World Development Vol. 39, No. 1, pp. 77–86, 2011 Crown Copyright Ó 2010 Published by Elsevier Ltd. All rights reserved 0305-750X/$ - see front matter www.elsevier.com/locate/worlddev doi:10.1016/j.worlddev.2010.06.010 An Inquiry into Constraints on a Green Revolution in Sub-Saharan Africa: The Case of NERICA Rice in Uganda YOKO KIJIMA University of Tsukuba, Ibaraki, Japan KEIJIRO OTSUKA Foundation for Advanced Studies on International Development (FASID), Tokyo, Japan National Graduate Institute for Policy Studies (GRIPS), Tokyo, Japan and DICK SSERUNKUUMA * Makerere University, Kampala, Uganda Summary. — In Uganda, New Rice for Africa (NERICA), a high-yielding upland rice variety suitable for the African environment, was introduced to increase food security and reduce poverty in rural areas in 2002. However, more than 50% of the NERICA adopters in 2004 had abandoned it in 2006. The regression results indicate that the low profitability of NERICA relative to alternative crops in variable rainfall areas explains the massive dropout. It is also found that the profitability of NERICA production was low when farmerproduced seeds were used in 2006, suggesting the weak dissemination of appropriate information on seed production to rice farmers. Crown Copyright Ó 2010 Published by Elsevier Ltd. All rights reserved. Key words — Green Revolution, technology adoption, NERICA, Uganda, Africa, panel data 1. INTRODUCTION the average yield of NERICA per hectare is found to be 2.5 tons on farm in Uganda (Kijima, Sserunkuuma, & Otsuka, 2006), which is significantly higher than the average upland rice yield of one ton per hectare in SSA (Balasubramanian, Sie, Hijmans, & Otsuka, 2007). Moreover, there is evidence that the adoption of NERICA increases the income of NERICA adopters significantly (Adekambi, Diagne, Simtowe, & Biaou, 2008; Kijima, Otsuka, & Sserunkuuma, 2008). In addition to these characteristics, another advantage of NERICA is that the seeds can be self-produced by farmers as with other rice varieties. Hence, there is no need to purchase new seeds for several years, which enables the wide adoption of NERICA even in countries in which rice seed markets are underdeveloped. 1 Even though NERICA varieties seem to have great potential for realizing rice Green Revolution in SSA, the adoption rate is still low except in a few countries (Rodenburg et al., 2006). One reason for this low adoption rate is the farmers’ low exposure to NERICA varieties (Diagne, 2006; Diagne & Demont, 2007; Spencer, Dorward, Abalu, Philip, & Ogungbile, 2006). The low exposure in West African countries was The recent sudden and sharp increase in food prices in international markets has significantly and adversely threatened food security in developing countries, especially in Sub-Saharan Africa (SSA), which is a net importer of food grains (Benson, Mugarura, & Wanda, 2008; Ivanic & Martin, 2008). There is, thus, an urgent need to increase food production to alleviate the widespread poverty and food insecurity in this region. Given the increasingly limited room for the further expansion of cultivated area in many countries in SSA, there is no substitute for a Green Revolution, which enhances crop yield per unit of land, in an effort to boost the food production in SSA (Diao, Headey, & Johnson, 2008; Otsuka & Kijima, in press). Since most of the increased consumption of rice associated with urbanization and change in diet is currently filled by imports ( Africa Rice Center, 2008), the scarce foreign reserves that could have been used for the import of capital goods and materials necessary for economic development are actually used for rice imports. Thus, a Green Revolution in rice production is urgently required in this region. One of the ways of realizing a rice Green Revolution is to expand the adoption of New Rice for Africa (NERICA) varieties, high-yielding upland rice varieties suitable for the African environment developed by the Africa Rice Center (or WARDA). NERICA varieties have traits of traditional rice varieties in SSA (Oryza glaberrima) characterized by good weed competitiveness and resilience against major African biotic and abiotic stresses and Asian rice varieties (Oryza sativa) characterized by good yields, and absence of lodging and grain shattering, and high fertilizer returns (Jones, Dingkuhn, Aluko, & Semon, 1997; Wopereis, Diagne, Rodenburg, Sié, & Somado, 2008). Indeed, * We would like to thank Peter Hazell, Derek Barley, Takashi Yamano, Don Larson, Tomoya Matsumoto, Kei Kajisa, and four anonymous referees for very helpful comments. We have benefitted from discussions with participants of the Coalition for African Rice Development (CARD) meeting in Nairobi, the Center for the Study of African Economics (CSAE) meeting in Oxford, and the Theoretical Economics and Agriculture (TEA) meeting in Tsukuba, seminar at Nagoya University. We are grateful to Paul Kandasamy for editorial assistance. Final revision accepted: June 23, 2010. 77 78 WORLD DEVELOPMENT due to the lack of effective extension and seed delivery systems (Dalton, 2004; Spencer et al., 2006). In consequence, the diffusion of the NERICA varieties was mostly through participatory varietal selection (PVS) systems and community-based seed system (CBSS) training sessions conducted by WARDA and NARS, both systems of which are time consuming. While paying attention to the role of extension, this paper highlights the dynamic behavior of the NERICA adoption by undertaking a case study of Uganda which is considered as a model country of rapid NERICA adoption due to successful public–private partnerships among the national program, NGOs, seed companies, and farmers (Africa Rice Center (WARDA), 2006). We found from the panel data of 374 rural households in Uganda collected in both 2004 and 2006 that more than 50% of the NERICA adopters in 2004 had abandoned it in 2006. Unless the problem of this high dropout rate is resolved, a NERICA-led Green Revolution will not be realized. The purpose of this paper is to examine why the dropout rate of the seemingly profitable rice variety was so high. We identify that the major constraining factors are problematic program design and targeting at variable rainfall areas where the profitability of NERICA is low, and underdeveloped markets for seeds and rice milling services. Although we take the specific case of NERICA varieties in Uganda, the results will be useful for other countries which attempt to introduce NERICA varieties. We find that while the seed distribution program contributed to the early adoption of NERICA, it targeted not only suitable but also unsuitable areas for NERICA production where the profitability of NERICA relative to other crops is low, thereby resulting in massive dropouts in the unsuitable areas. We also find that while favorable access to input and output markets is an important determinant of NERICA adoption, the use of farmer-produced seeds reduces the profitability of NERICA most likely due to the deterioration of the quality of the seeds. The rest of this paper is structured as follows. Section 2 provides an overview of the NERICA program in Uganda. Section 3 presents the conceptual framework. Section 4 describes the survey data used in this study and their major characteristics. Section 5 explains the empirical models and results for the adoption decision. Section 6, analyzes the NERICA profit function, and Section 7 discusses the conclusions and policy implications. 2. NERICA PROGRAM IN UGANDA Rice is now widely grown in many parts of the country, especially in the eastern and northern regions. Domestic rice production has not been able to keep up with the demand, which is growing fast because of rapid urbanization and changing food habits. As a result, Uganda resorts to importing about $90 million of rice (the third largest import item in the country) every year to meet the demand (Africa Rice Center (WARDA), 2006). The government is, therefore, keen to increase local rice production in order to reduce its import. In 2002, a NERICA variety was released in Uganda by two independent sources, the National Agricultural Research Organization (NARO) and the NASECO seed company, under two different names—NARIC 3 (NARO) and SUPARICA 2 (NASECO) (Africa Rice Center (WARDA), 2006). At that time, the diffusion of NERICA was limited around these sources. Since the Ugandan Vice President was convinced that the poor could escape the poverty trap by growing NERICA varieties, he initiated a NERICA-based rice initiative as part of Uganda’s poverty eradication campaign in January 2004. Subsequently, the President officially launched the initiative in March 2004, in the Vice President’s farm in Wakiso district. NERICA seeds were distributed to representatives of farmers’ groups from 11 districts. According to the Vice President’s office, the targeted areas were selected based on agro-ecological suitability for upland rice cultivation in poorer areas. After selecting the areas, local NGO staff provided seeds to farmers who were interested in growing NERICA varieties often in the form of in-kind credit to offer the opportunity to try the new technology even to poor farmers. Since the purpose of the government’s NERICA program is to expand the adoption to wider areas, the seeds are not distributed to the same farmers more than once and the program areas are shifted to uncovered areas. A seed shortage proved to be a bottleneck to the wide dissemination of NERICA and an attempt was made to alleviate this by partnering with NGOs and private seed companies. The two NGOs—Sasakawa-Global 2000 and the USAIDfunded Investment in Developing Export Agriculture (IDEA) project of the Agribusiness Development Centre (ADC)—purchased breeder seed from the NASECO seed company for formal seed multiplication during the initial promotion of NERICA varieties in the country. These activities have played a pivotal role in the NERICA dissemination in Uganda (Africa Rice Center, 2006). 3. CONCEPTUAL FRAMEWORK Our conceptual framework is based on the unique characteristics of the crop under study, i.e., upland rice in the context of Central and Western Uganda in which the high dropout took place within a short period of time. We focus on the possible effects of three factors, namely program targeting, market development, and relative profitability. (a) Program design and targeting It must be emphasized at the outset that the method of diffusing NERICA varieties was changed after the government program started. Especially in the first year, newspapers and radio and TV programs presented the dissemination of NERICA varieties as a way of getting out of poverty (New Vision, 2004). Since there were only a small number of the extension workers who knew about rice cultivation, there is no doubt that the commitment of the government to NERICA dissemination contributed to the enhancement of the farmers’ exposure to NERICA varieties. It is likely, however, that only positive information about NERICA varieties as an income generating crop was highlighted and thus NERICA’s impact could have been overvalued by the public. The production of upland NERICA is greatly affected by the vagaries of rainfall, even though it is drought-tolerant. It also requires intensive labor use for planting, weeding, harvesting, and bird scaring, compared with other subsistence crops such as maize (Kijima, Otsuka, & Sserunkuuma, 2008). It is possible that some of the early adopters might not have been aware of these characteristics before they adopted NERICA. This lack of accurate knowledge about this new crop may have resulted in disappointment among the early adopters of NERICA in subsequent years. According to the Vice President’s office, the targeting criterion was the suitability of rice cultivation in poor areas. However, there was neither a clear definition of “suitability” nor a specific threshold to divide suitable and unsuitable areas. AN INQUIRY INTO CONSTRAINTS ON A GREEN REVOLUTION IN SUB-SAHARAN AFRICA Because of this ambiguity, it is possible that some of the areas under the government’s seed distribution program were not suitable for rice production but were politically favored. Given that NERICA in Uganda is grown without irrigation, the initial dissemination of NERICA in unsuitable areas for rice cultivation characterized by low and variable rainfall might have resulted in the high dropout rates. (b) Market access Upland rice is a recently introduced crop to most of the sample farmers. When a new crop is introduced, the related markets are often missing. This was the case in the sample areas. Our informal interviews with rice farmers in 2004 revealed serious problems in marketing the harvested paddy rice due to the absence of rice millers in nearby towns. Since in Uganda, rice is considered a commercial crop rather than a subsistence food crop in contrast to West Africa, accessibility to markets is expected to affect the adoption decision (Ashraf, Gine, & Karlan, 2009; Carletto, de Janvry, & Sadoulet, 1999). Limited NERICA seed availability was also a serious constraint in 2004 when a small amount of rice seed was produced by seed companies and distributed mainly by the seed programs. In the survey period, there were four possible ways through which farmers could obtain NERICA seed: (1) participation in the seed distribution program, (2) direct purchase of seed from seeds companies, (3) by use of own seeds saved from the previous harvests, or (4) purchase of seed from other farmers. Note that the seed distribution programs procured certified seed from seed companies and distributed the seed to farmers via NGOs and extension workers. However, the direct purchase of seed from seed companies by individual farmers was observed mainly in areas close to such companies, where the farmers engage in contract farming for the seed companies which require the farmers to use the treated seeds from the company to maintain the quality of the seeds produced by these farmers. Because NERICA rice seeds can be produced by farmers, it is also reasonable to expect that the effect of seed distribution programs is moderated over time as farmers produce their own seeds. It is found in existing studies that lack of access to credit tends to limit the adoption of new technology since such adoption of new technology needs to be accompanied by the increased use of complementary inputs such as labor, fertilizer, herbicide, and pesticide (Feder, Just, & Zilberman, 1985; Sunding & Zilberman, 2001). Since the seed program did not provide credit, the high dropout rate of NERICA may be explained by such constraints. In the sample areas, on one hand, NERICA rice varieties were grown without fertilizer and the credit to purchase chemical fertilizer would thus not be a serious constraint to growing NERICA varieties. In terms of labor, on the other hand, rice requires more labor use than other subsistence crops such as maize and banana, which make the households who are not endowed with abundant family labor or are unable to hire labor not to adopt NERICA varieties. (c) Relative profitability The farmers will choose to keep using the new technology as long as the expected profit of the new agricultural technology exceeds that of the traditional technology (Cameron, 1999). Given that traditional upland rice varieties were not grown in the sample areas, we cannot compare the profitability of NERICA varieties with that of traditional upland rice varieties. According to our field interviews, those who decided to 79 discontinue the adoption of NERICA varieties were disappointed with the low returns to NERICA production in the past. For this reason, the profitability of NERICA compared with that of alternative crops may have played an important role. Note that since the production of NERICA requires more water than alternative upland crops, such relative profitability may be significantly affected by the rainfall pattern. For those who adopt a new technology for the first time, favorable access to information and intense social interactions among community members are expected to increase the adoption (Bandiera & Rasul, 2006; Conley & Udry, 2005). It is found that the households who have other job opportunities such as employment in urban areas and the production of other cash crops tend to discontinue the adoption of laborintensive cropping systems in developing countries since their opportunity costs of adopting such systems are high (Barrett, Moser, McHugh, & Barison, 2004; Moser & Barrett, 2003; Moser & Barrett, 2006; Neill & Lee, 2001). Given that the production of NERICA requires more labor inputs than the alternative crop, households who reside closer to towns and are more educated may stop growing NERICA since their higher labor costs decrease the relative profitability of NERICA to the activities. 4. DATA The data used in this paper were collected in 2004 and 2006. Since the dissemination of NERICA started in 2002 as explained in Section 2, farm households growing NERICA rice were found mainly in areas targeted by the government’s NERICA seed dissemination programs and in areas near seed companies. Thus, we intentionally selected 10 NERICA-growing areas covering the Central and Western regions (Kijima et al., 2006; Kijima et al., 2008). 2 In each sample area, we drew a random sample of 25 households that grew NERICA rice in the second cropping season of 2004, and 15 households that did not (the total sample size is 40 10 = 400). In order to control for the differences in the population of NERICA growers in each area, sampling weights are used for all analyses. In the second survey (2006), we had to decrease the number of sample districts up to nine due to the budget constraints (40 households were dropped). In addition, we could not collect data of 13 households in the remaining nine districts due to out-migration from the sample areas, the dissolution of households, and the absence of household members during the data collection period. In total, we used a panel sample of 347 households for this analysis. 3 Based on differences in the NERICA adoption behavior, we stratified the sample into four groups. The first group, nonadopters, has never adopted NERICA; the second group, dropouts, includes households that grew NERICA in 2004 but not in 2006; the third group, continuous adopters, consists of households that grew NERICA in both 2004 and 2006; and the last group, late adopters, refers to households that adopted NERICA in 2006 but not in 2004. We also refer to the dropouts and the continuous adopters as the early adopters. Table 1 presents the data on the household and community characteristics of the four adoption categories. The table shows that there are significant differences in household characteristics such as educational attainment and asset holdings between the early adopters and the other groups. 4 It is important to recognize that the dropouts and continuous adopters are almost equally educated and also equally endowed with family labor and land, indicating that the reason for abandoning NERICA rice during 2004–06 80 WORLD DEVELOPMENT Table 1. Household and community characteristics by type of adoptersa Early adopters Dropouts Number of Households 129 Household characteristics in 2004 Rice cultivation experience (years) Household head’s age Household head’s years of schooling Number of adult males aged 15–59 Number of adult females aged 15–59 % of female-headed households Land area per capita (ha)b Land area per household (ha)b Land cultivated in 2nd season (ha) Household asset (USD)c Value of livestock (USD) Yield in 2004 (ton per ha) Yield in 2006 (ton per ha) Profit from rice production in 2004 (USD/ha) Profit from alternative crop in 2004 (USD/ha)g 1.49 48.2 7.0 1.80 1.96 10.2 0.38 4.52 1.19 149 371 2.01 na 40.54 86.83 Community characteristics Availability of seed program in 2004 (%) Availability of seed program in 2006 (%) Distance to rice miller in 2004 (km) Distance to rice miller in 2006 (km) Traveling time to town (hours) Relative price of maize to rice in 2004 Relative price of maize to rice in 2006 Three years av. rainfall 2001–03, 2004–6, 90 days (mm) Three years C.V. rainfall 2001–03, 2004–6, 90 days 37.4 20.4 15.4 11.1 0.62 0.512 0.606 440 0.151 Other groups Continuous adopters d * * * * * * * * * * * * * * * Late adopters Non-adopters 99 e 25 94 f 1.88 43.9 7.7 1.81 1.68 8.0 0.47 4.23 1.30 172 390 2.97 2.54 202.21 72.54 * 0.50 49.4 4.5 0.99 1.34 29.7 0.38 2.53 0.78 54 80 na 1.49 na na 0.07 48.7 4.9 1.43 1.50 32.8 0.24 2.56 0.92 160 307 na na na na * 17.3 23.9 28.9 5.5 0.66 0.448 0.467 465 0.145 18.6 10.7 19.0 14.1 0.42 0.385 0.452 417 0.192 33.7 28.6 26.9 6.2 0.77 0.465 0.563 470 0.115 * * * * * * * * * * * * * * * * * * * * * * * * * * a The data pertain to 2004 unless stated otherwise. Land area refers to owned land and tenanted land under the mailo regime. c Household assets include furniture, bicycles, and electrical appliances. d * Indicates significant difference in means between dropouts and continuous adopters by the t-tests on the equality of means at the 5% level. e * Indicates significant differences in means of late adopters and continuous adopters by the t-tests on the equality of means at the 5% level. f * Indicates significant difference in means between early adopters (continuous or dropouts) and the others by the t-tests on the equality of means at the 5% level. g Profit from alternative crop is only available in 2004. Alternative crops to rice are mainly maize and beans (Kijima et al., 2008). b cannot be attributed to the lack of human capital, family labor, and land. The average yield of the continuous adopters in 2004 is 3.0 tons per hectare, which attests to the high yield potential of NERICA. It is significantly higher than that of the dropouts in 2004. This result is expected because the poor performance of NERICA production likely discourages NERICA adoption in subsequent periods. 5 Moreover, the dropouts obtained significantly lower profit from rice production in 2004 than that of the continuous adopters. In contrast, the profit from alternative crops is much higher among the dropouts than the continuous adopters. 6 The community characteristics seem to be different between the continuous adopters and the dropouts. Though the distance to the nearest rice miller was shorter for the dropouts than for the continuous adopters in 2004, it has shortened considerably in the past 2 years, particularly for the continuous adopters. Table 1 clearly indicates that the early adopters had better access to the seed distribution programs in 2004. However, the availability of such programs decreased in 2006 for all NERICA adoption categories, except in areas where the late adoption took place. The average rainfall and the coefficient of variation in the previous 3 years, i.e., 2001–03 for 2004 and 2003–05 for 2006, which are intended to capture the longer-term rainfall patterns during the main cropping season, show that the non-adopters reside in areas with low and variable rainfall. The comparison between the dropouts and the continuous adopters indicates that areas where the dropouts reside are less favorable in terms of the reliability of rainfall than in the areas where the continuous adopters reside. 5. DETERMINANTS OF DROPOUT AND ADOPTION In order to rigorously identify the critical factors affecting the adoption of NERICA rice varieties, we conduct regression analyses in this section. The adoption decision is modeled as the decision between planting a plot of land to NERICA and to other alternative crops such as maize and beans. It is assumed that if the expected profitability of rice is greater than that of the other alternative crop, rice is adopted. The expectation is updated by using past experience, while considering the effects of household and plot specific characteristics. The adopters decide whether they remain adopters or become non-adopters of NERICA varieties based on their actual relative profitability in the previous year, while the non-adopters decide whether to start growing NERICA varieties or to remain non-adopters without information about relative profitability. Since we have only two-period data, the past information utilized in the regression analyses pertain to the information AN INQUIRY INTO CONSTRAINTS ON A GREEN REVOLUTION IN SUB-SAHARAN AFRICA only 2 years ago, which is denoted by t 1. Households who did not cultivate rice at t 1 do not update their expectations on the relative profitability of NERICA cultivation. Thus, we specify the empirical model for the early adopters and nonearly adopters as: y ijt ¼ 1½ai þ bðpNijt1 pAijt1 Þ þ dX ijt þ cZ jt þ eijt > 0 if y ijt1 ¼ 1 ð1Þ y ijt ¼ 1½ai þ dX ijt þ cZ jt þ eijt > 0 if y ijt1 ¼ 0 ð2Þ where 1[] is an indicator function if household i in village j grew NERICA rice at time t and is zero otherwise, pijt1 is the profit per hectare from NERICA (N) or the alternative crop (A) plot at t 1, and X and Z are household and community level characteristics at the time of the adoption decision, respectively. We model the adoption decision differently for those who have adopted NERICA at t 1 shown in Eqn. (1) and for those who did not adopt it at t 1 shown in Eqn. (2). Since we use only early adopters to estimate Eqn. (1) for the adoption decision in 2006, selection bias is likely to arise. Thus, we estimate Eqns. (1) and (2) by the Probit model with selection. 7 The possible determinants of NERICA adoption include (1) a set of variables indicating the suitability of rice production and the transaction costs of acquiring seeds and selling paddy rice, such as the average rainfall, rainfall variation, availability of seed programs, and distance to rice millers; and (2) household characteristics such as the household head’s education, the number of adult male and female household members aged between 15 and 59 years old, and asset holdings. As a measure of the relative profitability, we use the profit differential of rice and the alternative crop in the previous period. Column (1) in Table 2 shows the first stage regression results of the determinants of NERICA adoption in 2004. Column (2) is the second stage regression results of NERICA adoption for the early adopters. Column (3) shows the second stage result for the non-early adopters indicated. In the second stage Table 2. NERICA adoption in 2004 and 2006 (Probit model with selection) Adoption in 2004a Stay adopting in 2006 (early adopters)b Adoption in 2006 (non-early adopters)c Average rainfall (mm) C.V. rainfall Distance to rice miller (km) Seed program dummy Traveling time to town (hours) Profit from rice plot – Profit from alternative crop plot in 2004 (100 USD)d Number of adult males aged 15–59 Number of adult females aged 15–59 % of female-headed households Household head’s age Household head’s years of schooling Land area per capita (ha) Household asset (1000 USD) Value of livestock (1000 USD) Number of groups household belonged to Head’s education number of groups household belonged to Rice experience (years) Wald chi-squared (p-Value) [1st stage] (1) [2nd stage] (2) [2nd stage] (3) 0.001 (4.33)** 0.436 (2.01)* 0.002 (3.35)** 0.092 (4.66)** 0.092 (4.40)** 0.001 (3.27)** 2.353 (4.41)** 0.004 (1.61) 0.056 (0.58) 0.442 (4.15)** 0.066 (1.93)* 0.048 (1.85)+ 0.025 (0.90) 0.308 (3.09)** 0.002 (0.84) 0.003 (1.50) 0.018 (0.44) 0.254 (1.95)* 0.141 (2.53)** 0.029 (0.63) 0.001 (9.10)** 0.899 (9.14)** 0.097 (4.68)** 0.021 (1.58) 0.002 (3.87)** 0.033 (4.59)** 0.027 (4.75)** 0.047 (2.68)** 0.004 (7.92)** 0.000 (0.45) 0.068 (5.70)** 0.055 (1.96)* 0.095 (5.35)** 0.069 (6.53)** 46.71 (0.000) 289.8 (0.000) 0.051 (6.86)** 0.032 (4.17)** 0.018 (0.97) 0.001 (1.93)* 0.009 (2.54)* 0.004 (0.25) 0.004 (0.51) 0.016 (1.31) 0.089 (3.29) 0.011 (2.88)** 0.036 (9.05)** 81 **, *, and + indicate significance at 1%, 5%, and 10%, respectively. The figures are marginal effects. a Estimated by the Probit model with selection, assuming that the error terms of the first and second stage regression models are bivariate normal. b The decision of dropout or continuous adoption in 2006 is only observed among those who adopted NERICA in 2004. c Similarly, the decision of new adoption or non-adoption at all in 2006 is only observed among those who did not adopt NERICA in 2004. d Endogenous variable: instrumental variable – rice cultivation experience before 2004 (year). 82 WORLD DEVELOPMENT regressions, self-selection bias is controlled for as explained in the previous section. The figures shown in this table are the marginal effects. As may be expected, higher average rainfall and lower rainfall variations in the previous 3 years, which are favorable for NERICA production, significantly raised the probability of remaining NERICA adopters and newly adopting NERICA varieties in 2006 (see columns 2 and 3). An increase in average rainfall in the previous 3 years by 10 mm enhances the adoption rate by 1% point in 2006. It is important to note that higher rainfall decreases and higher rainfall variation increases the probability of adoption in 2004 (see column 1). This suggests that the new adoption in 2006 took place in areas that are more suitable for NERICA production, while in 2004, NERICA tended to be adopted in less suitable areas for NERICA production characterized by high rainfall variation and lower average rainfall. In other words, some of the areas that received NERICA dissemination programs were likely to have been mis-targeted. This interpretation is supported by the positive coefficient of the relative profitability of NERICA to the alternative crop in column (2): it significantly increased the probability of continuing NERICA adoption in 2006. This means that the observed high dropout rate in 2006 is partly due to the low profitability of NERICA compared to that of the alternative crop. According to the estimated coefficients, an increase in the profit differential by USD 10 decreases the dropout rate of NERICA by 0.7% points. The effects of the distance to rice millers on the adoption decision are significant in columns 1 and 3. This indicates that NERICA is less likely to be adopted in areas where the cost of marketing paddy rice is higher. The availability of seed programs increased the probability of adoption in 2004 but not in 2006. This may suggest that the role of such programs as the seed source became less important in 2006 due to the development of seed markets or the use of self-produced seeds. There are positive relationships between NERICA adoption and the household head’s education for early adoption in 2004. It appears that the ability to decode new information and rice production knowledge may matter in NERICA adoption. Among the early adopters, however, the higher education does not increase the probability of continuing NERICA production in 2006. Rather, there is a weak evidence that the educated farmers quickly abandoned NERICA production in 2006 (insignificant but negative coefficient of household head’s education in column 2) since their opportunity costs of adopting labor-intensive cropping systems are higher than those for the less educated farmers. Asset ownership variables have mixed effects on adoption decisions. Household asset and livestock ownership do not have an impact on NERICA adoption in 2004 while they have positive effects on continuous adoption in 2006 and negative effects on new adoption in 2006. As shown in column (3), larger land per capita increases the probability of adopting NERICA in 2006. Since rice is considered as a cash crop and farmers tend to grow their own food crops as well, small farm size can be a limitation for NERICA adoption. As shown in column (1), the endowment of family labor, measured by the number of adult household members, positively affected NERICA adoption in 2004. However, the positive effects of family labor endowment are not observed in 2006. In conclusion, we would like to point out that the low relative profitability of NERICA compared with that of the alternative crops and unfavorable access to markets are critical factors explaining the high dropout rate during 2004–06. Our analysis also suggests that the inappropriate targeting of NERICA seed distribution programs toward areas with low and variable rainfall is partly responsible for the massive dropouts. Table 3. NERICA plot characteristics by type of adopters 2004 Dropouts Number of plots Size of NERICA plot (ha) 129 0.423 Plot location and cultivation practice % of plots with straight-row planting % of late planting % of plots with zero yield % of plots with steep slope % of plots with rice in the previous two seasons % of plots which are rented in Walking time from homestead to plot (minutes) 94.4 8.5 4.4 12.9 0.8 16.1 6.3 Seed source % of self-produced seeds % of purchased seed from neighbors % of program seeds (NGO, VP) % of other seeds (purchased from traders, contract farming) Input use (per hectare) Chemical fertilizer (kg) Seeds (kg) % of pesticide/herbicide used Male labor (hours) Female labor (hours) Child labor (hours) a 5.2 3.8 53.8 37.2 7.97 87.97 3.64 666.3 788.0 547.4 a 2006 Continuous adopters b 107 0.377 * * * * * * 93.1 2.8 0.4 8.6 0.7 12.6 6.0 7.7 11.7 42.9 37.7 2.43 147.32 6.22 930.3 1020.8 607.6 Continuous adopters c 100 0.471 * * * * 93.2 11.1 6.9 1.7 2.6 6.9 10.5 41.5 12.0 15.0 31.5 5.40 97.0 10.6 1038.7 1166.5 412.4 Late adopters 23 0.241 * * * 86.6 6.1 24.9 0 0 2.0 10.2 5.8 46.5 10.2 37.5 0 95.0 2.0 1257.5 1589.2 434.7 * Indicates significant difference in means between dropouts and continuous adopters in 2004 by the t-tests on the equality of means at the 5% level. * Indicates significant difference in means of continuous adopters during 2004–06 by the t-tests on the equality of means at the 5% level. c * Indicates significant difference in means between late adopters and continuous adopters in 2006 by the t-tests on the equality of means at the 5% level. b AN INQUIRY INTO CONSTRAINTS ON A GREEN REVOLUTION IN SUB-SAHARAN AFRICA 6. DETERMINANTS OF PROFIT In the previous section, we found that relative profitability is one of the key determinants of the dropout from NERICA production in 2006. To achieve sustainable adoption, we need 83 to understand what determines the profitability of NERICA. Thus, in this section, we estimate the profit functions. Table 3 shows the plot-level characteristics such as plot location and cultivation practices related with soil fertility, seed source, and input use by the different adoption categories. Table 4. Determinants of NERICA profita 2004 2006 (1) (2) (3) (4) 4.470 (1.64) 13.837 (1.33) 0.056 (0.00) 22.812 (0.66) 99.669 (0.63) 55.281 (0.73) 43.834 (0.45) 0.794 (0.01) 56.486 (0.71) 1.544 (0.68) 19.866 (0.15) 0.030 (0.07) 165.562 (1.29) 8.905 (3.36)** 0.625 (0.49) 78.972 (1.96)* 5.141 (0.13) 147.845 (1.25) 106.302 (1.23) 341.542 (2.20)* 73.287 (0.81) 11.280 (0.15) 9.109 (1.10) 132.797 (1.29) 0.585 (1.64) 41.182 (0.47) 99.743 (0.48) 7.866 (2.73)** 1.106 (0.88) 61.118 (1.66)+ 10.959 (0.28) 302.307 (2.30)* 66.099 (0.81) 197.439 (1.33) 89.083 (0.99) 134.288 (1.60) 4.085 (0.57) 174.094 (1.25) 0.551 (1.42) 18.225 (0.20) 250.942 (1.77)* 102.772 (1.19) 57.730 (0.18) 335.885 (2.44)* 148.517 (2.02)* 0.194 (0.07) 0.412 (0.43) 1.269 (1.79)* 298.552 (2.54)* 0.164 (5.08)** 0.028 (1.51) 0.165 (3.10)** 160.244 (0.55) 0.38 0.63 Constant 111.221 (0.29) 3.410 (1.23) 3.340 (0.32) 1.417 (0.05) 43.001 (1.16) 112.052 (0.79) 17.987 (0.24) 38.610 (0.39) 82.270 (0.97) 6.004 (0.07) 0.559 (0.22) 109.919 (0.76) 0.139 (0.32) 0.000 (0.11) 102.271 (0.77) 249.546 (1.90)+ 10.712 (0.11) 96.043 (0.86) 126.270 (1.34) 0.146 (0.07) 1.307 (1.58) 0.448 (2.06)* 75.723 (0.51) 0.124 (2.59)* 0.108 (2.17)* 0.014 (0.39) 379.106 (0.94) R-squared 0.07 0.27 Household head’s age Household head’s years of schooling Number of adult males aged 15–59 Number of adult females aged 15–59 % of female-headed households Land area per capita (ha) Household asset (1000 USD) Value of livestock (1000 USD) Seed program dummy Distance to rice miller (km) Traveling time to town (hours) Rainfall for 90 days in the second cropping season (mm) Maize–rice price ratio Straight-row planting dummy Late planting dummy Steep slope plot dummy Rent-in plot dummy Farmer-produced seed dummy Walking time from homestead to plot (min) Chemical fertilizer application per ha (kg) Seed used per ha (kg) Pesticide/herbicide use dummy Male labor hours spent per ha Female labor hours spent per ha Child labor hours spent per ha **, *, and + indicate significance at 1%, 5%, and 10%, respectively. a The numbers in parentheses are t-statistics. The second stage regression results are shown. In the first stage regression, the interaction term of household head’s education with the number of farmers’ groups is used for identification to be adopters in each specification. The result for the specification (1) is shown in Table 2 column (1). 84 WORLD DEVELOPMENT The continuous adopters are less likely to plant late than the dropouts. 8 Partly due to this difference, the proportion of plots with zero yields is higher among the dropouts than the continuous adopters in 2004, which is directly responsible for lowering the average yield. In 2006, compared with the continuous adopters, the late adopters are less likely to practice straight-row planting, which makes weeding more difficult, thereby resulting in lower yield. The seed source has changed drastically during 2004–06. In 2004, the proportion of sample plots planted to seed obtained either from the seed companies or from the seed distribution programs was 80–90%, and the use of farmer-produced seeds, i.e., self-produced seeds and seeds purchased from neighbors, was rare. There is not much difference in seed source between the continuous adopters and the dropouts in this year. However, in 2006, the continuous adopters used mainly their own self-produced seeds, while the late adopters used mainly purchased seeds from neighbors. Although NERICA seeds can be produced by farmers themselves as with other rice varieties, farmers have to remove undesirable plants to obtain highquality rice seed. Once farmers learn how to produce highquality seed, the farmer-produced seeds can be as good as that sold by seed companies. 9 Given that most of the sample farmers had only recently started rice production, there is a possibility that the quality of the farmer-produced seed was not as good as that of the purchased seeds, unless the extension services provided appropriate information on seed production. Thus, we also test whether using self-produced seed lowers the profit or not. To rigorously analyze what increases the NERICA profit, we estimate the profit function by using the plot-level data. Since the profit information is only available among adopters, we apply Heckman’s two-step model separately for 2004 and 2006 so as to control for self-selection bias. We estimate two specifications with and without the variables of cultivation practice and plot location which are likely to be endogenous. The explanatory variables used for this analysis are plot-level variables such as land tenancy, the walking time from the homestead to the plot, the slope, the location, and the cropping pattern shown in Table 3 as well as the household and community level data indicated in Table 1. Note that we use the rainfall for 3 months after NERICA was planted in the NERICA profit functions, while we used the average rainfall over the 3-year period in the estimation of the adoption function as a proxy for the expected rainfall pattern. Table 4 reports the estimated results of the NERICA profit function. In 2004, the NERICA profits were not significantly affected by household and community characteristics. The profits tended to be lower when planting was late, when fewer seeds were used, and when more male and female labor inputs were used. The signs of the labor inputs are contrary to the expectation, but this is probably because the unfamiliarity of the farmers with certain activities such as planting and harvesting in rice cultivation resulted in longer working hours without much labor productivity gains. In 2006, household characteristics such as the household head’s age and the number of male adult members affected the NERICA profit. In terms of plot characteristics, recycled seed, straight row planting, rent-in plots, the amount of seeds, pesticide/herbicide use, and male and child labor had significant impacts on the profits The coefficient of the farmer-produced seed dummy is negative and significant, suggesting the possibility of the deterioration of seed quality over time. If so, there is an urgent need for training on the production of high quality seeds. Whether the plot is rented or owned affected the profit only in 2006. In terms of the location of the plot, the slope and distance from the homestead do not have significant impacts on the profit. 10 7. CONCLUSION AND POLICY IMPLICATIONS Using panel data of 347 households collected in 2004 and 2006 in rural Uganda, we identified four types of NERICA adoption behaviors: continuous adoption in the 2 years, dropouts, late adoption, and non-adoption. The NERICA yield was found to be much higher among the continuous adopters than among the dropouts. Furthermore, for the dropouts, the profit from the NERICA plot is much lower than that for the alternative crop. The regression analysis confirmed that this relatively low profitability of NERICA partly explains the high dropout rate of NERICA. The relative profitability seems to be determined largely by the rainfall pattern. Indeed, NERICA adoption is positively affected by sufficient rainfall and lower rainfall variation in 2006. However, farmers in areas unsuitable for its cultivation, such as those in areas with high rainfall variation, have been targeted to receive NERICA seed program in 2004. These findings strongly suggest the mis-targeting of the NERICA dissemination programs. We also found that the availability of seed distribution programs was a critical determinant of NERICA adoption in 2004 but not in 2006, most likely because the use of farmer-produced seed was widespread in 2006. Shortened distance to rice millers, whose number has increased rapidly in the past 2 years in response to the increasing demand for milling services, significantly increased the NERICA adoption. These findings suggest that improved access to rice millers and the increased exchange of farmer-produced seeds among farmers stimulated the new adoption of NERICA rice, which, in turn, point to the possibility of a rice Green Revolution. The first policy implication of this study is that in order to achieve the wider dissemination of NERICA and to realize a rice Green Revolution, the extension system must be strengthened with regard to teaching farmers how to grow rice. The appropriate timing of planting is critical to avoid crop failure. The failure to disseminate appropriate methods for producing high-quality farmer-produced seed is another important factor which will likely reduce not only the yield of NERICA but also the adoption of NERICA. 11 Also important is the appropriate targeting of NERICA dissemination areas. Capacity building for extension workers and the allocation of resources to extension activities are the keys to the realization of a “NERICA Revolution” in this country. The second implication is that rice development policies should be designed to support the development of markets for rice seed and milling services, as they promote sustainable NERICA adoption. Although we do not have concrete evidence, in all likelihood, the development of the rice milling market was a response to the increased demand for milling services. The fact that the distance to rice millers declined more significantly in areas where the continuous adopters are located than in those where the dropouts and the non-adopters are located is consistent with our conjecture. The burgeoning trade of seed from experienced rice farmers to new farmers is indicative of the emergence of an informal seed market. Thus, there seems to be a virtuous circle of increased seed production, the increased production of rice, and the improvement of rice milling markets. To the extent that these markets still “fail” due to credit constraints and imperfect information about the methods of seed production, the quality of seeds, and the rice milling business, AN INQUIRY INTO CONSTRAINTS ON A GREEN REVOLUTION IN SUB-SAHARAN AFRICA there is room for the government to support the further development of these markets in order to improve the 85 efficiency of rice production and reduce poverty among smallholders in Uganda. NOTES 1. In the case of our study country, Uganda, it can be said that the higher price of rice is another potential benefit of rice production. Although it is difficult to obtain solid statistical evidence, it is widely believed that the prices of imported goods, including rice, are generally high in Uganda due importantly to poor infrastructure. 2. Two to three local councils (the lowest administrative unit in Uganda called LCI) constitute each NERICA growing area, and our sample covers 29 LC1s. 3. In addition, we use the rainfall data provided by the department of meteorology, Government of Uganda. 4. The early adopters tend to be more educated according to the literature on the adoption of new agricultural technologies (Sunding & Zilberman, 2001; Feder et al., 1985). 5. A recent study conducted in Uganda (Sserunkuuma, 2008) shows that the occurrence of severe drought conditions during the cropping season significantly reduced the rice yield. 6. We have tried the multinomial approach to analyze the transitions between states of adoption and non-use of NERICA, but the qualitative results are similar to the current results. 7. Since the dependent variable at the second stage regression is an indicator variable, we apply the probit model with sample selection (heckprob for STATA command) where the error terms in the first and second stage regression models are assumed to be bivariate normal. The profit is computed by subtracting both the actual and the imputed costs of non-land inputs from the gross value of production. 8. We constructed a dummy variable for whether farmers planted rice too late according to their planting date. We consider a case as late planting when farmers plant upland rice later than August 15 for the second cropping season in 2004 and 2006 based on the upland cultivation manual provided by APEP (The Uganda Agricultural Productivity Enhancement Program, a 5-year USAID-funded activity). 9. This is why rice seed suppliers cannot make large profits in Asia, where farmers are adept at producing high-quality seeds. In Uganda, certified seeds are actually produced by farmers under contract with seed companies which provide detailed instructions on seed production. 10. Since we have soil data only for 2004, we included the soil carbon content, one of the soil fertility measures, as extra explanatory variables. 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