Transpiration of urban trees and its influence on ...
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Janina Konarska1, Johan Uddling2, Björn Holmer1, Martina Lutz2,
Fredrik Lindberg1, Håkan Pleijel2, Sofia Thorsson1
ICUC9, Toulouse, France, 20-24 July 2015
1 Urban Climate Group, Department of Earth Sciences, University of Gothenburg, Sweden 2 Department of Biological and Environmental Sciences, University of Gothenburg, Sweden
Transpiration of urban trees
and its impact on nocturnal cooling
in Gothenburg, Sweden
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RESEARCH CONTEXT. Urban trees
• Urban trees – a common mitigation strategy in climate-sensitive planning
• Urban environment – tree growing conditions and stress factors different
from those in forests
• To provide a cooling effect, trees need to remain healthy in the stressful
urban environment
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RESEARCH CONTEXT. Night-time tree transpiration?
Holmer B,Thorsson S, Linden J (2013) Evening evapotranspirative cooling in relation to vegetataion and urban geometry in the city
of Ouagadougou, Burkina Faso. Int J Climatol 33: 3089-3105
Phase 1 Phase 2
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Air
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ture
(°C
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Ta veg sites xstable
Ta non-veg sites xstable
cr veg sites xstable
cr non-veg sites xstable
Phase 1 (around sunset)
- Site specific, intensive cooling
- Holmer et al. 2013: more intensive
cooling in vegetated than non-
vegetated sites in Ouagadougou,
Burkina Faso
Phase 2 (starting 2-3 h after sunset)
- Spatially homogeneous, less
intensive cooling
- Holmer et al. 2013: similar cooling
rates at vegetated and non-
vegetated sites in Ouagadougou
non-vegetated
vegetated
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OBJECTIVES
• Quantify the magnitude and diurnal variations of transpiration of the
most common urban tree species in a high latitude city of Gothenburg,
Sweden
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OBJECTIVES
• Quantify the magnitude and diurnal variations of transpiration of the
most common urban tree species in a high latitude city of Gothenburg,
Sweden
• Analyse the influence of meteorological conditions and surface
permeability on the transpiration of urban trees
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OBJECTIVES
• Quantify the magnitude and diurnal variations of transpiration of the
most common urban tree species in a high latitude city of Gothenburg,
Sweden
• Analyse the influence of meteorological conditions and surface
permeability on the transpiration of urban trees
• Find out whether the transpiration of urban trees contributes to daytime
or nocturnal cooling
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MEASUREMENTS. Instruments
• LiCor XT-6400 Portable Photosynthesis System – an open
system measuring gas exchange between leaf and air using
an infrared gas analyser
– leaf transpiration rate (EL, mmol m⁻² s⁻¹)
– stomatal conductance (gs, mmol m⁻² s⁻¹)
• Ta and RH ( cooling rates) measured simultaneously with
two TinyTag Plus 2 instruments:
– at the measurement site, under one of the trees
– at a reference site in a non-vegetated street canyon
• Energy loss per unit ground area (QE, W m-2) due to tree
transpiration was calculated by scaling up EL using
measured leaf area index (LAI)
• Note: for more information on LAI measurements in urban
areas, see Jenny Klingberg’s presentation this afternoon,
session UCP11
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MEASUREMENTS. Study sites
• Seven most common tree species in Gothenburg: common lime (linden), English oak,
Norway maple, Silver birch, Horse chestnut, European beech, Japanese cherry
• Street and park trees, different growing
conditions (but no irrigation)
• 4-6 tree individuals per site, 8 leaves
per tree (4 sunlit and 4 shaded)
• Daytime and night-time measurements
on warm, sunny summer days (2012-13)
• Linden trees: three sites, continuous
hourly measurements from noon until
a few hours after sunset
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RESULTS. Diurnal course
• EL of sunlit leaves was on average 3x higher than
of shaded leaves
• Park trees transpired more intensively than street
trees
• Transpiration dropped significantly before sunset
due to decreasing VPD and incoming solar
radiation, but remained active during the night
(7% of midday EL of sunlit leaves and 20% of
those in shadow)
Park trees
Street trees
wide grass lawn
Street trees
narrow grass lawn
of transpiration (linden, T. europaea)
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RESULTS. Influence of weather and surface permeability
Accummulated rainfall [mm]
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RESULTS. Influence of weather and surface permeability
Accummulated rainfall [mm]
Fraction of permeable surfaces
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RESULTS. Influence of weather and surface permeability
A simple estimation of available rainwater [mm]:
– soil characteristics, interception, the extent of roots etc. are not
accounted for
+ widely available data
+ no measurements needed
Accummulated rainfall [mm]
Fraction of permeable surfaces
Accummulated rainfall x Fraction of permeable surfaces
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RESULTS. Influence of weather and surface permeability
Fraction of permeable surfaces
Accummulated rainfall [mm]
– soil characteristics, interception, the extent of roots etc. are not
accounted for
+ widely available data
+ no measurements needed
Accummulated rainfall x Fraction of permeable surfaces
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RESULTS. Estimated energy loss per unit ground area
Species, location Date
Incoming solar
radiation
(midday, W m-2)
Energy loss due to tree
transpiration, QE [W m-2]
Midday Night-time
Linden, park trees 11.07.2013 859 92 16
Linden, street trees, narrow
grass lawn
20.07.2013 788 72 13
22.08.2013 594 132 20
Linden, street trees, wide
grass lawn
03.09.2013 572 206 30
06.09.2013 609 174 18
English oak 12.07.2013 795 343 38
28.08.2013 433 390 32
Silver birch 09.07.2013 812 230 1.5
20.08.2013 528 190 26
Norway maple 20.08.2013 613 196 12
Horse chestnut 23.07.2013 799 171 32
29.07.2013 635 260 31
European birch 26.07.2012 809 127 30
Japanese cherry 13.07.2013 780 244 25
02.09.2013 610 260 35
Average 682 206 24
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RESULTS. Transpiration vs daytime and nocturnal cooling
- More intensive cooling with increasing EL
- Less intensive cooling at a non-vegetated
reference site
- No correlation between cooling rate and EL
Phase 1 (meas.)
Phase 2 (meas.)
Phase 1 (ref.)
Phase 2 (ref.)
Phase 1
Phase 2
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RESULTS. Transpiration vs daytime and nocturnal cooling
- More intensive cooling with increasing EL
- Less intensive cooling at a non-vegetated
reference site
- No correlation between cooling rate and EL
Phase 1
Phase 2
- No correlation between midday
warming rate and El dispite strong
transpiration
Midday
Phase 1 (meas.)
Phase 2 (meas.)
Phase 1 (ref.)
Phase 2 (ref.)
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CONCLUSIONS
• Poor growing conditions of trees (impermeable surfaces surrounding the trees)
decrease their transpiration and therefore cooling effect. A simple estimation of
available rainwater, based on widely available data, explained 68% of variance in
stomatal conductance
• Night-time transpiration was active in all studied trees and reached on average
7% and 20% of daytime EL of sunlit and shaded leaves, respectively, with an
estimated latent heat flux of 24 W per unit ground of vertically projected tree area
• A significant correlation of transpiration rate with the cooling rate of the air, as
well as less intensive cooling at a non-vegetated reference site, indicated a
contribution of tree transpiration to cooling around and shortly after sunset, but not
later in the night
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Research paper: Konarska J., Uddling J., Holmer B., Lutz M., Lindberg F., Pleijel H., Thorsson S., 2015.
Transpiration of urban trees and its cooling effect in a high latitude city. Int J Biometeorol (in press)
The research was funded by the Swedish Research Council Formas (259-2012-887 and 214-2010-1706),
Swedish Transport Administration and Mistra Urban Futures.
Thank you for your attention!