Transcript Document
Stable Isotope Analyses of
Carbon Dioxide Exchange in
Forest and Pasture Ecosystems
L. Flanagan, J. Ometto, T. Domingues,
L. Martinelli, J. Ehleringer
Atlanta LBA Ecology, February 12-14, 2001
Research Objectives:
To study effects of:
Environmental variation on forest carbon
dioxide and water vapor exchange
(Using C stable isotope measurements)
Land-use change on ecosystem stable
isotope discrimination
(Forest [C3] conversion to Pasture [C4])
Rationale for Expected
Environmental Effects on Forest
Physiology:
.
Manaus
1. Large seasonal
changes in
precipitation and
associated seasonal
drought
Precipitation, mm month
-1
300
200
100
0
2
4
6
8
10
Time, Month of Year
12
Rationale for Expected
Environmental Effects on Forest
Physiology:
2. El Nino/La Nina can
cause substantial
interannual variation
in precipitation
Stable Isotopes Provide Integrated
Eco-physiological Measurements
13C
measurements represent changes in the ratio of
stomatal conductance to photosynthetic capacity
Spatial and temporal integration depends on the
nature of the measurements:
Single leaves
Tree rings
Atmospheric CO2
The carbon isotope composition of plant tissues depends on
• d13Ca, atmospheric source
• a, 13CO2 diffusion rates relative to 12CO2
• b, enzymatic discrimination during carboxylation
• ci/ca, ratio of internal to ambient CO2
d13Cleaf = d13Ca - a - (b - a)•ci/ca
-8 ‰
4.4 ‰
27 ‰
0.4 - 0.9
d13Cleaf = d13Ca - a - (b - a)•ci/ca
This carbon isotope
discrimination occurs
continuously during
photosynthesis and
the resulting organic
carbon integrates over
the entire photosynthetic
period.
ci
ca
Precipitation
Soil Moisture
Stomatal
Conductance
Photosynthetic
Capacity
Leaf Ci/Ca
Carbon Isotope
Discrimination
-25
Leaf d13C, per mil
-35
Low
Water Availability
High
Sampling Atmospheric CO2
Stable Isotope Ratios
Increases the spatial integration of
Eco-Physiological information obtained
A Keeling Plot
Keeling Plot Technique Provides
an estimate of:
Spatially integrated changes in the ratio of stomatal
conductance to photosynthetic capacity
Spatial integration similar to E.C. footprint
Temporal integration: Days – Week
(primarily represents recently fixed carbon)
Santarem Km 83
September 2000
40
New Leaves
Old Leaves
Height, m
30
20
10
0
-38
-36
-34
13
-32
Leaf d C, ‰
-30
-28
.
Santarem Km 83
35
September 2000
9 am
12 noon
4 pm
9 am
12 noon
4 pm
30
Height, m
25
20
15
10
5
0
360
380
400
420
440
CO2 Concentration, mol mol
-12
-1
-11
-10
13
d C, ‰
-9
-8
13
Ecosystem Respiration d C, ‰
-25
Manaus
Santarem
-26
-27
-28
-29
-30
2
4
6 8 10 12 2
1999
4
6 8 10 12
2000
Time, Month of Year
C13 Ecosystem Respiration
(per mil)
Santarem
y = -0.0112x - 25.699
2
R = 0.8626
-25
-26
-27
-28
-29
-30
0
100
200
300
400
Monthly Precipitation (mm)
500
Land Use Change Effects
C
3
C
4
18O
in CO2 could be an important signal
for C3-C4 vegetation conversions
The 18O Content of Atmospheric CO2 in terrestrial
ecosystems is controlled by:
Discrimination during CO2 Assimilation
(equilibration with chloroplast water)
Release of Respiratory CO2 from Soils
(equilibration with soil water)
.
40
Ecosystem Respiration
d18O, ‰
30
20
Pasture
Forest
10
Forest
Pasture
0
-10
-20
Stem Water
2
4
6 8 10 12 2
1999
4
6 8 10 12
2000
Time, Month of Year
We expect differences between C3 and C4
plants for discrimination against C18O16O
because:
Leaf Water O-18 values
Ci/Ca differences
Carbonic Anhydrase Activity
C3 and C4 plants contribute different DC18O16O signals
Conclusions:
1. Significant temporal variation occurs in
d13C of forest respired carbon dioxide
Associated with seasonal and interannual
variation in precipitation??
Conclusions:
2. A shift occurs in the d13C of respired CO2
caused by forest-pasture conversion
Pastures do not have a pure C4 signal
Temporal variation is caused by C3
encroachment and pasture burning
Conclusions:
3.
18O
Tropical pasture respired CO2 is higher
in 18O than that from tropical forest
DC18O16O is different in C3 and C4
ecosystems
in CO2 could be an important signal
for forest-pasture conversions
Discrimination against CO2 containing 18O
Predicted d18OLW and ∆C18O16O values
for forests and pastures in Amazonia
d18OLW
∆C18O16O CA eq.
-5.6 ‰
2.8 ‰
100 %
C4 grassland +2.3 ‰ 6.7 ‰
38 %
C3 forest