emissions of air pollutants from power plants in … of air pollutants from power plants in china...
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Emissions of air pollutants from power plants in China
Shuxiao Wang, Jiming Hao
Tsinghua University
October 9, 2012
Outline
2
Historical evolution of China’s power sector
Emission projection up to 2030
Issues and questions to be addressed
Power sector is the largest coal user in China
Source: China Statistical Yearbook, 2011
In 2010, power plants burned 1527 Mt coal, accounting for 50% of total coal consumption in China.
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020000400006000080000
100000120000140000160000
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009年份
原煤
消耗
量/万
吨
Power sector is the largest emitter of SO2 and NOx
Wang et al., Atmospheric Environment, 2011, 45: 6347-6358
In 2005, China’s power plants emitted 55% of SO2 and 38% of NOx.
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0
5000
10000
15000
20000
25000
30000
SO2 NOx PM2.5
Em
issi
ons o
f air
pol
luta
nts,
kt
Open BiomassBurningTransportation
Domestic sources
Industrial Process
Industrial Combustion
Power Plants
1996ChinaSO2:1200-2100mg/m3
NOx:650-1000mg/m3
PM: 200mg/m3
2002BeijingSO2:100-150mg/m3
PM:50mg/m3
2003ChinaSO2: 400-1200mg/m3
NOx:450-1000mg/m3
PM: 50mg/m3
2007BeijingSO2:50mg/m3
NOx:150-250mg/m3
SO2:10mg/m3
2011ChinaSO2:200mg/m3
NOx:100-200mg/m3
PM: 30mg/m3
5
Evolution of emission standard for power sector
Emission standard of air pollutants for thermal power plants
Application of FGD in China’s power plantsIn
stal
latio
n ca
paci
ty, G
W
1000
800
600
400
200
0 Rat
io o
f FG
D in
stal
latio
n, %
Capacity of coal-fired power plants (China) Capacity of FGD installation (China)
Capacity of power plants (US)FGD capacity (US )FGD ratio (China)FGD ratio (US)
6Wang and Hao. Journal of Environmental Sciences, 2012
Application of NOx control technology
The capacity of operating flue gas deNOx units, mainly SCR, was over 140 GW by the end of 2010, accounting for 18% of the total coal-fired power units.
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020406080
100120140160
2005 2006 2007 2008 2009 2010
Inst
alla
tion
of D
eNO
x te
chno
logy
, GW
SNCR SCR
After late 1990’s, power plants with capacity >=300 MW installed advanced LNBs;
All power plants built after Jan. 1st 2004 installed advanced LNBs.
Wang and Hao. Journal of Environmental Sciences, 2012
Emission from China’s power plants: 2005-2010
8
0.002.004.006.008.00
10.0012.0014.00
SO2 NOX PM10 PM2.5
Air
pol
luta
nts
emis
sion
s, M
t 2005 2006 2007 2008 2009 2010
0.00.20.40.60.81.0
SO2 NOX PM10 PM2.5
Evo
lutio
n of
em
issi
on fa
ctor
s, %
2005 2006 2007 2008 2009 2010 GAINS
Outline
9
Historical evolution of China’s power sector
Emission projection up to 2030
Issues and questions to be addressed
Assumptions on future emission scenarios
Energy scenario Energy scenario definition Pollution control scenario
definition
Business as usual(BAU)
Current legislation and compliance (till the end of 2010) are assumed. CO2 intensity will be 40%-45% lower in 2020 than that of 2005.
Current legislation and compliance (till the end of 2010) are assumed.
Alternative policy(PC)
New energy-saving policies are enforced, including life style changes, structural adjustment and energy efficiency improvement.
New air pollution control policies are released and implemented, representing the “best guess” of future environmental policies.
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Driving forces of China’s power generation
Item 2010BAU PC
2020 2030 2020 2030
GDP (2005 price)/109 CHY 31165 65741 117718 65741 117718
Population/billion 1.340 1.440 1.474 1.440 1.474
Urbanization rate/% 49.7 58.0 63.0 58.0 63.0
Power generation/TWh 4205 6690 8506 5598 7457
Thermal efficiency of coal-fired power/% 35.7 38.0 40.0 38.8 41.7
Crude steel yield/Mt 627 710 680 610 570
Cement yield/Mt 1880 2001 2050 1751 1751
Urban residential building area percapita/m2
23.0 29.0 33.0 27.0 29.0
Rural residential building area percapita/m2
34.1 39.0 42.0 37.0 39.0
Share of new and renewable energy/% a 7.5 8.3 8.9 11.9 15.8
a Including hydro power, solar energy, wind energy, ocean energy, and nuclear energy 11
Evolution of power generation technologies
12
Change of fuel consumption by power sector
13
Application of control technologies
SO2 control for coal-fired units
PM control for coal-fired units
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NOx control for coal-fired units
0%10%20%30%40%50%60%70%80%90%
100%
Shar
e of
con
trol
tech
nolo
gies
LNB+SCR LNB+SNCR LNB No Control
0%10%20%30%40%50%60%70%80%90%
100%
2005 2010 2020BAU2030BAU 2020PC 2030PC
Shar
e of
con
trol
tech
nolo
gies
No Control FGD
0%10%20%30%40%50%60%70%80%90%
100%
2005 2010 2020BAU 2030BAU 2020PC 2030PC
Shar
e of
con
trol
tech
nolo
gies
FFESPWETCYC
GAINS gives higher SO2 emissions in the base year. Projection by CLE-GAINS is higher, mainly because of its higher
forecast of coal consumption compared with PC-TU.
SO2
Future emissions of China’s power sector
15.8315.83
2.85
7.02
20.33
57.45
0.00
10.00
20.00
30.00
40.00
50.00
60.00
70.00
2005 2010 2015 2020 2025 2030
SO2E
MIS
SIO
N, M
t
BAU-TUPC-TUCLE-GAINSNFC-GAINS
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NOX
Future emissions of China’s power sector
4.94
13.74
6.51
2.32
4.94
10.95
0.00
2.00
4.00
6.00
8.00
10.00
12.00
14.00
16.00
2005 2010 2015 2020 2025 2030
NO
xEM
ISSI
ON
, Mt
NFC-GAINSBAU-TUPC-TUCLE-GAINS
GAINS gives lower NOx emissions in the base year. Projection by CLE-GAINS is similar to BAU-TU. NOx emissions can
be further reduced by 60% under PC-TU.16
PM2.5
Future emissions of China’s power sector
GAINS gives higher PM emissions in year 2010. Projection by CLE-GAINS is much higher than because it assumes
the PM emission factors will not change in the future.
2.83
0.690.41
2.43
0.00
0.50
1.00
1.50
2.00
2.50
3.00
2005 2010 2015 2020 2025 2030
PM2.
5EM
ISSI
ON
, Mt
NFC-GAINSBAU-TUPC-TUCLE-GAINS
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Hg
Future emissions of China’s power sector
Air pollution control measures (SCR) reduce Hg emissions by 75t ACT (accelerated control) strategy might reduce Hg emissions to 29%
of 2008 levels18
0
20
40
60
80
100
120
140
160
2008 2020 2030
Mer
cury
em
issi
on fr
om C
FPPs
in C
hina
(t)
Reference-BAUReference-EECReference-ACTAlternative-BAUAlternative-EECAlternative-ACT
Wang et al., Energy & Fuel, 2012
Outline
19
Historical evolution of China’s power sector
Emission projection up to 2030
Issues and questions to be addressed
Issues and questions
Possibility to consider the regional difference or national circumstances?Difference among the emission inventories in 2005Might be necessary to reflect the recent emission changes
(2005-2010) in some countries such as ChinaCarefully define “current legislation”Future activity levels of power sector
01000020000300004000050000600007000080000
2005 2010 2020 2030
Coa
l con
sum
ptio
n, p
j
IEA BAU-TU PC-TU
Issues and questions
Consider not only the emission reduction but also the cost of control technologies
Long-term research needs: cost-benefit analysis of various emission scenarios
020406080
100120140
2020 2030
Incr
ease
of c
ost,
billi
on
CN
Y
Power genration technologiesAir pollution control technologies
Cost for reduction of GHGs and air pollutants
negative cost technologies
GHGs and air pollutants reduction at unit cost/income in 2030positive cost technologies
23
Cost difference between BAU and PC
24
0
20
40
60
80
100
120
140
2020 2030
Incr
ease
of c
ost,
billi
on C
NY
Power genration technologiesAir pollution control technologies
Total cost by technology
25
Future work: cost-benefit analysis
Cost of NOx control of power plants in China during 2011-2015
104 CHY
Benefit of NOx control of power plants in China during 2011-2015
83.8 billion CHY 37 billion CHY
26
Future work: projection for other sources
Develop emission scenarios for other larger point sources,
including cement industry, iron & steel industry, etc.
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0.00
0.50
1.00
1.50
2.00
2.50
2005 2006 2007 2008 2009 2010 2011
Cem
ent p
rodu
ctio
n, b
illio
n to
ns shaft kilnPortland
Application of low NOx burners
Introduced low NOx burners (LNB) since early 1990’s; Power plants with capacity over 300 MW built after late 1990’s installed
advanced LNBs; All units built after Jan. 1st 2004 installed advanced LNBs.
第1时段, 75. 3%
第1时段, 71. 3%
第2时段, 94. 5%
第2时段, 91. 8%
第3时段, 100. 0%
第3时段, 100. 0%
0. 0% 10. 0% 20. 0% 30. 0% 40. 0% 50. 0% 60. 0% 70. 0% 80. 0% 90. 0% 100. 0%
台数比例
容量比例
28
Application of PM control technology
In 2010, 96% of power units installed ESP and 4% installed fabric filter.
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Comparison between China and United States
Both the coal consumption of unit power generation and SO2 emission factor are lower than that of the United States. But NOx emission factor is still high.
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
SO2 NOx PME
mis
sion
fact
or, g
/kW
h
ChinaUnited States
300310320330340350360370380390400
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
coal
con
sum
ptio
n of
pow
er
gene
ratio
n,g/
kWh
30
Emission reduction of various control measures
SCR – Selective Catalytic Reduction; SNCR - Selective Non-Catalytic Reduction; LNB –Low NOX combustion technologies; LSC – Life style change; STA – Structure adjustment.
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