temporal variability and drivers of net ecosystem production of a turkey oak (quercus cerris l.)...
TRANSCRIPT
TEMPORAL VARIABILITY AND DRIVERS OF NET ECOSYSTEM PRODUCTION OF A TURKEY OAK (QUERCUS CERRIS L.) FOREST
IN ITALY UNDER COPPICE MANAGEMENT
Luca Belelli Marchesini (1), Ana Rey (2), Dario Papale (1), Riccardo Valentini (1)
(1) DISAFRI, University of Tuscia, Viterbo, Italy. (2) EEZA-CSIC, Almería, Spain.
CARBO-Extreme Annual Meeting
13 September 2010, Roskilde (DK)
Activities during the first year of Carbo-Extreme project (WP3):
Analysis of a long-term eddy covariance dataset from Roccarespampani site (coppice forest in central Italy): 15 years of continuous NEE data representative for forest stand age from 0 (post-harvest) to 18 years covering almost the whole rotation period.
Inter-annual and seasonal variability of NEE, GPP, Reco
Climatic drivers (functional relations) of the C cycle and disturbance
induced by coppice management.
Separation of age and climate as factors controlling the temporal trend
of the C balance by Artificial Neural Networks (AANs). (preliminary)
Comparison of NEE with modelled NPP (inventories+ allometric
functions) and assessment of NBP. (not shown here)
shoots
Stand after coppicing
reserve trees
(42.3903 N; 11.9209 E)
(42.4082 N ; 11.9303 E)
Roccarespampani
Coppice forest ~1250ha
Mature stand
Two eddy covariance sites
Sites location and applied management
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
NEE, R
eco, G
PP [
g C m
-2 d
-1]
-15
-10
-5
0
5
10
15
20 stand age
b
2002
2003
2004
2005
2006
2007
2008
2009
-15
-10
-5
0
5
10
15
20
0 1 2 3 4 5 6 7 8
stand age
11 12 13 14 15 16 17
a b
time since forest harvest
Rocca 1 (2000-2008), harvested in Dec. 1999
Rocca 2 (2002-2008), harvested in Dec. 1990
Chronosequence reconstructed by assembling the dataset of 2 EC stations
Standard Carbo-Europe data processing (QA, gapfilling, partitioning)
NEE
GPP
Reco
Similar soil features, specific composition, topography, same management
0 18
EC data set
NE
E (
g C
d-1)
2002
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2003
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2004
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2005
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2006
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2008
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
NEE [
gC
m-2 d
-
1]
doy2000 2001 2002 2003 2004 2005 2006 2007 2008 2009
Rain
[m
m]
0
10
20
30
40
50
60
70100
200
300
Air
tem
p [
°C]
0
5
10
15
20
25
30
35
40
45
2005
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2006
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
2008
0 100 200 300
-14
-12
-10
-8
-6
-4
-2
0
2
4
6
NE
E (
g C
d-1)
Rocca 1Rocca 2
Seasonal trend of NEE
Rec
o [g
C m
-2d-
1]
0
1
2
3
4
5
SW
C [
m3 m
-3]
10
15
20
25
30
35
40
45
50
VPD
[hPa
]
0
5
10
15
20
25
30
35
Tair [°C]
0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32
GPP
[gC
m-2d-
1]
0
2
4
6
8
10
12
age 0- 8
age 11- 17
Rec
o [g
C m
-2d-
1]
0
1
2
3
4
5
NEE [
gC m
-2d-
1]
- 8
- 6
- 4
- 2
0
2
4
Tair [°C]
0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32
GPP
[gC
m-2d-
1]
0
2
4
6
8
10
12
age 0- 8
age 11- 17
GPP
Soil Water Content (-10 cm)
Vapour Pressure Deficit
Ecosystem respiration
(Reco)
NEE
Dry period
CO2 fluxes response to air temperature
Daily fluxes
Gap filling fQC1>=90%
Relative importance of “physiological” seasons
winter
spring
dry period
fall
Gro
win
g se
aso
n
doy
76 61 158 29 41
101 64 56 90 54104 61 56 97 47
100 49 119 50 47105 40 120 59 41
84 79 120 41 4294 83 108 38 43
101 49 126 42 47110 37 129 46 43
96 48 125 46 5096 39 122 49 59
79 86 58 80 62
87 76 94 59 5096 67 94 70 39
0 50 100 150 200 250 300 350
W
S
DP
F
W
2004
2003
2001
2002
2005
2006
2007
2008
R1R2
R1
R1R2
R1R2
R1R2
R1R2
R1R2
R1
Duration of seasons
Growing season GS Reco 0.95 ***
NEE 0.98 ***
GPP 0.93 ***
Spring S Reco 0.77 **
NEE 0.45 n.s
GPP 0.11 n.s
Dry period DP Reco 0.75 **
NEE 0.91 ***
GPP 0.90 ***
Fall F Reco 0.67 **
NEE 0.79 ***
GPP 0.38 n.s
Dormancy NG Reco 0.89 ***
NEE 0.07 n.s
GPP -0.29 n.s
Winter - Spring WS Reco 0.77 **
NEE 0.18 n.s
GPP -0.18 n.s
Fall - Winter FW Reco 0.68 **
NEE 0.74 **
GPP 0.16 n.s
Year
Reco NEE GPP
* P<0.05
** P<0.01
*** P<0.0001
Which period influences mostly the annual C balance?
Correlation analysis (ρ- Spearman):
Annual mean flux
vs
Mean flux of each period
Importance of different seasons on annual NEE
Years after coppicing
0 2 4 6 8 10 12 14 16 18
NEE [
g C m
-2 y
-1]
-1200
-1000
-800
-600
-400
-200
0
200
400
sourcesink
Carbon budget
R2 = 0.66P < 0.001
2008
2008
2003
20032005
2005
2006
2006
20042004 2002
2002
2001
2000
2007
NEE inter-annual variability
R2 = 0.32P=0.02
R2 = 0.41P < 0.01
Years af ter coppicing
0 2 4 6 8 10 12 14 16 18
Rec
o [g
C m
-2 y
-1]
600
800
1000
1200
1400
1600
GPP
[g
C m
-2 y
-1]
1000
1200
1400
1600
1800
2000
stand age (years)
0 5 10 15
Rec
o/G
PP
0.2
0.4
0.6
0.8
1.0
1.2
R2=0.70p<0.0001
Decreasing Reco/GPP ratio2008
20082003
20032005
2005
2006
2006
2004
2004
20022002
2001
2000
2007
2008 2008
2003
20032005
2005
2006
2006
2004
2004
2002
2002
2001
2000
2007
Trend of Reco consistent with that of soil respiration
(Tedeschi et al., 2006)
Reco, GPP inter-annual variability
Variable Partial correlation p-level
1 Age -0.87 0.0021
**
2 Ts mean annual 0.77 0.0079
**
3 PPT annual 0.74 0.0130
*
4 Ta anomaly (JJA)
0.64 0.0457
*
NEER= .95 R²= .91Adjusted R²= .86F(4,8)=20.421 p<.00029 Std.Error: 115.96
Variable Partial correlation p-level
1 Age 0.63 0.0278
*
2 Ta mean GS -0.60 0.0367
*
3 PPT annual -0.47 0.1160
4 Ta anomaly (JJA) -0.41 0.1742Variable Partial correlation p-level
1 Age 0.80 0.0030
**
2 PPT anomaly (JJA) 0.59 0.0528
3 Ts mean annual 0.48 0.1350
GPPR= .81 R²= .66Adjusted R²= .53F(4,10)=5.0438 p<.01736 Std.Error : 197.72
Reco annual R= .91 R²= .82 Adjusted R²= .76F(3,9)=13.993 p<.00098 Std.Error: 89.931
NEE inter-annual variability and climatic factors
Multiple regression (forward step-wise) : Ta, Ts, PPT, Rg (annual-growing season); Ta, PPT anomalies (JJA); PPT anomaly (Jan-May)
Influence of climate on NEE, GPP. Reco inter-annual variability
Warming effect of clear cut on forest microclimate
*mean values of August
Years af ter coppicing
0 5 10 15 20
Tai
r, T
soil
[°C]
-5
0
5
20
25
30Tair
Tsoil
(Ts-Ta)
(T
air
-Tso
il) [
°C]
cooler soil
warmer soil
Clear cut effect
Rocca 1 -FW 2003
T soil [°C]
5 10 15 20
Rec
o [g
C m
-2 d
-1]
0
2
4
6
8
10
R2=0.92 n=97 P<0.001
Rocca 1 -WS 2003
R2=0.82 n=149 P<0.001
10
10
)10(10
T
refeco QRR
Increased soil temperature after coppicing, but same temperature sensitivity?
Analysis of parameters of the Reco-Tsoil curve (Rref, Q10), for the winter-spring (WS) and fall-winter (FW) periods.
Reco- Tsoil dependence
RrefSignificantly higher in the WS period compared to FW(Wilcoxon test: P=0.013)
Decreases with stand age, both in FW (R2 0.61, p<0.001); and WS (R2=0.48, p<0.01)
years af ter coppicing
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18
Rre
f(10
) [g
C m
-2 d
-1]
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5R ref _FW
Rref _WS Rref
Q10
difference beween WS and FW (Wilcoxon test p=0.02).
Q10 in the WS period significantly varies with age (R2=0.41, p<0.05)
years af ter coppicing
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18
Rre
f(10
) [g
C m
-2 d
-1]
0
2
4
6
8
Q10 _FW
Q10 _WS Q10
Q10 function parameters
Conclusions
1. Coppice management of Roccarespampani forest associated
to high C sequestration rates and limited duration of net
C release following clear cuts (C budget <0 already after
2years )
2. Sink strenght increases primarily with age, but negatively
impacted by warmer temperatures and droughts.
3. Enhanced ecosystem respiration after coppicing,
independently of the altered microclimate (input of C,N through
biomass residuals/root mortality).
4. Importance of taking into account the role of forest
management on ecosystem carbon dynamics together with
climatic drivers.
Country Site Start of EC records
Years in database
Vegetation/climate
FI Hyttiala 1996 13 Evergreen/boreal
FI Sodankila 2000 9 Evergreen/boreal
SE Norunda 1996 8 Evergreen/boreal
SE Flakaliden 1996 7 Evergreen/boreal
DK Soro 1996 14 Deciduous/cool temperate
GER Tharandt 1996 14 Evergreen/cool temperate
BE Vielsam 1996 14 Mixed /cool temperate
NL Loobos 1996 14 Evergreen/ cool temperate
FR Le Bray 1996 13 Evergreen/ cool temperate
FR Hesse 1997 12 Deciduous/cool temperate
BE Brasschat 1997 11 Mixed/ cool temperate
IT Collelongo 1996 14 Deciduous/ warm temperate
IT Roccarespampani 1 2000 9 Deciduous/ warm temperate
IT Roccarespampani 2 2002 7 Deciduous/ warm temperate
IT Castelporziano 1997 10 Evergreen/ warm temperate
FR Puechabon 2000 9 Evergreen/ warm temperate
Analysis of eddy covariance data from forest sites differing for plant functional type with long time series available:
Outlook on next activities (1/2)
• Use of ANNs to disentangle stand age and climate effects on NEE time series of forest ecosystems and single out main drivers of NEE variability.
-1200
-1000
-800
-600
-400
-200
0
200
400
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18
years after coppicing
NEE (
gC m
-2 y
-1)
18 years old stand (simulation)
Observed NEE
which synthesize the dependence structure of data, regardless of marginal distributions (Fx1,Fx2,..), to produce multivariate probability functions of NEE and climatic drivers and individuate thresholds for different climate domains.
X1
x2
F(x
1,x 2
)/x 3
Example of 3-copula:
Joint probability density function of (x1,x2) , given x3
(from Grimaldi & Serinaldi, 2006)
• Explore the use of copula (C) functions (Genest & McKay, 1986)
(Roccarespampani forest)
In particular:
Outlook on next activities (2/2)
Thank you for your attention!
More information: Luca Belelli ([email protected])
climate anomalies_ mean Ta, PPT (2000-2008)
-200-150-100
-500
50100150200250300
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-00
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-5-4-3-2-101234567
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