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Agricultural Productivity Growth and Environmental Externalities
“Can Soil Conservation Practices Increase
Upland Farm Productivity?”Agnes C. Rola, Asa Jose U.
Sajise, Dieldre S. Harder, Joe Marvin Alpuerto
(Paper presented during the Asian Society of Ag Economists
Meeting, Makati,Philippines, 28-30 Aug. 2008)
Introduction
Present results from a larger study Southeast Asian Regional Center for
Graduate Study and Research in Agriculture (SEARCA) Productivity Growth for Philippine Agriculture Project
Project component on Agricultural Productivity and Environmental Externality
Upland-Lowland Agriculture (Aggie to Aggie externality)
In-Situ Effects of Soil Erosion on Upland Farm Productivity
Technology Adoption & Soil Erosion
Soil Erosion and Irrigation Systems
Introduction: Detail of Larger Study
Ex-Situ Effects of Soil Erosion (thru Irrigation Systems) on Lowland Farm Productivity
Review of Literature on Upland Corn Cultivation and Soil Erosion
Empirical Case Study: Panel Data Analysis
Review of Literature on Irrigation and Lowland Farm Productivity
“Empirical” Case Study: Productivity Change Analysis
Focus of Presentation
Rationale for Scope of the Study
Ecosystem: Upland Agricultural Systems Commodity: Corn Natural Resource Base: Soil Environmental Factor: Soil Loss/ Erosion Why?
Soil erosion has been identified as a leading problem in upland resource management
Upland areas will be the potential bread basket because of dwindling lowland areas
Huge amount of R and D investments on soil erosion control (agroforestry, SALT, etc.)
General Methodology
No direct measure of soil erosion Therefore, look at the indirect
relationship Adoption practices -> Soil Loss -> Decline/
Increase in Productivity Review literature on corn production and
soil erosion Case Study: use data and estimate a
panel stochastic frontier on a primal production determination function
Empirical Methodology
Posit the following yield/ production determination function: Corn Yieldit =f(Ωit, θit, dit)
where Ωit is a vector of household/ plot characteristics
for household i at time t Θt is a vector of economic/ institutional /
physical variables for household i at time t dit is an indicator variable d=1 if adopts a soil
conservation practice, assumes value of 0 otherwise for household i at time t
Econometric Specification: Stochastic Frontier Corn Yieldit =f(Ωit, θit, dit) + εit + μit
where εit is the usual error term for household i at
time t μit is the truncated error term that
represents technical inefficiency for household i at time t
Furthermore we specify a time varying technical efficiency term of the form
( ( ))
2( , )
it Tit
iid
i
e
where
N
Econometric Issue
Adopting a conservation measure or not is endogenous A function of some set of variables
A better or alternative way to look at it: Measurement error soil erosion is a latent variable (in the
absence of an indicator) or may not be measured properly
using only adoption of soil conservation technology as a proxy
Roughly: Prob(d=1) = soil erosion + Є
Solution: Two Stage Estimation or Treatment Effects 1st Stage: Discrete Choice
Probit on discrete decision to adopt Get Mill’s ratio for non-adoption and
adoption 2nd Stage: Stochastic Frontier
Revised specification: E[Corn Yield|Ωit,θit,1]= f(Ωit,θit,1) + E[Corn Yield|Ωit,θit,0]=f(Ωit,θit,0) +
)(
)(
z
zua
)(1
)(
z
zu
na
Results of Review of Literature: Some Statistics Corn production (kg./ha) in the
Philippines is lagging behind it’s SEA neighbors (FAO Statistics)
Country 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005
Ave
growth
rate
1995-2005
Cambodia 1,219 1,374 1,243 1,217 1,595 2,735 2,761 2,080 3,747 3,320 3,516 15.46
Indonesia 2,258 2,486 2,614 2,653 2,663 2,765 2,845 3,088 3,241 3,344 3,428 4.30
Malaysia 1,870 1,800 1,846 1,852 2,111 2,407 3,046 3,044 3,000 3,000 3,000 5.22
Myanmar 1,703 1,710 1,908 1,642 1,706 1,724 2,124 2,251 2,477 2,630 2,842 5.65
Philippines 1,521 1,592 1,589 1,624 1,735 1,797 1,820 1,803 1,915 2,142 2,045 3.10
Thailand 3,289 3,448 3,198 3,345 3,552 3,676 3,735 3,729 3,855 3,869 3,760 1.42
Viet Nam 2,114 2,498 2,490 2,481 2,534 2,747 2,963 3,076 3,436 3,462 3,569 5.52
Results of Review of Literature: Some Statistics In terms of agro-
zone Uplands has lower
minimum and maximum production
In general, wide range of production (i.e. more erratic)
Range of maize yield by agro-ecozone (t/ha) Type of maize
material Rainfed
lowlands Upland plains
Rolling-to-
hilly
Local/traditional
Most common - 1.0 – 2.0 0.1 – 2.5
Minimum attained - 0.5 – 1.5 0.1 – 3.0
Maximum attained - 1.0 – 2.0 0.2 – 3.8
Improved OPVs
Most common - 2.0 – 4.0 0.9 – 2.4
Minimum attained - 1.0 – 3.5 1.0 – 2.1
Maximum attained - 2.0 – 4.5 2.0 – 4.5
Hybrids
Most common 4.6– 6.0 3.0 – 5.7 1.6 – 5.0
Minimum attained 3.0– 5.0 1.5 – 5.0 2.0 – 4.3
Maximum attained 5.5– 9.0 4.0 – 7.0 4.0 – 7.0
Summary of Literature Review Yield gap is due to a variety of reasons:
biological constraints, soil and water constraints, socio-economic constraints, ‘erratic and unpredictable’ weather conditions and storms, use of sub-optimal fertilizer input due to capital constraints, soil acidity, and declining soil fertility
Literature acknowledges that corn in the uplands is very soil erosive
However, obviously dampened by adoption of technology (e.g. crop rotation, hedge rows, etc.)
Results of Empirical Study SANREM panel data
from 1994 to 2006 of from 195 households in 1994 to 80 households in 2006; and about 109 plots in 2006 Data series includes corn
input, output, soil conservation practices, demographic characteristics, some data on rainfall patterns, village level data on water quality
Site is in Lantapan Bukidnon
Casual look at trends in production show increasing production for adopters
05000
10000
1995 2000 2005 1995 2000 2005
0 1
Pro
duct
ion p
er
ha.
Year0 - Non-Adopters; 1 - Adopters
Production (per ha.), Adopters vs. Non-Adopters (1994-2006)
Data Problem
One problem is corn plot attrition (around 80%) Various reasons: out migration; shift to other crops
Can test for effects of attrition based on observables Use baseline data Regress yield with inputs, other variables and an
attrition indicator Test shows that attrition indicator is not
significant, implying attrition is not a real problem
Determinants of Technology Adoption Probability of
adoption higher in farms located in higher slopes
Favorable price expectations leads to higher likelihood of adoption
Households relying on family labor are more likely to adopt soil conservation technologies
Variable Coefficient Std. Err. Slope 0.15* 0.06 Watershed -0.05 0.24 Education of Household Head -0.03 0.08 Tenure -0.05 0.07 Age of Household Head -0.05 0.06 Squared Age of Household Head 0.00 0.00 Fertilizer Use -0.17 0.18 Favorable Price Expectation 0.38** 0.23 Above Mean Production -0.62* 0.17 Used Family Labor Only 0.61* 0.20 Year Dummies:
1996 -1.28* 0.24 1998 -1.27* 0.30 1999 -1.11* 0.27 2000 -0.36 0.28 2002 -0.98* 0.31 2006 -0.81* 0.34
Constant** 2.44** 1.43 * - significant at 5%
** - significant at 10%
Determinants of Technology Adoption (continued) Farms with higher
productivity are more likely to be put under a soil conservation regime
Adoption is also more likely during the base year than later years.
Variable Coefficient Std. Err. Slope 0.15* 0.06 Watershed -0.05 0.24 Education of Household Head -0.03 0.08 Tenure -0.05 0.07 Age of Household Head -0.05 0.06 Squared Age of Household Head 0.00 0.00 Fertilizer Use -0.17 0.18 Favorable Price Expectation 0.38** 0.23 Above Mean Production -0.62* 0.17 Used Family Labor Only 0.61* 0.20 Year Dummies:
1996 -1.28* 0.24 1998 -1.27* 0.30 1999 -1.11* 0.27 2000 -0.36 0.28 2002 -0.98* 0.31 2006 -0.81* 0.34
Constant** 2.44** 1.43 * - significant at 5%
** - significant at 10%
In-Situ Impact of Technology Adoption (Soil Erosion) on Upland Farm Productivity All production inputs
have the right signs and directly related to production
Adoption of soil conservation increases production implying that controlling erosion increases productivity among upland farms
Variables Coefficients Std. Err. Production Inputs: Ln (Seed Inputs)
0.12* 0.05
Ln (Urea Applied)
0.09* 0.03
Ln (Manure Applied)
0.05** 0.03
Ln (Complete Fertilizer Applied)
-0.03 0.02
Ln (Man-days of HH Labor)
0.13* 0.03
Ln (Man-days Hired Labor)
0.06* 0.03
Biophysical Variables
Drought Dummy
-1.27* 0.13
Watershed Dummy
-0.38* 0.19
Slope Dummy 0.02 0.05 Adoption Dummy
0.82* 0.29
Interaction Term Between Watershed and Adoption
0.45* 0.20
Interaction Term Between Slope and Adoption
0.02 0.06
Mills Ratio -0.79* 0.11 Constant 6.71* 0.24
In-Situ Impact of Technology Adoption (Soil Erosion) on Upland Farm Productivity Drought dummy for
(1997=8;others=0) drastically reduced production
Farms located in higher watershed also had lower corn yields
However, the interaction term between watershed location and adoption imply that farmers in the upper watershed who use soil conservation techniques will tend to have higher yields Soil conservation can
mitigate locational disadvantages
Variables Coefficients Std. Err. Production Inputs: Ln (Seed Inputs)
0.12* 0.05
Ln (Urea Applied)
0.09* 0.03
Ln (Manure Applied)
0.05** 0.03
Ln (Complete Fertilizer Applied)
-0.03 0.02
Ln (Man-days of HH Labor)
0.13* 0.03
Ln (Man-days Hired Labor)
0.06* 0.03
Biophysical Variables
Drought Dummy
-1.27* 0.13
Watershed Dummy
-0.38* 0.19
Slope Dummy 0.02 0.05 Adoption Dummy
0.82* 0.29
Interaction Term Between Watershed and Adoption
0.45* 0.20
Interaction Term Between Slope and Adoption
0.02 0.06
Mills Ratio -0.79* 0.11 Constant 6.71* 0.24
Other interesting insights
Calculated marginal effects for each variable Marginal effects show that the impact of adoption
on productivity is higher compared to the productivity effects of conventional input usage (singly or combined)
The technical inefficiency term is increasing across time Some farmers are indigenous people (IP), thus, practices
time old traditional conservation and cultivation Why then is there declining efficiency?
Labor opportunities in the lowland More variability in weather
Summary and Policy Implications (so far) Target extension (and R and D) efforts
on the upper watersheds There are productivity gains to R and D
efforts and soil conservation adoption. Gains commensurate (or even higher) than efforts to increase productivity through encouraging input use Another bite at the Green Revolution
Summary Preview in the Context of the Larger Study Our initial review of literature for the
latter half of the study Hard to trace soil erosion from upland
farms to irrigation systems Many other sources of soil erosion (mining,
roads, etc.) Not all soil erosion goes directly towards
the irrigation systems. Some ends up in the banks of rivers and other reservoirs
Summary Preview in the Context of the Larger Study Point #1: Literature is clear however that
large development (and more disruptive land use changes like mining) are more likely to be more significant sources of soil erosion
Point # 2: Soil erosion from upland farms may therefore have very miniscule impact on irrigation systems and therefore on lowland agriculture
Point #1 + Point #2 implies that aggie to aggie externality may not be that great an issue
Summary Preview in the Context of the Larger Study Can we therefore justify intervention on
the basis of efficiency? Results of the larger study say: Maybe Not But it maybe justified on equity grounds,
i.e. to increase production (and thus income) in poverty stricken upland areas
We have been doing the right things for the wrong reasons because of lack of empirics.
What we failed to get
Actual irrigation and farm data in the lowland areas
Focused on aggie to aggie or farm to farm externalities
What about Farm to Fish externalities? Large part of eroded soil goes to coastal
areas and river banks Coastal non-point source pollution is a big
issue But this might be a more wieldy study
Maraming Salamat Po