR) Program GAINS IGP Training Session 19 October 2020
  • 2. National emission ceilings Decision making on air quality management Policy targets Optimization Emissions Emission control options: ~2000 measures, co-control of 10 air pollutants and 6 GHGs) Atmospheric dispersion Costs Health, ecosystems and climate impact indicators The GAINS Model Energy activity projections • Global • IEA/WEO, IEA/ETP, POLES, MESSAGE, LEAP, etc. • Regional • PRIMES, AIMS • National • IIMA – AIMS, GCAM/IIMA, MARKAL; • TERI – MARKAL; • IRADe – CGE model; • CEEW - GCAM/IIMA; • NITI Aayog – MESSAGEix • CSTEP
  • 3. GAINS India: 23 Administrative regions ANPR: Andhra Pradesh (including Telangana); ASSA: Assam; BENG: West Bengal; BIHA: Bihar; CHHA: Chhattisgarh; DELH: Delhi NCT; EHIM: North East (excl. Assam); GOA: Goa; GUJA: Gujarat; HARY: Haryana; HIPR: Himachal Pradesh; JHAR: Jharkhand; KARN: Karnataka; KERA: Kerala; MAHA: Maharashtra; MAPR: Madhya Pradesh; ORIS: Odisha; PUNJ: Punjab; RAJA: Rajasthan; TAMI: Tamil Nadu; UTAN: Uttarakhand: UTPR: Uttar Pradesh; WHIM: Jammu and Kashmir. EHIM: Arunachal Pradesh, Manipur, Meghalaya, Mizoram, Nagaland, Sikkim and Tripura.
  • 5. CD-LINKS fuel ← Biomass ← OS1 OS2 Coal ← HC1 HC2 HC3 BC1 BC2 DC Gases ← GAS Liquids ← MD GSL LPG HF Electricity ← ELE Heat ← HT Geothermal ← GTH Solar ← STH Biomass ← OS1 OS2 Coal ← HC1 HC2 HC3 BC1 BC2 DC Gases ← GAS Liquids ← MD GSL LPG HF Electricity ← ELE Heat ← HT Other ← GTH Other ← STH Biomass ← OS1 OS2 Coal ← HC1 HC2 HC3 BC1 BC2 DC Gas ← GAS Oil ← MD GSL LPG HF Nuclear ← NUC Hydro ← HYD Geothermal ← GTH Solar ← SPV STH Wind ← WND Biomass ← (included in mineral oil products) Coal ← HC1 HC2 HC3 BC1 BC2 DC Gases ← GAS Oil ← MD GSL LPG HF Electricity ← ELE Hydrogen ← H2 CD-LINKS sector GAINS fuel GAINS sector Final Energy Residential (DOM_RES) Services (DOM_COM) Domestic others (DOM_OTH) Chemical industry boilers (IN_CHEM_BO) Conversion Sector Boilers (IN_CON_BO) Other Industry Boilers (IN_OTH_BO) Final Energy Paper & Pulp (IN_PAP_OC) Paper & Pulp Boilers (IN_PAP_BO) Non-Metalic Minerals (IN_NMM_OC) IGCCplants (PP_IGCC) Inland navigation (TRA_OT_INW) Maritime (TRA_OTS) Domestic aviation (TRA_OT_AIR) Primary Energy Existing power plants (PP_EX_OTH) New plants (PP_NEW) Advanced plants (PP_MOD) Final energy Off-road 2-&4- stroke sources (TRA_OT_LD, TRA_OT_LB) Off-road machinery and construction (TRA_OT_CNS) Agriculture (TRA_OT_AGR) Engines/DG-sets (PP_ENG) Transport Iron & Steel (IN_ISTE_OC) Chemical industry (IN_CHEM_OC) Non-Ferrous Metals (IN_NFME_OC) Other Industry (IN_OTH_OC) Rail (TRA_OT_RAI) Two-wheelers 2- &4-stroke (TRA_RD_LD2, TRA_RD_M4) Cars (TRA_RD_LD4C) Light-duty cars (TRA_RD_LD4T) Buses (TRA_RD_HDB) Heavy-duty trucks (TRA_RD_HDT) Residential and Commercial Industry Input to Power sector incl. CCS Mapping to the GAINS structure: Example
  • 6. Household energy end-use activities Fuel use for household cooking • Cooking • Heating (water + space) • Lighting (electricity/kerosene) • Heating and cooling • Air conditioners/Desert cooler/Fan • Refrigerators/Freezer • Electric heaters • Ironing (cloths) • Other • Washing machines • Radio/VCR/VCD Player/TV/Laptop/Mobile, etc. • Solid fuels • Fuelwood, agri-residues, cow dung, lignite/coal, charcoal • Liquid fuels • Kerosene, LPG • Gaseous fuels • NG, Biogas, Producer gas • Electricity • Solar (thermal) • Box/Concentrator type Household energy
  • 7.  Annual primary energy requirement for cooking • APEcooking = 365*Afw*CVfw  Annual useful energy requirement for cooking (annual) • AUEcooking = 365*Afw*CVfw*ηstove,fw • (5*18*13.5% = 12.15) o Calorific value of fuelwood (MJ/kg) o Efficiency of traditional cookstove (%) o Average fuelwood consumption (kg/HH/day) Household energy consumption for cooking  Daily useful energy requirement for cooking was 12.13 MJ/HH/Day (ABE, 1984)  An average of 138 kg of LPG is required per household per annum to meet their cooking energy needs • ≈9–10 LPG cylinders of 14.2 kg each in a year (IISD/IRADe, 2016) • ≈11.3 to 12.5 MJ/HH/Day
  • 8. 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% INDIA JAMMU & KASHMIR HIMACHAL PRADESH PUNJAB CHANDIGARH UTTARAKHAND HARYANA NCT OF DELHI RAJASTHAN UTTAR PRADESH BIHAR SIKKIM ARUNACHAL PRADESH NAGALAND MANIPUR MIZORAM TRIPURA MEGHALAYA ASSAM WEST BENGAL JHARKHAND ODISHA CHHATTISGARH MADHYA PRADESH GUJARAT DAMAN & DIU DADRA & NAGAR HAVELI MAHARASHTRA ANDHRA PRADESH KARNATAKA GOA LAKSHADWEEP KERALA TAMIL NADU PUDUCHERRY A. & N. ISLANDS RURAL 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% INDIA JAMMU & KASHMIR HIMACHAL PRADESH PUNJAB CHANDIGARH UTTARAKHAND HARYANA NCT OF DELHI RAJASTHAN UTTAR PRADESH BIHAR SIKKIM ARUNACHAL PRADESH NAGALAND MANIPUR MIZORAM TRIPURA MEGHALAYA ASSAM WEST BENGAL JHARKHAND ODISHA CHHATTISGARH MADHYA PRADESH GUJARAT DAMAN & DIU DADRA & NAGAR HAVELI MAHARASHTRA ANDHRA PRADESH KARNATAKA GOA LAKSHADWEEP KERALA TAMIL NADU PUDUCHERRY A. & N. ISLANDS URBAN State-wise distribution of households by type of fuel used for cooking in rural and urban areas in India Source: Census (2011)
  • 9.  Annual primary energy demand for cooking (APEcooking) 𝐴𝑃𝐸𝑐𝑜𝑜𝑘𝑖𝑛𝑔 = 365 𝑖=𝑗=1 𝑚,𝑛 𝑁𝑖,𝑗𝜉𝑖,𝑗𝑈𝐸𝑐𝑜𝑜𝑘𝑖𝑛𝑔− 𝑖,𝑗 𝜂𝑠𝑡𝑜𝑣𝑒,𝑖 Where Ni,j = Number of households using ith fuel in jth State/UT ξi,j = % of households using ith fuel in jth State/UT ηstove,i = Efficiency of utilization of ith fuel  Data sources  Census of India;  NSSO;  CSO;  NCAER;  Demographic and Health Survey (DHS)/IIPS Household energy demand for cooking in India
  • 10. o Annual kerosene consumption (AKClighting) for lighting in GAINS region “i” in year “y” is estimated by using the following ex-pression: 𝐴𝐾𝐶𝑙𝑖𝑔ℎ𝑡𝑖𝑛𝑔 = 𝑃𝑂𝑃𝑖.𝑦 𝐻𝐻𝑆𝑖.𝑦 (1 − 𝐸𝐿𝐸𝑖.𝑦)365 𝑗=1 𝑛 𝑁𝑖,𝑗,𝑦ℎ𝑖,𝑗,𝑦𝐶𝑉𝑘𝑓𝑖,𝑗,𝑦 𝑆𝐶𝑗 o where • POP = population, • HHS = household size, • ELE = electrification rate, • f = share of device type “j” (either wick lamps or hurricane lanterns), • N = number of kerosene lamps, • h = daily operating hours, • SC = specific kerosene consumption of a device • CVk = calorific value of kerosene Kerosene lighting
  • 11. Diesel generators  Fossil fuel-burning backup generators in developing countries produce as much energy as 700-1,000 coal-fired power stations, consume US$50 billion in annual spending, and emit dangerous chemicals into homes and businesses.  Data and Information gaps  Number of diesel generators (residential, commercial, industry, agriculture, etc.)  Capacity factor  Age (New/Old)  Type (Large/small)
  • 12. Application rates of abatement measures: % of capacity/activity 0 20 40 60 80 100 2010 2020 2030 2040 2050 JAPAN - Heavy Duty Diesel Vehicles control (%) EURO I EURO II EURO III EURO IV EURO V EURO VI EURO VII 0 20 40 60 80 100 2010 2020 2030 2040 2050 CHINA - Power sector - SO2 control (%) High efficiency flue gases desulphurisation Wet flue gases desulphurisation Wet flue gases desulphurisation (retrofitted) In-furnace control - limestone injection Low sulphur coal (0.6 %S) 0 20 40 60 80 100 2010 2020 2030 2040 2050 INDIA - Power sector - PM2.5 control (%) High efficiency deduster Electrostatic precipitator: 2 fields Electrostatic precipitator: 1 field
  • 13. What is a GAINS control strategy? • A set of numbers (weighted averages) that tell you for each emission source to what extent which control technology is being applied Represents what kind of technologies are used Represents what policies are planned or implemented, and how this changes over time • For each technology: value is between 0% and 100% • Sum over all technologies (incl. ‘no control’) = 100% o Total activity is either controlled or not o % is always relative to activity o For power plants activity means energy input
  • 14. How do I calculate a control strategy? Example: Coal-fired power plants 500 MWel 250 MWel STEP 1: Start with capacities: Total = 800 MWel 50 MWel
  • 15. How do I calculate a control strategy? 500 MWel 250 MWel 50 MWel Step 2: Calculate fuel input per year, using • Operating hours per year • Conversion efficiency 4,000 hours/yr, 35% efficiency 2,000 hours/yr, 30% efficiency 6,000 hours/yr, 32% efficiency 20.6 PJ/yr = 69% 6.0 PJ/yr = 20% 3.4PJ/yr = 11%
  • 16. How do I calculate a control strategy? Step 3: Determine control technology in operation 20.6 PJ/yr = 69% 6.0 PJ/yr = 20% 3.4PJ/yr = 11% e.g. flue gas desulfurization e.g. lime stone injection e.g. no control
  • 17. How do I calculate a control strategy? 1 500 20.6 1 250 6.0 1 50 3.4 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% Number of plants Capacity Fuel input Plant C Plant B Plant A Apply control strategy here
  • 18. How do I calculate a control strategy? 1 500 20.6 1 250 6.0 1 50 3.4 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% Number of plants Capacity Fuel input Plant C Plant B Plant A Flue gas desulphurization = 69% Lime stone injection = 20% No control = 11%
  • 19. Pathways towards clean air in India Pallav PUROHIT (E-mail: purohit@iiasa.at) IIASA - Air Quality and Greenhouse Gases (AIR) Program GAINS IGP Training Session 19 October 2020
  • 20. Air Pollution & Health • Air pollution poses a major threat to human health and climate. The combined effects of ambient and household air pollution cause about 7 million premature deaths every year (UN, 2019), largely as a result of increased mortality from stroke, heart disease, chronic obstructive pulmonary disease, lung cancer and acute respiratory infections. • Exposure to ambient particulate matter is a leading risk factor for environmental public health in India. It is estimated that only about 1% of the Indian population is exposed to less than the global WHO guideline level of 10 μg/m3 annual mean PM2.5 (IEA, 2016), and the majority of the population faces exposure of more than 35 μg/m3, i.e., above the highest Target Level 1 defined by the World Health Organization (WHO). • If no additional measures are taken to change the ongoing regular air pollution crises, deaths from air pollution in India will rise from 1.1 million in 2015 to 1.7 million deaths annually in 2030 and 3.6 million deaths annually by 2050 (HEI, 2019).
  • 21. Exposure to air pollution costs the world’s economy some 5.1 trillion USD per year in welfare losses INDIA: 2013 welfare losses equivalent to 7.7% of GDP Source: World Bank (2016)
  • 22. India has the most polluted cities on earth Average level of fine particulate matter (PM2.5) pollution in 2018 94 93 87 90 89 87 131 143 172 149 120 105 98 173 138 120 101 144 146 92 0 20 40 60 80 100 120 140 160 180 µg/m 3 Source: WHO Global Ambient Air Quality Database (update 2018)
  • 23. India has the most polluted cities on earth Average level of fine particulate matter (PM2.5) pollution in 2018 94 93 87 90 89 87 131 143 172 149 120 105 98 173 138 120 101 144 146 92 0 20 40 60 80 100 120 140 160 180 µg/m 3 Source: WHO Global Ambient Air Quality Database (update 2018) NAAQS WHO guideline
  • 24. The Methodological Approach: Soft linking GCAM-IIMA and GAINS Buildings Industry Transport
  • 25. Air quality management needs to address urban and rural areas • While current ambient PM2.5 monitoring in India reveals high levels in urban areas, remote sensing, comprehensive air quality modelling and emission inventories suggest large-scale exceedances of the NAAQS also in rural areas. • Household fuel combustion, small industries, burning of garbage and agricultural waste, etc., cause high emissions in rural areas too. • Pollution from rural areas is transported into the cities (and vice versa), where it constitutes a significant share of pollution. Emission densities of PM2.5, 2015 Source: IIASA/GAINS Computed ambient levels of PM2.5 Satellite-derived PM2.5 Source: NASA Source: IIASA/GAINS PM 2.5 (kt/year)
  • 26. Effective solutions require regional cooperation between cities and States • A large share of PM2.5 in ambient air originates from sources outside of cities and from other States, which are beyond the immediate jurisdictions of cities. • Cost-effective strategies require regionally coordinated approaches, and need to address urban and rural emission sources. 0 20 40 60 80 100 120 PM 2.5 (µg/m³) Natural sources Outside India Other India Neighboring States This State NAAQS WHO guideline Origin of (population-weighted) PM2.5 concentrations in ambient air 2015 Source: IIASA/CEEW – Purohit et al. (2019)
  • 27. Source-apportionment of PM2.5 in Delhi NCT 0 20 40 60 80 100 120 140 µg/m 3 PM2.5 Origin Diesel soot Road dust, tyr Fireworks, cre Trash burning Cookstoves Small industri High stacks po Secondary ino Agricultural N Agricultural w Soils and vege 0 20 40 60 80 100 120 140 µg/m 3 PM2.5 Diesel soot Road dust, tyre wear, brakes Fireworks, cremation, etc. Trash burning, BBQ, smoking Cookstoves Small industries High stacks power & industry Secondary inorganic PM: Agricultural NH3 with SO2/NOx Agricultural waste burning Soils and vegetation Emission controls: • Bharat IV from 2010 • CNG for buses and three-wheelers • Enhanced penetration of natural gas • Improved public transport Source: IIASA/NEERI – Amann & Purohit et al. (2017); Bhanarkar & Purohit et al. 2018
  • 28. Effective solutions must address all sources that contribute to PM2.5 formation 0 20 40 60 80 100 120 Delhi West Bengal Haryana Uttar Pradesh Jharkhand Bihar Punjab Gujarat Odisha Rajasthan Chattisgarh Maharashtra Madhya Pradesh Uttarakhand North East Andhra Pradesh** Goa Assam Karnataka Kerala Tamil Nadu Jammu, Kashmir Himachal Pradesh PM 2.5 (µg/m³) Natural sources Secondary PM2.5* Power stations Other high stacks Households Transport Waste Agriculture Other NAAQS WHO guideline • A significant share of emissions still originates from sources associated with poverty and underdevelopment (i.e. solid fuel use in households and waste management practices). • Any effective reduction of PM2.5 levels in ambient air and the resulting health burden needs to balance emission controls across all these source sectors. • A focus on single sources alone will not deliver effective improvements and is likely to waste economic resources to the detriment of further economic and social development. *Secondary particles formed in the atmosphere from agricultural NH3 emissions through chemical reactions with SO2 and/or NOx emissions; **Including Telangana Source: IIASA/CEEW – Purohit et al. (2019)
  • 29. Macro-economic development and energy consumption 0% 200% 400% 600% 800% 1000% 2010 2020 2030 2040 2050 relative to 2015 GDP Primary energy consumption GDP/Capita Population CO2 emissions CO2 emissions/Capita 0 20 40 60 80 100 120 2010 2020 2030 2040 2050 EJ/year Coal Oil Gas Biomass Renewables (excl. biomass) Nuclear
  • 30. Compliance with current legislations will be essential for stabilizing pollution levels as the economy grows 2015 2030 with current legislations Computed ambient levels of PM2.5 • Current emission controls are effective, but their impacts are compensated by rapid economic growth. • By 2030, effective implementation and enforcement of the 2018 legislation could allow a three-fold increase in GDP without further deteriorating air quality. Source: IIASA/CEEW – Purohit et al. (2019)
  • 31. Policies and measures are available that could bring air quality more in compliance with the NAAQS -Advanced Emission Control Technology Scenario 2015 2030 with current legislations Computed ambient levels of PM2.5 • Advanced technical emission controls can deliver additional air quality improvements, but will not be sufficient to achieve the NAAQS everywhere – NAAQS-compliant air quality to 60% of the Indian population 2030 with advanced controls Source: IIASA/CEEW – Purohit et al. (2019)
  • 32. Policies and measures are available that could bring air quality more in compliance with the NAAQS -Sustainable Development Scenario 2015 2030 with current legislations Computed ambient levels of PM2.5 2030 with development measures • A package of development measures that are usually taken for other policy priorities can deliver significant co-benefits on air quality. – NAAQS-compliant air quality to about 85% of the Indian population. Source: IIASA/CEEW – Purohit et al. (2019)
  • 33. Policies and measures are available that could bring air quality more in compliance with the NAAQS (Contd…) Source: IIASA/CEEW – Purohit et al. (2019)
  • 34. Air pollutant emission control costs 0.0% 0.2% 0.4% 0.6% 0.8% 1.0% 1.2% 1.4% 1.6% 1.8% 0 50 100 150 200 250 2015 2015 measures 2018 legislation Advanced technology Development measures 2015 measures 2018 legislation Advanced technology Development measures % of GDP Billion Euro/year Power sector Industry Residential Mobile sources Others % of GDP 2030 2050 • Air pollution emission control costs accounted for about 0.7% of the GDP in 2015. This share will increase to 1.4-1.7% of GDP in 2030. More than 80% of total costs emerged for mobile sources. • In 2050, with an almost 10-fold increase in GDP, air pollution controls will consume 1.1-1.5% of the GDP. Source: IIASA/CEEW – Purohit et al. (2019)
  • 35. 0.0% 0.2% 0.4% 0.6% 0.8% 1.0% 1.2% Uniform application of advanced end-of-pipe technologies Same health impacts, GAINS cost-effectiveness optimization Costs of future air pollution measures in 2030 (% of GDP) Power generation Industry Domestic Transport Other • Full application of advanced emission control technologies can reduce health impacts in India by 53% in 2030 • The GAINS optimization can identify the most cost- effective portfolio of measures – these achieve the same health improvements at 45% of the costs Emission control costs for reducing PM health impacts in India by 53% With GAINS optimization The GAINS cost-effectiveness approach can reduce costs for improving air quality by up to 55% Source: IIASA/TERI – Purohit et al. (2010)
  • 36. Sustainable development measures can deliver a wide range of benefits 0% 50% 100% 150% 200% 250% 300% 350% 2015 2030 2050 2015 2030 2050 2015 2030 2050 2015 2030 2050 CO₂ CH₄ All GHGs BC relative to 2015 emissions 2018 legislation Advanced technology Development measures • In the sustainable development scenario, India’s CO2 emissions would be about 60% lower in 2050 than in the baseline case. • Even without dedicated measures focused on methane, CH4 emissions would be 40% lower in 2050 compared to the baseline case. • Black carbon emissions would decline by 80% in the development scenario in 2050 compared to 2015. Source: IIASA/CEEW – Purohit et al. (2019)
  • 37. Priority measures • Access to clean fuels and technologies for cooking (e.g., promotion of LPG/electric stoves) • Effective implementation of current policy measures (e.g., FGD in power plants, BS-VI from 2020) • Improved waste management and agricultural production practices • Substituting coal with natural gas and renewables (solar/wind) in power generation and industry • Improvements in energy efficiency (power, industry, transport and residential/commercial) • Advanced emission controls (e.g., HED and ESP Stage-II for PM and SCR for NOx control in power plants) • Enhanced public transport (e.g., metro) and increased incentives for greater adoption of electric vehicles • Emission control on non-industrial sources (e.g., road dust) • Coordination of urban, rural and inter-State responses
  • 38. The GAINS tool is available online to explore cost-effective strategies that maximize multiple benefits Access on the Internet: http://gains.iiasa.ac.at Thank you! purohit@iiasa.ac.at