Elena Gottardini, Fabiana Cristofolini, Antonella CristoforiElena Gottardini, Fabiana Cristofolini,...
Transcript of Elena Gottardini, Fabiana Cristofolini, Antonella CristoforiElena Gottardini, Fabiana Cristofolini,...
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Do ecosystem services have a biological cost? Ozone and climate regulation by Norway spruce forests along
an Alpine altitudinal transect in Trentino, northern Italy
Elena Gottardini, Fabiana Cristofolini, Antonella CristoforiResearch and Innovation Centre, Fondazione Edmund Mach (FEM)
San Michele all'Adige, Trento, Italy
Marco FerrettiTerraData environmetrics
Monterotondo M.mo, Grosseto, Italy
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Scheme of the presentation
• Introduction– Ozone and impact on ecosystem services
provided by forests• The study on Picea abies along an
altitudinal transect on Alps– Study design– Measurements of environmental and tree
response variables • Results
– Environmental variables– Ozone removal– Relationship between ozone removal and
(i) structural/environmental variables(ii) tree responses
• Discussion– Functional interpretation of monitoring data – Possible biological costs of removing ozone
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Ecosystem services
• Cultural• Provisioning• Supporting • Regulating
• Slope stability• Water cycle regulation• Carbon storage• Climate regulation• Air pollutant removal
Introduction
Ecosystem servicesbenefits people obtain from
ecosystems
Regulating servicesof forests
Mills et al., 2013
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Ecosystem services
• Cultural• Provisioning• Supporting • Regulating
• Slope stability• Water cycle regulation• Carbon storage• Climate regulation• Air pollutant removal
Introduction
Ecosystem servicesbenefits people obtain from
ecosystems
Regulating servicesof forests
Mills et al., 2013
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• Ozone can potentially affect the vegetation:- phytotoxicity - high values- wide distribution in remote areas
• Forests may reduce ozone through stomatal and non-stomatal deposition
Stomatal uptake
Surface reaction
depositionO3
Aim of the study is to assess the size of ozone regulating services provided by forests:
i) the portion of ozone removed by vegetationii) if ozone removal may have a biological cost for plants
with vegetation
without vegetation
20%
grad
ient
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Scheme of the presentation
• Introduction– Ozone and impact on ecosystem services
provided by forests• The study on Picea abies along an
altitudinal transect on Alps– Study design– Measurements of environmental and tree
response variables • Results
– Environmental variables– Ozone removal– Relationship between ozone removal and
(i) structural/environmental variables(ii) tree responses
• Discussion– Functional interpretation of monitoring data – Possible biological costs of removing ozone
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Fully randomized study on Norway spruce along an altitudinal gradient(900 - 1600 m a.s.l.) in Trentino, north Italy
Study design
Picea abies L.
0 20000 40000 60000
0-300
>300-600
>600-900
>900-1200
>1200-1500
>1500-1800
>1800-2100
>2100
elev
atio
n, m
a.s
.l.
ha
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Fully randomized study on Norway spruce along an altitudinal gradient(900 - 1600 m a.s.l.) in Trentino, north Italy
Study design
Picea abies L.
0 20000 40000 60000
0-300
>300-600
>600-900
>900-1200
>1200-1500
>1500-1800
>1800-2100
>2100
elev
atio
n, m
a.s
.l.
ha
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Statistical selection of:- 3 + 1 sites (open area)- 3 x 3 plot (forest)
750 m asl
900 m asl
1200 m asl
1600 m asl
Study design
open area
forest plot
Site 1
Site 2
Site 3
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Environmental variables
In each forest plot and open area, measurement at 2 m of:
Passive sampling:- Ozone - Nitrogen dioxide
Data logger:- Temperature- Relative humidity
Period: May - August 2013
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Tree response variables
• Chl a fluorescence (n=9 trees, 15 shoots per tree, C0 and C1)Fv/Fm = maximum quantum yield efficiency
• Crown condition (n=27 trees)
• Needle weight (n=9 trees, 900 needles per tree, C0)
• Shoot length (n=9 trees, 45 shoots per tree, C0)
Tree health
Productivity
Photosynthetic efficiency
Picea abies L.
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Scheme of the presentation
• Introduction– Ozone and impact on ecosystem services
provided by forests• The study on Picea abies along an
altitudinal transect on Alps– Study design– Measurements of environmental and tree
response variables • Results
– Environmental variables– Ozone removal– Relationship between ozone removal and
(i) structural/environmental variables(ii) tree responses
• Discussion– Functional interpretation of monitoring data – Possible biological costs of removing ozone
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Altitudinal profile of T and RH concentration
600
800
1000
1200
1400
1600
0 10 20
Temperature, °C
elev
atio
n, m
a.s
.l.
open areasforests
600
800
1000
1200
1400
1600
0 50 100
Relative humidity, %
elev
atio
n, m
a.s
.l.open areasforests
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600
800
1000
1200
1400
1600
0 2 4 6NO2, g m-3
elev
atio
n, m
a.s
.l.
open areasforests
Altitudinal profile of NO2 concentration
• Nitrogen dioxide concentration decreased with altitude, both inside and outside forests.
• Concentrations are very low (1.4 ug m-3)
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600
800
1000
1200
1400
1600
40 50 60 70 80 90 100O3, g m-3
elev
atio
n, m
a.s
.l.
open areasforests
Altitudinal profile of ozone concentration
• Ozone concentration increased with altitude, both inside and outside forests.
• Lower ozone concentrations within the forest (64.8 ug m-3) than in open areas (74.5 ug m-3) (P<0.001)
Site 0
Site 1
Site 2
Site 3
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010002000300040005000
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15
Week
AOT4
0, p
pbh
0
20
40
60
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15
Week
O3,
ppb
AOT40 estimation
Weekly O3 concentration Weekly AOT40
AOT40 = [O3] x 75.484 – 2462.9
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Site 1 - 913 m a.s.l.
0
1000
2000
3000
4000
5000
6000
7000
22/5 5/6 19/6 3/7 17/7 31/7
AO
T40,
ppb
h
AOT40: differences between open areas and forest
UNECE Critical level
Site 3 - 1521 m a.s.l.
0
1000
2000
3000
4000
5000
6000
7000
22/5 5/6 19/6 3/7 17/7 31/7
AO
T40,
ppb
h
Site 2 - 1177 m a.s.l.
01000200030004000500060007000
22/5 5/6 19/6 3/7 17/7 31/7
AO
T40,
ppb
h
0
1000
2000
3000
4000
5000
6000
7000
22/5 5/6 19/6 3/7 17/7
AO
T40,
ppb
h
open areaforest
Mean site 1, 2, 3
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0
1000
2000
3000
4000
5000
6000
7000
22/5 5/6 19/6 3/7 17/7
AO
T40,
ppb
h
open areaforest
Site 1 - 913 m a.s.l.
0
1000
2000
3000
4000
5000
6000
7000
22/5 5/6 19/6 3/7 17/7 31/7
AO
T40,
ppb
h
AOT40: differences between open areas and forest
UNECE Critical level
Site 3 - 1521 m a.s.l.
0
1000
2000
3000
4000
5000
6000
7000
22/5 5/6 19/6 3/7 17/7 31/7
AO
T40,
ppb
h
Site 2 - 1177 m a.s.l.
01000200030004000500060007000
22/5 5/6 19/6 3/7 17/7 31/7
AO
T40,
ppb
h
Mean portion of ozone removed by forest 56%
Mean site 1, 2, 3
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• Is there a relationship between ozone removal and environmental/structural factors?
– Elevation
– Ozone concentration
– LAI
– Tree circumference
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Ozone removal vs. environmental/structural factors
0
2000
4000
6000
0 500 1000 1500 2000
Elevation, m a.s.l.
O3 r
emov
al, p
pbh
0
2000
4000
6000
50 60 70 80 90[O3], ug m-3
O3 r
emov
al, p
pbh
0
2000
4000
6000
50 100 150Tree circumference, cm
O3 r
emov
al, p
pbhy = -1528.8x + 10789
R2 = 0.72
0
2000
4000
6000
2 4 6 8LAI
O3 r
emov
al, p
pbh
P<0.05
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• Is there a biological “cost” for plants because of ozone removal?
Response indicators:
– Trasparency
– Shoot lenght, needle wheight
– Chlorophyll fluorescence
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Ozone removal vs. tree responses
0
3
6
9
12
0 2000 4000 6000Ozone removal, ppbh
Sho
ot le
nght
, cm
0
2
4
6
8
0 2000 4000 6000Ozone removal, ppbh
Nee
dle
wei
ght,
mg
0.80
0.82
0.84
0.86
0.88
0 2000 4000 6000Ozone removal, ppbh
Fv/F
m
0
10
20
30
40
50
0 2000 4000 6000Ozone removal, ppbh
Tran
spar
ency
, %
~ 900 m a.s.l.~1200 m a.s.l.~1500 m a.s.l.
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Elevation vs. tree responses
y = 0.02x - 20.93R2 = 0.47
0
10
20
30
40
50
0 500 1000 1500 2000Elevation, m a.s.l.
Tran
spar
ency
, %
~ 900 m a.s.l.~1200 m a.s.l.~1500 m a.s.l.
y = -0.0048x + 13.87R2 = 0.98
0
3
6
9
12
0 500 1000 1500 2000Elevation, m a.s.l.
Shoo
t len
ght,
cmy = -0.00x + 7.39
R2 = 0.99
0
2
4
6
8
0 500 1000 1500 2000Elevation, m a.s.l.
Nee
dle
wei
ght,
mg
y = -0.00x + 0.88R2 = 0.97
0.80
0.82
0.84
0.86
0.88
0 500 1000 1500 2000Elevation, m a.s.l.
Fv/F
m
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Relationship among tree responses
Nested within such a superimposed effect of the
elevation, the various response indicators were
related to each other
y = -0.00x + 0.85R2 = 0.90
0.810.82
0.830.84
0.850.86
0 10 20 30 40Transparency, %
Fv/F
m
y = 0.01x + 0.78R2 = 0.73
0.81
0.820.83
0.840.85
0.86
0 3 6 9 12Shoot lenght, cm
Fv/F
m
y = -0.10x + 9.34R2 = 0.80
0
3
6
9
12
0 10 20 30 40Transparency, %
Sho
ot le
nght
, cm
~ 900 m a.s.l.~1200 m a.s.l.~1500 m a.s.l.
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Scheme of the presentation
• Introduction– Ozone and impact on ecosystem services
provided by forests• The study on Picea abies along an
altitudinal transect on Alps– Study design– Measurements of environmental and tree
response variables • Results
– Environmental variables– Ozone removal– Relationship between ozone removal and
(i) structural/environmental variables(ii) tree responses
• Discussion– Functional interpretation of monitoring data – Possible biological costs of removing ozone
![Page 26: Elena Gottardini, Fabiana Cristofolini, Antonella CristoforiElena Gottardini, Fabiana Cristofolini, Antonella Cristofori Research and Innovation Centre, Fondazione Edmund Mach (FEM)](https://reader034.fdocuments.net/reader034/viewer/2022050405/5f82c4afa6ce635ee86d00eb/html5/thumbnails/26.jpg)
Higher elevation > increase of abiotic stress(climate, solar radiation, ozone)
Lower photosyntheticefficiency
Greater susceptibility to other stress
Growth decrease
Worse crownconditions
More biotic andabiotic damages
Functional interpretation of monitoring data
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Higher elevation > increase of abiotic stress(climate, solar radiation, ozone)
Lower photosyntheticefficiency
Greater susceptibility to other stress
Growth decrease
Worse crownconditions
More biotic andabiotic damages
Functional interpretation of monitoring data
![Page 28: Elena Gottardini, Fabiana Cristofolini, Antonella CristoforiElena Gottardini, Fabiana Cristofolini, Antonella Cristofori Research and Innovation Centre, Fondazione Edmund Mach (FEM)](https://reader034.fdocuments.net/reader034/viewer/2022050405/5f82c4afa6ce635ee86d00eb/html5/thumbnails/28.jpg)
Higher elevation > increase of abiotic stress(climate, solar radiation, ozone)
Lower photosyntheticefficiency
Greater susceptibility to other stress
Growth decrease
Worse crownconditions
More biotic andabiotic damages
Functional interpretation of monitoring data
![Page 29: Elena Gottardini, Fabiana Cristofolini, Antonella CristoforiElena Gottardini, Fabiana Cristofolini, Antonella Cristofori Research and Innovation Centre, Fondazione Edmund Mach (FEM)](https://reader034.fdocuments.net/reader034/viewer/2022050405/5f82c4afa6ce635ee86d00eb/html5/thumbnails/29.jpg)
• Vegetation provides ecosystem services → ozone removal
• Ozone removal resulted:
– slightly dependent on elevation and on ozone concentration
– slightly associated to lower productivity and photosynthetic activity, and higher crown transparency
• Thus, ozone removal seems to have a slight (if any) “biological cost”
• Plants are able to play an important role in regulating services -like ozone removal - also where environmental conditions are more stressful
• Side findings: data suggest a possible functional interpretation of forest health monitoring data
Possible biological costs of removing ozone
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Acknowledgments
Forest and Fauna Serviceof Autonomous Province of Trento
Parco Naturale Paneveggio, Pale di San Martino