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© Natural Resources Institute Finland© Natural Resources Institute Finland
• Tuomo Purola, Heikki Lehtonen, Xing Liu,
• Fulu Tao, Taru Palosuo
• Natural Resources Institute Finland (Luke)
• ClimSmartAgri workshop
• October 23 2017
Future climate change and impacts
on yields and farm management:
a case study at a pilot region in Finland
© Natural Resources Institute Finland
Objectives – main research questions:
• What are the effects of crop productivity change on farm level
land use, input use, management and farm income?
• How much more value can a farmer expect from improved
crop yields?
• How do the effects vary with different future price levels?
• Differences between spring and winter cereals in future
climate conditions?
• Do higher crop yields lead to reduced GHG emissions per
farm, or per kg produced?
2 24.10.2017
© Natural Resources Institute Finland
Crop modelling results utilised in this study
• Ensemble simulations using a process-based large
area crop model (MCWLA) (Tao et al., 2015)
It explicitly parameterized the effects of extreme temperature and
drought stress on wheat yields, and accounted for a wide range
of wheat cultivars with contrasting phenological characteristics
and thermal requirements.
• Climate scenarios B1, A2
• Other main assumptions
– Yields of all spring crops will develop in the very similar
way, but winter wheat yields differently
3 24.10.2017
© Natural Resources Institute Finland
Estimated future yields 2042-2070 of spring and winter wheat in
North Savo in B1 (upper) and A2 (lower) climate scenarios
4 24.10.2017
0
1000
2000
3000
4000
5000
6000
2040 2045 2050 2055 2060 2065 2070 2075
Yield(kgha-1
Year
Spring wheat A2 BCCR Spring wheat A2 IPSL Winter wheat A2 BCCR Winter wheat A2 IPSL
0
1000
2000
3000
4000
5000
6000
2040 2045 2050 2055 2060 2065 2070 2075
Yield(kgha-1
Year
Spring wheat B1 GISS Spring wheat B1 CSIRO Winter wheat B1 GISS Winter wheat B1 CSIRO
© Natural Resources Institute Finland
Historical yield vs. simulated future yield of spring (up) and
winter (down) wheat in North Savo
Source: Official agricultural statistics www.stat.luke.fi (left); MCWLA bio.phys. model, Luke (right)
5 24.10.2017
0
1000
2000
3000
4000
5000
6000
1990 2000 2010 2020 2030 2040 2050 2060 2070 2080
Yields 1995-2015 B1 GISS A2 IPSL
0
1000
2000
3000
4000
5000
6000
1990 2000 2010 2020 2030 2040 2050 2060 2070 2080
Yields 1995-2014 B1 GISS A2 IPSL
© Natural Resources Institute Finland
Economic model employed
• Rational farmers, mean-variance utility function:
• Maximize present income discounted expected profit
• Minimize the variance of expected profits
• Choosing the sequence of crops i planted on parcels p every
year during next H years
• A(p,t,i)=Land allocation on parcel p of crop i on year t
• Y=Crop yield, depends on past land use, N fert., soil pH,
fungicide use; X=past (expected) gross margin covariance;
C=cost per ha; P=crop price; S=support payments per crop
6 24.10.2017
( )( )
∑ ∑ ∑
∑ ∑∑
−
=
+−
−++
H
t
c c
t
p
M
i
t
H
t
XAAr
itpCiSiPitpAitpitpAYrMax
1
2
10
11=
'))1/(1(
),,()()(),,(,,),,,())1/(1(
θ
1,=),,( ctpA
c
∑∀
© Natural Resources Institute Finland
Special features of the economic model
employed
Nitrogen response function (Lehtonen, 2001)
Fungicide treatment (Purola, 2013)
7 24.10.2017
oilseedsiwhenNcNbaNY
oatsbarleywheatiwhenkemNY
iii
mean
bNi
mean
i
=++=
=−=



2
000)(
,,)1()(
)(),,(),,(
1
i
j
jj
ii
cKctpctpF ∑=
=
γ
βδ
Liming treatment (Myyrä et al. 2006)
© Natural Resources Institute Finland
Cereals farms in North Savo region
• Farm size appr. 50 ha, average yields of the region,
land and input use derived from statistical sources
and verified calculations (Pro Agria (proagria.fi),
Luke)
• 32% of farm family income from agriculture
• A generic assumption: 10 parcels and the distances
of the parcels to the farm centre vary between 0
and 7 km, with an average distance of 2.9 km for
the region
– logistic costs dependent on the distance
• Decisions to cultivate a crop in each field parcel,
with input use decisions (yields) set up a dynamic
programming problem, over all field parcels
8 24.10.2017
© Natural Resources Institute Finland
Simulated land allocation vs. historical land allocation
Source: Dynamic economic crop rotation and management model results, Luke 2017
9 24.10.2017
0 %
10 %
20 %
30 %
40 %
50 %
60 %
70 %
80 %
90 %
100 %
t1 t3 t5 t7 t9 t11 t13 t15 t17 t19 t21 t23 t25 t27 t29
SWheat WWheat Barley Oats Oilseed Setaside
0 %
10 %
20 %
30 %
40 %
50 %
60 %
70 %
80 %
90 %
100 %
20002001200220032004200520062007200820092010201120122013
SWheat Barley Oats Oilseeds Setaside
© Natural Resources Institute Finland
Scenario settings
Price scenario
Emission
scenario –
Climate
model -
combination
-20% baseline
price
(LP)
Baseline price
(BP)
+20% baseline
price
(HP)
Baseline Baseline LP Baseline BP Baseline HP
A2 BCCR A2 BCCR LP A2 BCCR BP A2 BCCR HP
A2 IPSL A2 IPSL LP A2 IPSL BP A2 IPSL HP
B1 GISS B1 GISS LP B1 GISS BP B1 GISS HP
B1 CSIRO B1 CSIRO LP B1 CSIRO BP B1 CSIRO HP
© Natural Resources Institute Finland
Simulated results in current climate under different price scenarios
Average yields 1995–2015 Simulated baseline yields from economic model
LP BP HP
Spring wheat 3086 2886(-6.5%) 3162(+2.4%) 3168(+2.6%)
Winter wheat 3051
Barley 2948 2895(-1.8%) 3171(+7.6%) 3185(8.0%)
Oats 2785 2611(-6.2%) 2870(+3.1%) 2888(+3.7%)
Spring turnip
rape
1305 1228(-5.9%) 1376(+5.5%) 1388(+6.4%)
Frequency of fungicide treated
barley and wheat/ farm
0 0 0
Average pH/ farm 5.71 6.56 6.65
Total gross margin €/farm, over 30 years 55 739 64 815 78 181
GHG emissions tons CO2 eq. /year
(normalised per 10 ha/year)
24.12 30.89 34.83
© Natural Resources Institute Finland
Simulated results under A2 and B1 climate scenarios
B1 GISS A2 IPSL
Regional
average
yields kg/ha
Simulated
Yield
(MCWLA
bio.phys. model)
Simulated
Yield (Economic model)
Simulated
Yield
(MCWLA
bio.phys. model)
Simulated
Yield (Economic model)
LP BP HP LP BP HP
Spring
wheat
[3086]
3927
4008
(+2.1%)
4020
(+2.4%)
4026
(+2.5%)
3685
3755
(+1.9%)
3766
(+2.2%)
3778
(+2.5%)
Winter
wheat
[3051]
3623 3402 - - -
Barley
[2948] 3939
4231
(+7.4%)
4321
(+9.7%)
4396
(+11.6%) 3697
3962
(+7.2%)
4016
(+8.6%)
4101
(+10.9%)
Oats
[2785] 3543
3680
(+3.9%)
3688
(+4.1%)
3711
(+4.7%)
3325
3458
(+4.0%)
3461
(+4.1%)
3472
(+4.4%)
Oilseed
[1305] 1660
1761
(+6.1%)
1766
(+6.4%)
1773
(+6.8%)
1558
1647
(+5.7%)
1662
(+6.7%)
1660
(+6.5%)
Frequency of fungicide treated
barley and wheat/ farm [0] 0 112 198 0 53 177
Average pH/ farm
[6.56]
6.62 6.67 6.69 6.58 6.66 6.68
Total profit €/farm/year
[10803]
16777 20644 24474 15050 19243 22849
GHG emissions overall tons
CO2 eq. /year (normalized per
10 ha/year) [30.89]
31.68 33.59 34.79 29.79 33.67 34.79
© Natural Resources Institute Finland
Land allocation: Baseline (left) vs. A2 IPSL (right)
SWheat
WWheat
Barley
Oats
Oilseed
Setaside
NMF
SWheat
WWheat
Barley
Oats
Oilseed
Setaside
NMF
SWheat
WWheat
Barley
Oats
Oilseed
Setaside
NMF
SWheat
WWheat
Barley
Oats
Oilseed
Setaside
NMF
SWheat
WWheat
Barley
Oats
Oilseed
Setaside
NMF
SWheat
WWheat
Barley
Oats
Oilseed
Setaside
NMF
LP
BP
HP
© Natural Resources Institute Finland
GHG emissions per kg produced decrease if higher
yields - increase if higher prices
(due to concave production functions, decreasing marginal effect of inputs)
Baseline A2 IPSL B1 GISS
Barley yield (kg/ha) 3171 4016 4321
Total crop production (tons per year
per 10 ha) 24.225 36.529 39.135
Gross margin per farm per year
(eur)(average over 30 years) 10.803 19.243 20.644
GHG emissions (tons CO2 eq. Per
10 ha) 30.89 33.67 33.59
GHG emissions per ton produced
(tons CO2 eq./ton) 1.28 0.92 0.86
Emissions per unit produced (tons CO2
eq./ton)
LP BP HP
BASE 1.75 1.28 1.22
A2 IPSL 0.95 0.92 0.95
B1 GISS 0.85 0.86 0.89
Emissions per unit (tons CO2 eq. /ton), set
aside land excluded
LP BP HP
BASE 0.87 1.03 1.10
A2 IPSL 0.76 0.85 0.87
B1 GISS 0.78 0.79 0.82
LP = -20% from baseline
prices
BP = Baseline prices 2000-
2013
HP = +20% from baseline
prices
© Natural Resources Institute Finland
Conclusive remarks
• Crop modelling results suggest increase of spring cereals yields from current
3 t/ha up to 3.5-3.6 t/ha (winter wheat; +15-20%) and to 4 t/ha (barley, spring
wheat; +30%) until 2040-2070 in A2, B1
• Higher yields incentivize higher soil pH (liming), fungicide use and thus a
further increase yields by 2-12%
• Economic model results suggest that barley production becomes dominating
if yields increase, due to lower (historical) gross margin variability and strong
fungicide response of yields
• 26-36% higher yields would imply 50-60% higher production and 36-46%
higher gross margins per farm in scenarios B1, A2 - from current low levels
• GHG emissions per kg produced decrease by 27-33%
• The results suggest that current unexploited production potential will be used
if 20-30% higher yields, but 30% less GHG emissions per kg produced –
There are possibilities for ”sustainable intensification”
© Natural Resources Institute Finland
Thank you for your attention!
References:
• Liu, X., Lehtonen, H., Purola, T., Pavlova, Y., Rötter, R. & Palosuo, T. 2016. Dynamic
economic modelling of crop rotations with farm management practices under future pest
pressure. Agricultural Systems (2016), pp. 65-76 DOI: 10.1016/j.agsy.2015.12.003
• Lehtonen, H., Liu, X. and Purola, T. 2016. Balancing climate change mitigation and
adaptation with socio-economic goals at farms in northern Europe. In: Paloviita, A. and
Järvelä, M. (Eds) 2015. Climate Change Adaptation and Food Supply Chain Management
(Routledge Advances in Climate Change Research), Routledge, London, 264 pp. ISBN13:
978-1138796669; http://www.tandf.net/books/details/9781317634034/. p. 132-146
• Lehtonen, H., 2001. Principles, structure and application of dynamic regional sectormodel of
Finnish agriculture Academic dissertation Systems Analysis Laboratory, Helsinki University
of Technology. Publications 98. Agrifood Research Finland, Economic Research (MTTL),
Helsinki.
• Myyrä, S., Ketoja, E., Yli-Halla,M., Pietola, K., 2005. Land improvements under land tenure
insecurity: the case of pH and phosphate in Finland. Land Econ. 81 (4), 557–569.
• Purola, T., 2013. Taudinkestävien ja tautialttiiden ohralajikkeiden taloudellinen vertailu.
Master thesis University of Helsinki. Department of economics and management.
(https://helda.helsinki.fi/handle/10138/40225)
• Tao F, Rötter RP, Palosuo T, Höhn J, Peltonen-Sainio P, Rajala A, Salo T. 2015. Assessing
climate impacts on wheat yield and water use in Finland using a super-ensemble-based
probabilistic approach. Climate Research, 65, 23-37.
© Natural Resources Institute Finland
Thank you!
24.10.201717

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Higher yielding cultivars, more sustainable agriculture

  • 1. © Natural Resources Institute Finland© Natural Resources Institute Finland • Tuomo Purola, Heikki Lehtonen, Xing Liu, • Fulu Tao, Taru Palosuo • Natural Resources Institute Finland (Luke) • ClimSmartAgri workshop • October 23 2017 Future climate change and impacts on yields and farm management: a case study at a pilot region in Finland
  • 2. © Natural Resources Institute Finland Objectives – main research questions: • What are the effects of crop productivity change on farm level land use, input use, management and farm income? • How much more value can a farmer expect from improved crop yields? • How do the effects vary with different future price levels? • Differences between spring and winter cereals in future climate conditions? • Do higher crop yields lead to reduced GHG emissions per farm, or per kg produced? 2 24.10.2017
  • 3. © Natural Resources Institute Finland Crop modelling results utilised in this study • Ensemble simulations using a process-based large area crop model (MCWLA) (Tao et al., 2015) It explicitly parameterized the effects of extreme temperature and drought stress on wheat yields, and accounted for a wide range of wheat cultivars with contrasting phenological characteristics and thermal requirements. • Climate scenarios B1, A2 • Other main assumptions – Yields of all spring crops will develop in the very similar way, but winter wheat yields differently 3 24.10.2017
  • 4. © Natural Resources Institute Finland Estimated future yields 2042-2070 of spring and winter wheat in North Savo in B1 (upper) and A2 (lower) climate scenarios 4 24.10.2017 0 1000 2000 3000 4000 5000 6000 2040 2045 2050 2055 2060 2065 2070 2075 Yield(kgha-1 Year Spring wheat A2 BCCR Spring wheat A2 IPSL Winter wheat A2 BCCR Winter wheat A2 IPSL 0 1000 2000 3000 4000 5000 6000 2040 2045 2050 2055 2060 2065 2070 2075 Yield(kgha-1 Year Spring wheat B1 GISS Spring wheat B1 CSIRO Winter wheat B1 GISS Winter wheat B1 CSIRO
  • 5. © Natural Resources Institute Finland Historical yield vs. simulated future yield of spring (up) and winter (down) wheat in North Savo Source: Official agricultural statistics www.stat.luke.fi (left); MCWLA bio.phys. model, Luke (right) 5 24.10.2017 0 1000 2000 3000 4000 5000 6000 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 Yields 1995-2015 B1 GISS A2 IPSL 0 1000 2000 3000 4000 5000 6000 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 Yields 1995-2014 B1 GISS A2 IPSL
  • 6. © Natural Resources Institute Finland Economic model employed • Rational farmers, mean-variance utility function: • Maximize present income discounted expected profit • Minimize the variance of expected profits • Choosing the sequence of crops i planted on parcels p every year during next H years • A(p,t,i)=Land allocation on parcel p of crop i on year t • Y=Crop yield, depends on past land use, N fert., soil pH, fungicide use; X=past (expected) gross margin covariance; C=cost per ha; P=crop price; S=support payments per crop 6 24.10.2017 ( )( ) ∑ ∑ ∑ ∑ ∑∑ − = +− −++ H t c c t p M i t H t XAAr itpCiSiPitpAitpitpAYrMax 1 2 10 11= '))1/(1( ),,()()(),,(,,),,,())1/(1( θ 1,=),,( ctpA c ∑∀
  • 7. © Natural Resources Institute Finland Special features of the economic model employed Nitrogen response function (Lehtonen, 2001) Fungicide treatment (Purola, 2013) 7 24.10.2017 oilseedsiwhenNcNbaNY oatsbarleywheatiwhenkemNY iii mean bNi mean i =++= =−=    2 000)( ,,)1()( )(),,(),,( 1 i j jj ii cKctpctpF ∑= = γ βδ Liming treatment (Myyrä et al. 2006)
  • 8. © Natural Resources Institute Finland Cereals farms in North Savo region • Farm size appr. 50 ha, average yields of the region, land and input use derived from statistical sources and verified calculations (Pro Agria (proagria.fi), Luke) • 32% of farm family income from agriculture • A generic assumption: 10 parcels and the distances of the parcels to the farm centre vary between 0 and 7 km, with an average distance of 2.9 km for the region – logistic costs dependent on the distance • Decisions to cultivate a crop in each field parcel, with input use decisions (yields) set up a dynamic programming problem, over all field parcels 8 24.10.2017
  • 9. © Natural Resources Institute Finland Simulated land allocation vs. historical land allocation Source: Dynamic economic crop rotation and management model results, Luke 2017 9 24.10.2017 0 % 10 % 20 % 30 % 40 % 50 % 60 % 70 % 80 % 90 % 100 % t1 t3 t5 t7 t9 t11 t13 t15 t17 t19 t21 t23 t25 t27 t29 SWheat WWheat Barley Oats Oilseed Setaside 0 % 10 % 20 % 30 % 40 % 50 % 60 % 70 % 80 % 90 % 100 % 20002001200220032004200520062007200820092010201120122013 SWheat Barley Oats Oilseeds Setaside
  • 10. © Natural Resources Institute Finland Scenario settings Price scenario Emission scenario – Climate model - combination -20% baseline price (LP) Baseline price (BP) +20% baseline price (HP) Baseline Baseline LP Baseline BP Baseline HP A2 BCCR A2 BCCR LP A2 BCCR BP A2 BCCR HP A2 IPSL A2 IPSL LP A2 IPSL BP A2 IPSL HP B1 GISS B1 GISS LP B1 GISS BP B1 GISS HP B1 CSIRO B1 CSIRO LP B1 CSIRO BP B1 CSIRO HP
  • 11. © Natural Resources Institute Finland Simulated results in current climate under different price scenarios Average yields 1995–2015 Simulated baseline yields from economic model LP BP HP Spring wheat 3086 2886(-6.5%) 3162(+2.4%) 3168(+2.6%) Winter wheat 3051 Barley 2948 2895(-1.8%) 3171(+7.6%) 3185(8.0%) Oats 2785 2611(-6.2%) 2870(+3.1%) 2888(+3.7%) Spring turnip rape 1305 1228(-5.9%) 1376(+5.5%) 1388(+6.4%) Frequency of fungicide treated barley and wheat/ farm 0 0 0 Average pH/ farm 5.71 6.56 6.65 Total gross margin €/farm, over 30 years 55 739 64 815 78 181 GHG emissions tons CO2 eq. /year (normalised per 10 ha/year) 24.12 30.89 34.83
  • 12. © Natural Resources Institute Finland Simulated results under A2 and B1 climate scenarios B1 GISS A2 IPSL Regional average yields kg/ha Simulated Yield (MCWLA bio.phys. model) Simulated Yield (Economic model) Simulated Yield (MCWLA bio.phys. model) Simulated Yield (Economic model) LP BP HP LP BP HP Spring wheat [3086] 3927 4008 (+2.1%) 4020 (+2.4%) 4026 (+2.5%) 3685 3755 (+1.9%) 3766 (+2.2%) 3778 (+2.5%) Winter wheat [3051] 3623 3402 - - - Barley [2948] 3939 4231 (+7.4%) 4321 (+9.7%) 4396 (+11.6%) 3697 3962 (+7.2%) 4016 (+8.6%) 4101 (+10.9%) Oats [2785] 3543 3680 (+3.9%) 3688 (+4.1%) 3711 (+4.7%) 3325 3458 (+4.0%) 3461 (+4.1%) 3472 (+4.4%) Oilseed [1305] 1660 1761 (+6.1%) 1766 (+6.4%) 1773 (+6.8%) 1558 1647 (+5.7%) 1662 (+6.7%) 1660 (+6.5%) Frequency of fungicide treated barley and wheat/ farm [0] 0 112 198 0 53 177 Average pH/ farm [6.56] 6.62 6.67 6.69 6.58 6.66 6.68 Total profit €/farm/year [10803] 16777 20644 24474 15050 19243 22849 GHG emissions overall tons CO2 eq. /year (normalized per 10 ha/year) [30.89] 31.68 33.59 34.79 29.79 33.67 34.79
  • 13. © Natural Resources Institute Finland Land allocation: Baseline (left) vs. A2 IPSL (right) SWheat WWheat Barley Oats Oilseed Setaside NMF SWheat WWheat Barley Oats Oilseed Setaside NMF SWheat WWheat Barley Oats Oilseed Setaside NMF SWheat WWheat Barley Oats Oilseed Setaside NMF SWheat WWheat Barley Oats Oilseed Setaside NMF SWheat WWheat Barley Oats Oilseed Setaside NMF LP BP HP
  • 14. © Natural Resources Institute Finland GHG emissions per kg produced decrease if higher yields - increase if higher prices (due to concave production functions, decreasing marginal effect of inputs) Baseline A2 IPSL B1 GISS Barley yield (kg/ha) 3171 4016 4321 Total crop production (tons per year per 10 ha) 24.225 36.529 39.135 Gross margin per farm per year (eur)(average over 30 years) 10.803 19.243 20.644 GHG emissions (tons CO2 eq. Per 10 ha) 30.89 33.67 33.59 GHG emissions per ton produced (tons CO2 eq./ton) 1.28 0.92 0.86 Emissions per unit produced (tons CO2 eq./ton) LP BP HP BASE 1.75 1.28 1.22 A2 IPSL 0.95 0.92 0.95 B1 GISS 0.85 0.86 0.89 Emissions per unit (tons CO2 eq. /ton), set aside land excluded LP BP HP BASE 0.87 1.03 1.10 A2 IPSL 0.76 0.85 0.87 B1 GISS 0.78 0.79 0.82 LP = -20% from baseline prices BP = Baseline prices 2000- 2013 HP = +20% from baseline prices
  • 15. © Natural Resources Institute Finland Conclusive remarks • Crop modelling results suggest increase of spring cereals yields from current 3 t/ha up to 3.5-3.6 t/ha (winter wheat; +15-20%) and to 4 t/ha (barley, spring wheat; +30%) until 2040-2070 in A2, B1 • Higher yields incentivize higher soil pH (liming), fungicide use and thus a further increase yields by 2-12% • Economic model results suggest that barley production becomes dominating if yields increase, due to lower (historical) gross margin variability and strong fungicide response of yields • 26-36% higher yields would imply 50-60% higher production and 36-46% higher gross margins per farm in scenarios B1, A2 - from current low levels • GHG emissions per kg produced decrease by 27-33% • The results suggest that current unexploited production potential will be used if 20-30% higher yields, but 30% less GHG emissions per kg produced – There are possibilities for ”sustainable intensification”
  • 16. © Natural Resources Institute Finland Thank you for your attention! References: • Liu, X., Lehtonen, H., Purola, T., Pavlova, Y., Rötter, R. & Palosuo, T. 2016. Dynamic economic modelling of crop rotations with farm management practices under future pest pressure. Agricultural Systems (2016), pp. 65-76 DOI: 10.1016/j.agsy.2015.12.003 • Lehtonen, H., Liu, X. and Purola, T. 2016. Balancing climate change mitigation and adaptation with socio-economic goals at farms in northern Europe. In: Paloviita, A. and Järvelä, M. (Eds) 2015. Climate Change Adaptation and Food Supply Chain Management (Routledge Advances in Climate Change Research), Routledge, London, 264 pp. ISBN13: 978-1138796669; http://www.tandf.net/books/details/9781317634034/. p. 132-146 • Lehtonen, H., 2001. Principles, structure and application of dynamic regional sectormodel of Finnish agriculture Academic dissertation Systems Analysis Laboratory, Helsinki University of Technology. Publications 98. Agrifood Research Finland, Economic Research (MTTL), Helsinki. • Myyrä, S., Ketoja, E., Yli-Halla,M., Pietola, K., 2005. Land improvements under land tenure insecurity: the case of pH and phosphate in Finland. Land Econ. 81 (4), 557–569. • Purola, T., 2013. Taudinkestävien ja tautialttiiden ohralajikkeiden taloudellinen vertailu. Master thesis University of Helsinki. Department of economics and management. (https://helda.helsinki.fi/handle/10138/40225) • Tao F, Rötter RP, Palosuo T, Höhn J, Peltonen-Sainio P, Rajala A, Salo T. 2015. Assessing climate impacts on wheat yield and water use in Finland using a super-ensemble-based probabilistic approach. Climate Research, 65, 23-37.
  • 17. © Natural Resources Institute Finland Thank you! 24.10.201717