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Evaluating Economic Impacts of
Agricultural Research: Examples
and Lessons
George W. Norton
Agricultural
and Applied
Economics
Seminar at the International Center for Tropical Agriculture (CIAT),
Cali, Colombia, June 30, 2015
Introduction
 Growing demand for impact assessment of
agricultural research
 Improvements in assessment methods
 Agriculture faces dynamic environment
 Population, income, climate, energy, pests
 Multiple goals and non-priced benefits
 Institutionalized system for research data
management useful for impact assessment
Objectives
 Key impact evaluation issues
 Assessment examples
 Lessons
Key Impact Evaluation Issues
1. Counterfactual (what would have
happened without the research)
2. Multiple objectives
3. Aggregation
4. Integrating impact assessment with
research data management
D
S0
S1
Price
Quantity
0
P0
P1
d
a
b
c
I0
I1
Q0 Q1
R
Bt = P0Q0K(1+.5Ken/(e+n)) =
Where: (1) K = (a-c)/a reflects yield and cost changes, technology adoption,
probability of success, and (2) e and n = supply and demand elasticities
1. Identifying what would have happened
without the research
Estimating K is Key
Kt=((E(Y)/ε) - (E(C)/(1+E(Y) )At(1-d)t
Kt = Per unit cost reduction
E(Y) = proportionate yield increase per ha for
adopters
ɛ = the price elasticity of supply
E(C) = the proportionate variable input cost change
per hectare
A = proportion of the area affected by the technology
d = the technology depreciation rate
Approaches for estimating K
• For specific technologies, can obtain K from:
• Expert opinions of scientists and others
• Input and yield data from biological field
experiments in budgets combined with
adoption data from surveys
• Farm-level survey data in regressions (e.g.,
using instrumental variables, propensity score
matching, double difference)
• Randomized controlled trials (RCTs);villages
and farmers are randomized with treated
(receives technology) and untreated groups
• Usefulness narrow for research evaluation
Retrospective (Ex Post) versus
Prospective (Ex Ante)
 Impact assessment methods can be
similar, but data sources differ
 Analysis often part ex ante, part ex post
 Probabilities and expectations are key in
ex ante impact analysis
 (Probability of research success) X
(Expected cost change per unit) X
(Expected adoption ratet)
Example of estimating K (part
ex ante, part ex post)
 Myrick et al (2014): benefits of
biocontrol program for papaya
mealybug in Southern India
 Benefits of more than $500 million on an
investment of $500,000
Ex post: CIAT-VT (DIVA) evaluation of
bean varieties in Rwanda and Uganda
 Larochelle et al (2015)
 Yield impacts estimated econometrically (IV)
with plot-level data from 1440 households in
Rwanda and 1908 H.H. in Uganda
 Compared counterfactual and actual income
distributions -- Poverty
would have been 0.4 and
0.1 percent higher in
Rwanda and Uganda in
absence of the improved
bean varieties.
Counterfactual for the Value of
CIP Genebank
 Study underway to assess, for
varieties that used material (genetic
resources) from CIP Genebank, what
it would have cost to obtain the
desired traits elsewhere without using
the Genebank.
 Provides lower bound but credible
economic estimate of GB value
2. Managing Multiple objectives
 Productivity/Income
 Poverty
 Environment
 Health/nutrition
 Risk/Resilience
 Gender
Tradeoffs among objectives; effects on
some easier to measure than others
Price
Quantity0
S0
S1
D
P0
P1
a
b
cd
I0
I1
Q0 Q1
a) Productivity or Income Impacts
Δ TS = +
Δ CS = +
Δ PS = -
Example: Ex post impacts of improved
maize varieties in rural Ethiopia
 Zeng et al (2015) Plot-level yield and cost
changes due to adoption were estimated in an
IV econometric model
 Results were included in an economic surplus
model to identify the counterfactual household
income that would have existed without
improved maize varieties.
 Poverty differences assessed -- Improved
maize varieties have led to a 0.8–1.3
percentage drop in poverty headcount ratio
b) Poverty Impacts
 Income gains can be estimated, adoption assessed, and
change in poverty rate calculated using a poverty index
(such as Foster-Greer-Thorbecke) or by calculating
income distributions with and without the intervention.
Assessing changes in poverty indexes or distributions
are complementary with RCTs, IVs, economic surplus
analyses, and other impact assessment methods.
Example
 Moyo et al (2007) calculated economic
surplus changes from virus resistant
groundnut varieties, disaggregating
income and poverty rate changes from
FGT poverty index to (a) adopters who
were also groundnut consumers, (b)
adopters who were not, and (c)
consumers who were not groundnut
producers (.5% to 1.5% poverty
reduction)
c) Environmental or Sustainable
Intensification Impacts
 Many methods for assessing bio-
physical (RCT, IV) and economic
values (CV, Choice Experiment,
Benefit Transfer)
 Must document research-induced
biophysical changes first
 Soil loss avoided, pesticide risk reduction,
carbon sequestered, etc.
 Then value non-market benefits of
technology or policy change
Examples
 Using contingent valuation, Cuyno et al.,
(2001) estimated the value of environmental
benefits from IPM-induced pesticide risk
reduction on onions to be $150,000 per year
in six villages in the Philippines.
 Using a choice experiment, Vaiknoras et al.,
(2015) estimated that farmers would be
willing to pay $10 per hectare in eastern
Uganda for a one-half reduction in soil
erosion per year.
d) Nutrition/Health Impacts
 More nutritious food has complex
impact pathways
 For micro-nutrients, can use RCT or IV
analysis to establish change in nutrient
consumption due to the intervention and
calculate disability-adjusted life years
 For macro-nutrients, combine results
from analysis of production and income
changes with demand system to project
consumption (and nutrient) changes
Example: Biofortified Cassava
 Nguema et al (2011)
Tj = total number of people in target group j
Mj = mortality rate associated with the deficiency in target group j
Lj = average remaining life expectancy for target group j
Iij = incidence rate of disease i in target group j
Dij = disability weight for disease i in target group j
dij = duration of disease i in target group j (for permanent
diseases dij equals the average remaining life expectancy Lj)
r = discount rate for future life years
DALYs lost to Vitamin A deficiency in
Nigeria and DALYs saved by bio-fortified
cassava
e) Risk/Resilence Impacts
 Important due to climate change effects on poor
 Benefits from reduction in yield variance
Kostandini et al (2011):
B/Y0= .5R (Y0) (σ2
Y0 - σ2
Y1)
 where B is the money value of reduction in income variation,
 R is coefficient of relative risk aversion
 Y0 is the mean of the income distribution before the technology
 Y1 is the mean after the new technology
 σ2
Y0 is CV squared for income distribution before the new
technology and σ2
Y1 is CV squared for the income distribution
after the new technology.
Example
 Kostandini et al., (2009) found the ex
ante benefits of drought-tolerance
research on cereals in eight African
countries to total more than $1 billion
per year with almost half of the
benefits due to yield variance
reduction
f) Gender Impacts
 Few quantitative assessments of gender
impacts of agricultural R&D
 Change in gender empowerment index
 Gender-disaggregated adoption analyses
3. Addressing Aggregation
 Project, program, portfolio
 Field, farm, market
 Research Spillovers
Impact Matrix to Organize Data
and Methods to Aggregate up
 
Level for which impact 
observed/assessed
 
Minimum 
Data used
 
Type of 
analysis/ 
model
Indicators Measured/Modeled
Outputs
Human Welfare Outcomes
Environment
Income Poverty
Nutrition/
health
International              
National                
Region/sub-sector/
ecosystem
             
Farm/Household/ 
Enterprise
             
Plot/Field/…              
4. Integrating impact assessment with
research data management
 In-house research impact assessment
capacity is important
 Key data for impact assessment are
often lost over time
 Need an IT system for entering and
storing data on inputs, yields, and other
traits from (1) near final trials, (2)
adoption surveys
 Used for internal and external assessments
Example
 Reviewing research data management
system at CIP and possibilities for
improving it for impact assessment
 Met with program leaders to discuss
major topics related to CIP strategic plan
 Identified candidates for assessment,
methods and data needs
 Reviewed current research data collection
by RIU and suggesting possible changes to
make it more useful in the future
 Undertaking impact case studies
Lessons
 Many research evaluation methods are
complementary in addressing multiple
objectives
 RCTs are unfortunately less useful for
assessing agricultural research impacts
than for other development interventions
 Tradeoff between cost and credibility of
impact assessment
 Need plan for collecting and managing data
from scientists to facilitate assessment

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Evaluating economic impacts of agricultural research ciat

  • 1. Evaluating Economic Impacts of Agricultural Research: Examples and Lessons George W. Norton Agricultural and Applied Economics Seminar at the International Center for Tropical Agriculture (CIAT), Cali, Colombia, June 30, 2015
  • 2. Introduction  Growing demand for impact assessment of agricultural research  Improvements in assessment methods  Agriculture faces dynamic environment  Population, income, climate, energy, pests  Multiple goals and non-priced benefits  Institutionalized system for research data management useful for impact assessment
  • 3. Objectives  Key impact evaluation issues  Assessment examples  Lessons
  • 4. Key Impact Evaluation Issues 1. Counterfactual (what would have happened without the research) 2. Multiple objectives 3. Aggregation 4. Integrating impact assessment with research data management
  • 5. D S0 S1 Price Quantity 0 P0 P1 d a b c I0 I1 Q0 Q1 R Bt = P0Q0K(1+.5Ken/(e+n)) = Where: (1) K = (a-c)/a reflects yield and cost changes, technology adoption, probability of success, and (2) e and n = supply and demand elasticities 1. Identifying what would have happened without the research
  • 6. Estimating K is Key Kt=((E(Y)/ε) - (E(C)/(1+E(Y) )At(1-d)t Kt = Per unit cost reduction E(Y) = proportionate yield increase per ha for adopters ɛ = the price elasticity of supply E(C) = the proportionate variable input cost change per hectare A = proportion of the area affected by the technology d = the technology depreciation rate
  • 7. Approaches for estimating K • For specific technologies, can obtain K from: • Expert opinions of scientists and others • Input and yield data from biological field experiments in budgets combined with adoption data from surveys • Farm-level survey data in regressions (e.g., using instrumental variables, propensity score matching, double difference) • Randomized controlled trials (RCTs);villages and farmers are randomized with treated (receives technology) and untreated groups • Usefulness narrow for research evaluation
  • 8. Retrospective (Ex Post) versus Prospective (Ex Ante)  Impact assessment methods can be similar, but data sources differ  Analysis often part ex ante, part ex post  Probabilities and expectations are key in ex ante impact analysis  (Probability of research success) X (Expected cost change per unit) X (Expected adoption ratet)
  • 9. Example of estimating K (part ex ante, part ex post)  Myrick et al (2014): benefits of biocontrol program for papaya mealybug in Southern India  Benefits of more than $500 million on an investment of $500,000
  • 10. Ex post: CIAT-VT (DIVA) evaluation of bean varieties in Rwanda and Uganda  Larochelle et al (2015)  Yield impacts estimated econometrically (IV) with plot-level data from 1440 households in Rwanda and 1908 H.H. in Uganda  Compared counterfactual and actual income distributions -- Poverty would have been 0.4 and 0.1 percent higher in Rwanda and Uganda in absence of the improved bean varieties.
  • 11. Counterfactual for the Value of CIP Genebank  Study underway to assess, for varieties that used material (genetic resources) from CIP Genebank, what it would have cost to obtain the desired traits elsewhere without using the Genebank.  Provides lower bound but credible economic estimate of GB value
  • 12. 2. Managing Multiple objectives  Productivity/Income  Poverty  Environment  Health/nutrition  Risk/Resilience  Gender Tradeoffs among objectives; effects on some easier to measure than others
  • 13. Price Quantity0 S0 S1 D P0 P1 a b cd I0 I1 Q0 Q1 a) Productivity or Income Impacts Δ TS = + Δ CS = + Δ PS = -
  • 14. Example: Ex post impacts of improved maize varieties in rural Ethiopia  Zeng et al (2015) Plot-level yield and cost changes due to adoption were estimated in an IV econometric model  Results were included in an economic surplus model to identify the counterfactual household income that would have existed without improved maize varieties.  Poverty differences assessed -- Improved maize varieties have led to a 0.8–1.3 percentage drop in poverty headcount ratio
  • 15. b) Poverty Impacts  Income gains can be estimated, adoption assessed, and change in poverty rate calculated using a poverty index (such as Foster-Greer-Thorbecke) or by calculating income distributions with and without the intervention. Assessing changes in poverty indexes or distributions are complementary with RCTs, IVs, economic surplus analyses, and other impact assessment methods.
  • 16. Example  Moyo et al (2007) calculated economic surplus changes from virus resistant groundnut varieties, disaggregating income and poverty rate changes from FGT poverty index to (a) adopters who were also groundnut consumers, (b) adopters who were not, and (c) consumers who were not groundnut producers (.5% to 1.5% poverty reduction)
  • 17. c) Environmental or Sustainable Intensification Impacts  Many methods for assessing bio- physical (RCT, IV) and economic values (CV, Choice Experiment, Benefit Transfer)  Must document research-induced biophysical changes first  Soil loss avoided, pesticide risk reduction, carbon sequestered, etc.  Then value non-market benefits of technology or policy change
  • 18. Examples  Using contingent valuation, Cuyno et al., (2001) estimated the value of environmental benefits from IPM-induced pesticide risk reduction on onions to be $150,000 per year in six villages in the Philippines.  Using a choice experiment, Vaiknoras et al., (2015) estimated that farmers would be willing to pay $10 per hectare in eastern Uganda for a one-half reduction in soil erosion per year.
  • 19. d) Nutrition/Health Impacts  More nutritious food has complex impact pathways  For micro-nutrients, can use RCT or IV analysis to establish change in nutrient consumption due to the intervention and calculate disability-adjusted life years  For macro-nutrients, combine results from analysis of production and income changes with demand system to project consumption (and nutrient) changes
  • 20. Example: Biofortified Cassava  Nguema et al (2011) Tj = total number of people in target group j Mj = mortality rate associated with the deficiency in target group j Lj = average remaining life expectancy for target group j Iij = incidence rate of disease i in target group j Dij = disability weight for disease i in target group j dij = duration of disease i in target group j (for permanent diseases dij equals the average remaining life expectancy Lj) r = discount rate for future life years
  • 21. DALYs lost to Vitamin A deficiency in Nigeria and DALYs saved by bio-fortified cassava
  • 22. e) Risk/Resilence Impacts  Important due to climate change effects on poor  Benefits from reduction in yield variance Kostandini et al (2011): B/Y0= .5R (Y0) (σ2 Y0 - σ2 Y1)  where B is the money value of reduction in income variation,  R is coefficient of relative risk aversion  Y0 is the mean of the income distribution before the technology  Y1 is the mean after the new technology  σ2 Y0 is CV squared for income distribution before the new technology and σ2 Y1 is CV squared for the income distribution after the new technology.
  • 23. Example  Kostandini et al., (2009) found the ex ante benefits of drought-tolerance research on cereals in eight African countries to total more than $1 billion per year with almost half of the benefits due to yield variance reduction
  • 24. f) Gender Impacts  Few quantitative assessments of gender impacts of agricultural R&D  Change in gender empowerment index  Gender-disaggregated adoption analyses
  • 25. 3. Addressing Aggregation  Project, program, portfolio  Field, farm, market  Research Spillovers
  • 26. Impact Matrix to Organize Data and Methods to Aggregate up   Level for which impact  observed/assessed   Minimum  Data used   Type of  analysis/  model Indicators Measured/Modeled Outputs Human Welfare Outcomes Environment Income Poverty Nutrition/ health International               National                 Region/sub-sector/ ecosystem               Farm/Household/  Enterprise               Plot/Field/…              
  • 27. 4. Integrating impact assessment with research data management  In-house research impact assessment capacity is important  Key data for impact assessment are often lost over time  Need an IT system for entering and storing data on inputs, yields, and other traits from (1) near final trials, (2) adoption surveys  Used for internal and external assessments
  • 28. Example  Reviewing research data management system at CIP and possibilities for improving it for impact assessment  Met with program leaders to discuss major topics related to CIP strategic plan  Identified candidates for assessment, methods and data needs  Reviewed current research data collection by RIU and suggesting possible changes to make it more useful in the future  Undertaking impact case studies
  • 29. Lessons  Many research evaluation methods are complementary in addressing multiple objectives  RCTs are unfortunately less useful for assessing agricultural research impacts than for other development interventions  Tradeoff between cost and credibility of impact assessment  Need plan for collecting and managing data from scientists to facilitate assessment