Upload
nguyennhu
View
215
Download
1
Embed Size (px)
Citation preview
Rice Production and Methane
Reiner WassmannInternational Rice Research Institute
Coordinator of the Rice and Climate Rice and Climate Change Consortium Change Consortium
Reiner WassmannInternational Rice Research Institute
Coordinator of the Rice and Climate Rice and Climate Change Consortium Change Consortium
IRRI’s Previous Projects on Climate/ Climate Change
In 1961-62, studies on the effect of temperatureon rice in the growth chamber
In 1971-72, studies on the effect of CO 2 enrichment on rice in open -top chambers
Since 2006, Rice and Climate Change Consortiumas a platform for assessing mitigation, adaptationand regional impacts
1991-1999, studies on CH 4 emissions, Temp/CO 2 + UV-B effects and modeling
on rice in open -top chambers
Open-top chambers (Temp./ CO2 effects)
US-EPA project (1991-1995)
Closed chambers (Methane emissions)
Interregional Program on Methane Emissions from Ric e Fields (funded by UNDP/GEF, 1993-1999)
IrrigatedIrrigatedRainfedRainfedDeepwaterDeepwater
Temporal patterns under different amendments(IRRI, 1993 wet season)
30
em
issi
on (
mg
m-2 h
-1) Dular
shaded = no organic amenmentline = + 5 t/ha rice straw
emis
sion
rat
e (m
g C
H4
m-2
h-1)
Shaded = no organic amendmentLine = + rice straw (5t/ha)
0
10
20
-20 -4 5 14 23 33 41 51 64 73 85 95
days after transplanting
CH
4 em
issi
on (
mg
m
line = + 5 t/ha rice straw
0 20 40 60 80 100
days after transplanting
emis
sion
rat
e (m
g C
H
Wassmann et al. 2000
0
10
20
30
20 40 60 80 100 120-300
-200
-100
0
100
water level (cm) / line Eh (mV) / dots
1200
1400methane emission (mg CH4 m-2 d-1)
0
10
20
30
20 40 60 80 100 120-300
-200
-100
0
100
water level (cm) / line Eh (mV) / dots
1200
1400methane emission (mg CH4 m-2 d-1)
Mid-season drainage
Days after planting
0
200
400
600
800
1000
1200
20 40 60 80 100 1200
200
400
600
800
1000
1200
20 40 60 80 100 120
Field experiment at Hangzhou, China (Wassmann et al., 2000)
200
300
400
500
600
700
800
900
1,000
200
300
400
500
600
700
800
900
1,000
Wat
er (
mill
ion
cubi
c m
eter
s)
Wat
er (
mill
ion
cubi
c m
eter
s)
Figure 1: Zhanghe Irrigation System,
Hubei, China Annual Water Allocations
for Irrigation and Other Uses 1965-2008Annual Irrigation Water Supplied
Competition, some examples in rice areas….Zanghe Reservoir, China
0
100
0
100
1961 1966 1971 1976 1981 1986 1991 1996 2001 2006
Wat
er (
mill
ion
cubi
c m
eter
s)
Wat
er (
mill
ion
cubi
c m
eter
s)
Years1965 1975 1985 1995 2005
Angat Dam, Philippines
0
10
20
30
40
50
60
70
80
90
100
1968 1971 1974 1977 1980 1983 1986 1989 1992 1995 1998 2001 2004YEARS
SH
AR
E (
%)
AgriculturalNon-Agricultural
Alternate wetting and drying (AWD) Alternate wetting and drying (AWD)
NO N2O NO N2O
"hole-in-the-pipe“-Modell
NH4+-NH2OH-NO2
--NO3- NO3
--NO2--NO-N2O-N2
Nitrification Denitrification
Davidson, 1991
Davidson, 1991
(aerob) (anaerob)
‘Site-Specific Nutrient Management’ (SSNM)
� Applying nutrients as and when needed
� Adjusting nutrient application to crop needs in given location and season
Leaf Color Chart
8
10
12
14eq
. ha-1
bc
N2O
CH
GWP of CH4 and N2O under AWD
0
2
4
6
8
t CO
2eq
. ha
aa
a
ab
b
CH4
Urea 48-h
before irrig.
Urea 2-h
after irrig.
Urea 2-h
after irrig. +
flooding for
7 days
Continuously
flooded
‘Other’ mitigation options for rice
High-yielding, short duration cultivars
No Contradiction between High Yields and Low Methane Emissions
Field experiment in Maligaya/ Philippines
y = -81.4x + 744R2 = 0.94
0
100
200
300
400
500
600
0 2 4 6 8 10
Yield (t/ha)
Sea
sona
l CH
4 em
issi
on (
kgC
H4/
ha)
Dry season
Wet season
Linear WS and DS
Early Maturing Rice Cultivars Reduce Methane Emissions
100
200
300
400
500E
mis
sion
rat
e (m
g C
H4
m-2
d-1
) IR64
CisadaneWet season Dry season
0
02
Dec
IR64
Cisadane
PLANTING H A R V E S T
08 Mar
06 Apr
PLANTING H A R V E S T
28
May
IR64
Cisadane
17 Aug
01 Sep
Field experiment in Jakenan/ Indonesia (Setyanto et al. 2000)
Cisadane:116 kg CH4/ha
Cisadane:142 kg CH4/ha
IR64:128 kg CH4/ha
IR64:81 kg CH4/ha
‘Other’ mitigation options for rice
High-yielding, short duration cultivars
Biogas technology for organic inputs
Use of rice straw as biofuel
Effect of fermented manure (biogas residues)
30
40
50
60
emission rate (mg CH4 m-2 h-1)
Fied experiment in Hunan Province, China (Wassmann et al. 1993)
combinedmineral
organicfermented
early rice
late rice0
10
20
30
fertilizer
season
Use of Rice Straw as Renewable Energy
“Globally, wasted rice grain and rice straw could produce 221 GL of bioethanol, replacing 159 GL of gasoline (about 14.3% of global gasoline consumption).”
Source: Kim and Dale 2004
Technological options:• combustion• biogas technology (in combinationwith animal husbandry)
• bio-char technology and • conversion of rice straw to ethanol
‘Other’ mitigation options for rice
High-yielding, short duration cultivars
Biogas technology for organic inputs
Use of rice straw as biofuel
Modification of fertilizer type (e.g. sulfate)Modification of fertilizer type (e.g. sulfate)
Soil amendments (industrial byproducts suchas phosphogypsum, silicate iron slag)
Direct seeding (with appropriate watermanagement)
Submission to UNFCCC (Dec. 2009)
http://cdm.unfccc.int/UserManagement/FileStorage/BA913K6D7SZMW4LOTFXJQCNRHV2085
GHG Mitiga -
tion
Conceptual Approach
Water-saving
tion
High N use effi-
ciencyResilience to climate extremes