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Technology adoption and the multiple dimensions of food security: the case of maize in Tanzania

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Abstract

The paper analyses the impact of agricultural technologies on the four pillars of food security for maize farmers in Tanzania. Relying on both matching techniques and endogenous switching regression models, we used a nationally representative dataset collected over the period 2010/2011 to estimate the causal effects of using improved seeds and inorganic fertilizers on food availability, access, utilization, and stability. Our results show that the adoption of both technologies have positive and significant impacts on food availability while for access, utilization and stability we observe heterogeneity between improved seeds and inorganic fertilizers as well as across the food security pillars. The study supports the idea that the relationship between agricultural technologies and food security is a complex phenomenon, which cannot be limited to the use of welfare indexes as proxy for food security.

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Notes

  1. Available at: http://data.worldbank.org/data-catalog/world-development-indicators.

  2. Available at: http://faostat.fao.org.

  3. See Appendix A for details of the empirical strategy to estimate the ERS model and the average treatment effect on the treated.

  4. Specifically, in the selection equation χ 2= 9.61 (p-value =0.008) and χ 2=78.01 (p-value =0.000) for improved seeds and inorganic fertilizers, respectively. For the total expenditure, for example, F = 0.54 (p-value = 0.59) for improved seed and F = 2.20 (p-value = 0.23) for inorganic fertilizers. Similar results were obtained for the other outcome variables with the exception of maize yield, which is influenced by extension services. In this case we substituted it with the asset proxy.

  5. Some may question the choice of using only the 2010/2011 survey without exploiting the dynamic dimension of the TZNPS. However, the previous available survey refers to 2008/2009 and the elapsed time between the two interviews could range between 13 and 36 month while the average is 24.05 months. As a consequence, between the two surveys the households went through two/three harvests from the short rainy seasons and other two/three harvests from the long rainy seasons. Such a large number of cycles make it very difficult to justify any connection between seeds or fertilizers adoption with food security outcomes and this is why we prefer limiting the analysis to the direct impacts of technologies after the harvest where they have been employed.

  6. The field work was conducted by the Tanzania National Bureau of Statistics (NBS) using four questionnaires on household, agriculture, fishery and community, and geospatial variables obtained by using the georeferenced plot and household locations in conjunction with various geospatial databases available to the survey team. The questionnaires and survey were designed in collaboration with line ministries, government agencies and donor partners (main donors were the European Commission and the World Bank).

  7. We could not use data from the short rainy season (Vuli) for two reasons. First, the short rainy season occurs only in some Northern and Eastern enumeration areas. Second, depending on the month when the individuals have been interviewed, data can be referred to the year 2009 instead of the period 2010/2011.

  8. The survey distinguished between traditional and improved seeds, where improved stands for hybrids.

  9. For all these reasons, we are prevented from using income as independent variable in the first stage of the PSM. In fact, income should be exogenous to the treatment but in this case data on economic activities needed to calculate the income proxy refer to a time span which goes from the pre-planting to the post-harvest period. As a consequence, income could be influenced by the treatment, leading to endogeneity issues, hence violating the conditional independence assumption.

  10. Table 6 in the Appendix reports the scoring factors used to build the index and the average ownership for the asset variables across different quintiles of the total consumption expenditure. The last row shows a positive correlation between the asset index and the quintiles of total expenditure. As shown by Filmer and Pritchett (2001), this can be interpreted as a good sign of reliability and internal coherence of the wealth proxy.

  11. The food expenditure includes all possible sources of consumption (i.e. purchases, own-production, gifts or barter) and it considers only what it was actually consumed by the household in the last seven days prior to the interview. Measure of prices to value own-production or food received as a gift or barter were obtained by calculating unit values from the information on the amount spent on purchases and on the quantity purchased for all food items (NBS 2012).

  12. As reported by Headey and Ecker (2013), there is an extensive literature showing a strong correlation between dietary diversity indicators and macro/μ-nutrient deficiency in developing countries, especially for anthropometric measures such as wasting and stunting. The authors conclude their work stating that dietary diversity indicators are the best performing class indicators for measuring food security because they correlate with economic status and malnutrition, are sensitive to shocks and seasonality, and easy to measure.

  13. A comprehensive review of the different vulnerability to poverty measures and the relative empirical strategies is provided in Hoddinott and Quisumbing (2003) and Ligon and Schechter (2004).

  14. See Appendix A2 for details about the measure and the empirical implementation of the vulnerability estimation.

  15. A more in depth analysis on the structural and environmental conditions that favour adoption in specific agro-ecological areas would be extremely helpful for designing better-targeted input subsidy programmes in large countries such as Tanzania. Shedding light on this issue goes beyond the scope of the present paper but it is a potentially interesting topic for future research on the determinants of technology adoption.

  16. The result does not include the cases where the ATT-NN(3) is not significant because - by definition – the hidden bias is equal to 1 such as in the case of staple share and vulnerability.

  17. For sake of completeness, it must be taken into consideration that the Rosenbaum bounds are a “worst-case” scenario (DiPrete and Gangl 2004). In fact, it does not imply the lack of impact on food security, but only that the confidence interval for the treatment effects could include zero if an unobserved covariate exists, which almost perfectly determines whether the outcomes would be different for the adopters and non-adopters in each pair of matched cases.

  18. For space limitation, results of the ESR regressions are not commented on in the paper but are available on request.

  19. The difference in the sign and magnitude of the results with respect to the matching methods should not be surprising considering that 1) we are using a parametric technique which implies specific distributional assumption for the errors terms and 2) the mean differences calculated with ESR regressions are obtained working with the full sample and not only on the matched units.

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Correspondence to Emiliano Magrini.

Appendix

Appendix

A1 - The Endogenous Switching Regression model

The endogenous switching regression model is defined by a selection Eq. (A.1) which establishes the regime of the household and two equations describing the food security outcome for adopters (A.2a) and non adopters (A.2b):

$$ {\mathrm{T}}_{\mathrm{i}}^{*}={\beta X}_{\mathrm{i}}+{\mathrm{u}}_{\mathrm{i}} $$
(A.1)
$$ {Y}_{1i}={\alpha}_1{C}_{1i}+{e}_{1i}\kern0.75em \mathrm{if}\kern0.75em {T}_i=1 $$
(A.2a)
$$ {Y}_{0i}={\alpha}_0{C}_{0i}+{e}_{0i}\kern0.75em \mathrm{if}\kern0.75em {T}_i=0 $$
(A.2b)

where \( {T}_i^{*} \) is the unobservable latent variable defining the technology adoption regime, T i its observable counterpart and X i the vector of covariates determining adoption. Y i refers to the food security outcome in regime 1 (adopters) and 0 (non adopters), while the set of covariates C are their determinants. The error terms u i , e 1i and e 0i are assumed to have a trivariate normal distribution with zero mean and a covariance matrix:

$$ \left[\begin{array}{ccc}\hfill {\upsigma}_{\mathrm{e}1}^2\hfill & \hfill \cdot \hfill & \hfill {\upsigma}_{\mathrm{e}1\mathrm{u}}\hfill \\ {}\hfill \cdot \hfill & \hfill {\upsigma}_{\mathrm{e}0}^2\hfill & \hfill {\upsigma}_{\mathrm{e}0\mathrm{u}}\hfill \\ {}\hfill \cdot \hfill & \hfill \cdot \hfill & \hfill {\upsigma}_{\mathrm{u}}^2\hfill \end{array}\right] $$
(A.3)

Since σ e1u . and σ e0u are different from zero, the expected values of the error terms of the food security outcomes are non-zero and equal to:

$$ E\left[\left.{e}_{1i}\right|{T}_i=1\right]={\sigma}_{e1u}\frac{\phi \left(\beta {X}_i\right)}{\varPhi \left(\beta {X}_i\right)}={\sigma}_{e1u}{\lambda}_{1i} $$
(A.4a)
$$ E\left[\left.{e}_{0i}\right|{T}_i=0\right]={\sigma}_{e0u}\frac{\phi \left(\beta {X}_i\right)}{1-\varPhi \left(\beta {X}_i\right)}={\sigma}_{e0u}{\lambda}_{0i} $$
(A.4b)

Where ϕ(⋅) and Φ(⋅) indicate, respectively, the standard normal density and standard normal cumulative functions. If the estimated covariances (\( {\hat{\sigma}}_{e1u} \) and \( {\hat{\sigma}}_{e0u} \)) turn out to be statistically significant, then the decision to adopt improved seed and inorganic fertilizers is correlated with the food security outcome, that is there is evidence of endogenous switching and the presence of sample selection bias (Maddala and Nelson, 1975; Di Falco et al. 2011).

The model is usually estimated using full information maximum likelihood (FIML) because it allows estimation simultaneously of the probit regression for technology adoption and the regression equations of the food security outcomes. Following Heckman et al. (2001), the results of the FILM estimation can be used to calculate the average treatment effect on the treated (ATT) by comparing the expected food security outcomes for adopters with their counterfactual scenario. In this case:

$$ \mathrm{E}\left[\left.{\mathrm{Y}}_{1\mathrm{i}}\right|{\mathrm{T}}_{\mathrm{i}}=1\right]={\upalpha}_1{\mathrm{C}}_{1\mathrm{i}}+{\upsigma}_{\mathrm{e}1\mathrm{u}}{\uplambda}_{1\mathrm{i}} $$
(A.5a)
$$ \mathrm{E}\left[\left.{\mathrm{Y}}_{0\mathrm{i}}\right|{\mathrm{T}}_{\mathrm{i}}=1\right]={\upalpha}_0{\mathrm{C}}_{1\mathrm{i}}+{\upsigma}_{\mathrm{e}0\mathrm{u}}{\uplambda}_{1\mathrm{i}} $$
(A.5b)
$$ ATT=E\left[\left.{Y}_{1i}\right|{T}_i=1\right]-E\left[\left.{Y}_{0i}\right|{T}_i=1\right]={C}_{1i}\left({\alpha}_1-{\alpha}_0\right)+{\lambda}_{1i}\left({\sigma}_{e1}^2-{\sigma}_{e0}^2\right) $$
(A.6)

A2 - The VEP estimation procedure

The calculation of the VEP index is based on the 3-steps Feasible Generalized Least Squares (FGLS) econometric procedure suggested by Amemiya (1977) to correct for heteroskedasticity. The starting point is the estimation through Ordinary Least Square (OLS) of a standard reduced-form of the consumption function based on the following simple linear econometric specification:

$$ {c}_{it}={X}_{it}\beta +{\varepsilon}_{it} $$
(A.7)

where citis the log of the real total consumption expenditure per adult-equivalent of household i at time t; Xit is the vector of exogenous variables which controls for the household’s characteristics and εit is an error term. In order to have robust estimates, the second step of the VEP method is calculating the residuals from the Eq. A.7 and running the following:

$$ {\varepsilon}_{OLS, it}^2={X}_{it}\theta +{\eta}_{it} $$
(A.8)

The predictions of Eq. (A.8) are thus used to weight the previous equation, obtaining the following transformed version:

$$ \frac{\varepsilon_{OLS, it}^2}{X_{it}{\hat{\theta}}_{OLS}}=\left(\frac{X_{it}}{X_{it}{\hat{\theta}}_{OLS}}\right)\theta +\left(\frac{\eta_{it}}{X_{it}{\hat{\theta}}_{OLS}}\right) $$
(A.9)

As reported by Chaudhuri et al. (2002), the OLS estimation of (A.9) gives us back an asymptotically efficient FGLS estimate, \( {\hat{\uptheta}}_{\mathrm{FGLS}} \), and thus \( {\mathrm{X}}_{\mathrm{it}}{\hat{\uptheta}}_{\mathrm{FGLS}} \) is a consistent estimate of \( {\upsigma}_{\mathrm{it}}^2 \), the variance of the idiosyncratic component of household consumption. Then, we use the square root of the estimated variance, i.e. \( {\hat{\upsigma}}_{\mathrm{FGLS},\mathrm{it}} \), for transforming Eq. A.7 and obtaining asymptotically efficient estimates of β:

$$ \frac{c_{it}}{{\hat{\sigma}}_{FGLS,\mathrm{it}}}=\left(\frac{X_{it}}{{\hat{\sigma}}_{FGLS, it}}\right)\beta +\left(\frac{\varepsilon_{it}}{{\hat{\sigma}}_{FGLS, it}}\right) $$
(A.10)

Once we have these estimates, it is possible to compute both the expected log consumption and its variance for each household of our sample as follows:

$$ \widehat{E}\left[\left.{c}_{it}\right|\ {X}_{it}\right]={X}_{it}{\widehat{\beta}}_{FGLS} $$
(A.11)
$$ \widehat{var}\left[\left.{c}_{it}\right|\ {X}_{it}\right]={X}_{it}{\widehat{\theta}}_{FGLS} $$
(A.12)

Under the assumption that consumption is log-normally distributed and then log-consumption is normally distributed, we can calculate the probability that household i will be poor in the future, given its characteristics X at time t as follow:

$$ {\widehat{V}}_{it}= \Pr \left[\left(\operatorname{}{C}_{i,t+1}<Z\right)\left|{X}_{it}\right)\right]=\Phi \left(\frac{lnz-\widehat{E}\left(\operatorname{}{c}_{it}\Big|{X}_{it}\right)}{\sqrt{\widehat{var}\left(\operatorname{}{c}_{it}\Big|{X}_{it}\right)}}\right) $$
(A.13)

where Φ(⋅) indicates the cumulative density function of the standard normal.

Table 6

Table 6 Scoring factors and summary statistics for the asset index

Table 7

Table 7 Balancing property of covariates

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Magrini, E., Vigani, M. Technology adoption and the multiple dimensions of food security: the case of maize in Tanzania. Food Sec. 8, 707–726 (2016). https://doi.org/10.1007/s12571-016-0593-7

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