Abstract
This article examines the impact of farmers’ perceptions of temperature change on implementing environmentally friendly agriculture practices on rubber plantations. Based on the data collected from 611 smallholder rubber farmers in Xishuangbanna Dai Autonomous Prefecture (XSBN) in the upper Mekong region, an endogenous switching probit model and an endogenous treatment effects model are applied to estimate the impacts of farmers’ perceptions of temperature change on implementing environmentally friendly rubber plantations (EFRP) proxied by the intercropping system. While the real annual average temperature in XSBN has been increasing, only 59% of respondents perceived an increasing trend, whereas over 38% perceived no change. Farmers’ perceptions of temperature change appear to hinge on their education and socioeconomic characteristics and the experience of shocks related to regional climate change. Improving farmers’ perceptions of increasing temperature can significantly foster their practice of EFRP. Hence, policies that promote awareness of regional climate change can effectively encourage the implementation of mitigation practices.
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Notes
Based on the arrangement of each enumerator interviewing two households per day, the number of households per village ranged from 12 to 16.
Alternatively, this study also established a theoretical framework based on conceptualizing adoption as a continuous optimization problem. The details are presented in Appendix B.
The details of the setting of the ESP model and counterfactual analysis are presented in Appendix B.
The details of the setting of the ETE model are presented in Appendix B.
Thank for the suggestion of the referee.
References
Abdulai A, Owusu V, Bakang JEA (2011) Adoption of safer irrigation technologies and cropping patterns: evidence from southern Ghana. Ecol Econ 70(7):1415–1423. https://doi.org/10.1016/j.ecolecon.2011.03.004
Angelsen A (1995) Shifting cultivation and “deforestation”: a study from Indonesia. World Dev 23(10):1713–1729. https://doi.org/10.1016/0305-750X(95)00070-S
Antle JM, Capalbo SM (2010) Adaptation of agricultural and food systems to climate change: an economic and policy perspective. Appl Econ Perspect Pol 32(3):386–416. https://doi.org/10.1093/aepp/ppq015
Bai J, Xu Z, Qiu H, Liu H (2015) Optimising seed portfolios to cope ex ante with risks from bad weather: evidence from a recent maize farmer survey in China. Aust J Agric Resour Econ 59(2):242–257. https://doi.org/10.1111/1467-8489.12056
Carlson, K. M., Curran, L. M., Ratnasari, D., Pittman, A. M., Soares-Filho, B. S., Asner, G. P., … Rodrigues, H. O. (2012) Committed carbon emissions, deforestation, and community land conversion from oil palm plantation expansion in West Kalimantan, Indonesia. Proc Natl Acad Sci U S A, 109(19):7559–7564. https://doi.org/10.1073/pnas.1200452109
Dawson TP, Jackson ST, House JI, Prentice IC, Mace GM (2011) Beyond predictions: biodiversity conservation in a changing climate. Science 332(6025):53–58. https://doi.org/10.1126/science.1200303
Di Falco S, Veronesi M, Yesuf M (2011) Does adaptation to climate change provide food security? A micro-perspective from Ethiopia. Am J Agric Econ 93(3):829–846. https://doi.org/10.1093/ajae/aar006
Fearnside PM (1997) Greenhouse gases from deforestation in Brazilian Amazonia: net committed emissions. Clim Chang 35(3):321–360. https://doi.org/10.1023/A:1005336724350
Hamada S, Tanaka T, Ohta T (2013) Impacts of land use and topography on the cooling effect of green areas on surrounding urban areas. Urban Forest Urban Green 12(4):426–434. https://doi.org/10.1016/j.ufug.2013.06.008
Hansen J, Sato M, Ruedy R, Lo K, Lea DW, Medina-Elizade M (2006) Global temperature change. Proc Natl Acad Sci U S A 103(39):14288–14293. https://doi.org/10.1073/pnas.0606291103
Hansen J, Sato M, Ruedy R (2012) Perception of climate change. Proc Natl Acad Sci U S A 109(37):E2415–E2423. https://doi.org/10.1073/pnas.1205276109
He Y, Zhang Y (2005) Climate change from 1960 to 2000 in the Lancang River valley, China. Mt Res Dev 25(4):341–349. https://doi.org/10.1659/0276-4741(2005)025[0341:CCFTIT]2.0.CO;2
Heckman JJ, Vytlacil E (2001) Policy-relevant treatment effects. Am Econ Rev 91(2):107–111. https://doi.org/10.1257/aer.91.2.107
Herath PHMU, Hiroyuki T (2003) Factors determining intercropping by rubber smallholders in Sri Lanka: a logit analysis. Agric Econ 29(2):159–168. https://doi.org/10.1111/j.1574-0862.2003.tb00154.x
Hergoualc’h K, Blanchart E, Skiba U, Hénault C, Harmand J-M (2012) Changes in carbon stock and greenhouse gas balance in a coffee (Coffea arabica) monoculture versus an agroforestry system with Inga densiflora, in Costa Rica. Agric Ecosyst Environ 148:102–110. https://doi.org/10.1016/j.agee.2011.11.018
Hou L, Huang J, Wang J (2015) Farmers’ perceptions of climate change in China: the influence of social networks and farm assets. Clim Res 63(3):191–201. https://doi.org/10.3354/cr01295
Hou L, Huang J, Wang J (2017) Early warning information, farmers’ perceptions of, and adaptations to drought in China. Clim Chang 141(2):197–212. https://doi.org/10.1007/s10584-017-1900-9
Hu H, Liu W, Cao M (2008) Impact of land use and land cover changes on ecosystem services in Menglun, Xishuangbanna, Southwest China. Environ Monit Assess 146(1–3):147–156. https://doi.org/10.1007/s10661-007-0067-7
Huang J, Wang Y, Wang J (2015) Farmers’ adaptation to extreme weather events through farm management and its impacts on the mean and risk of rice yield in China. Am J Agric Econ 97(2):602–617. https://doi.org/10.1093/ajae/aav005
Iqbal S, Ireland C, Rodrigo V (2006) A logistic analysis of the factors determining the decision of smallholder farmers to intercrop: a case study involving rubber–tea intercropping in Sri Lanka. Agric Syst 87(3):296–312. https://doi.org/10.1016/j.agsy.2005.02.002
Laurance WF, Koh LP, Butler R, Sodhi NS, Bradshaw CJA, Neidel JD et al (2010) Improving the performance of the roundtable on sustainable palm oil for nature conservation. Conserv Biol 24(2):377–381. https://doi.org/10.1111/j.1523-1739.2010.01448.x
Lee TM, Markowitz EM, Howe PD, Ko C-Y, Leiserowitz AA (2015) Predictors of public climate change awareness and risk perception around the world. Nat Clim Chang 5:1014. https://doi.org/10.1038/nclimate2728
Li S, Juhász-Horváth L, Harrison PA, Pintér L, Rounsevell MDA (2017) Relating farmer’s perceptions of climate change risk to adaptation behaviour in Hungary. J Environ Manag 185:21–30. https://doi.org/10.1016/j.jenvman.2016.10.051
Lokshin M, Glinskaya E (2009) The effect of male migration on employment patterns of women in Nepal. World Bank Econ Rev 23(3):481–507. https://doi.org/10.1093/wber/lhp011
Lokshin M, Sajaia Z (2011) Impact of interventions on discrete outcomes: maximum likelihood estimation of the binary choice models with binary endogenous regressors. Stata J 11(3):368–385. https://doi.org/10.1177/1536867X1101100303
Maddala GS (1983) Limited-dependent and qualitative variables in econometrics. Cambridge University Press, Cambridge
Maddison D (2007) The perception of and adaptation to climate change in Africa. The World Bank, Washington, D.C
Min S, Huang J, Bai J, Waibel H (2017a) Adoption of intercropping among smallholder rubber farmers in Xishuangbanna, China. Int J Agric Sustain 15(3):223–237. https://doi.org/10.1080/14735903.2017.1315234
Min S, Huang J, Waibel H (2017b) Rubber specialization vs crop diversification: the roles of perceived risks. China Agric Econ Rev 9(2):188–210. https://doi.org/10.1108/CAER-07-2016-0097
Min S, Bai J, Huang J, Waibel H (2018) Willingness of smallholder rubber farmers to participate in ecosystem protection: effects of household wealth and environmental awareness. Forest Policy Econ 87:70–84. https://doi.org/10.1016/j.forpol.2017.11.009
Min S, Huang J, Waibel H, Yang X, Cadisch G (2019) Rubber boom, land use change and the implications for carbon balances in Xishuangbanna, Southwest China. Ecol Econ 156:57–67. https://doi.org/10.1016/j.ecolecon.2018.09.009
Moser SC, Ekstrom JA (2010) A framework to diagnose barriers to climate change adaptation. Proc Natl Acad Sci 107:22026–22031. https://doi.org/10.1073/pnas.1007887107
Nordhaus WD (1992) An optimal transition path for controlling greenhouse gases. Science 258(5086):1315–1319. https://doi.org/10.1126/science.258.5086.1315
Qiu J (2009) Where the rubber meets the garden. Nature 457(7227):246–247. https://doi.org/10.1038/457246a
Shi J, Visschers VHM, Siegrist M (2015) Public perception of climate change: the importance of knowledge and cultural worldviews. Risk Anal 35(12):2183–2201. https://doi.org/10.1111/risa.12406
Sunding D, Zilberman D (2001) The agricultural innovation process: research and technology adoption in a changing agricultural sector. Handb Agric Econ 1:207–261. https://doi.org/10.1016/S1574-0072(01)10007-1
Swe LMM, Shrestha RP, Ebbers T, Jourdain D (2015) Farmers’ perception of and adaptation to climate-change impacts in the dry zone of Myanmar. Clim Dev 7(5):437–453. https://doi.org/10.1080/17565529.2014.989188
Tang J, Folmer H, Xue J (2016) Adoption of farm-based irrigation water-saving techniques in the Guanzhong plain, China. Agric Econ 47:1–11. https://doi.org/10.1111/agec.12243
Verchot LV, Van Noordwijk M, Kandji S, Tomich T, Ong C, Albrecht A et al (2007) Climate change: linking adaptation and mitigation through agroforestry. Mitig Adapt Strateg Glob Chang 12(5):901–918. https://doi.org/10.1007/s11027-007-9105-6
Wicke B, Sikkema R, Dornburg V, Faaij A (2011) Exploring land use changes and the role of palm oil production in Indonesia and Malaysia. Land Use Policy 28(1):193–206. https://doi.org/10.1016/j.landusepol.2010.06.001
Woods BA, Nielsen HØ, Pedersen AB, Kristofersson D (2017) Farmers’ perceptions of climate change and their likely responses in Danish agriculture. Land Use Policy 65:109–120. https://doi.org/10.1016/j.landusepol.2017.04.007
Xishuangbanna Biological Industry Office, (2013) Guideline of environmentally friendly rubber plantation in Xishuangbanna Dai Autonomous Prefecture (In Chinese)
Yu H, Wang B, Zhang Y-J, Wang S, Wei Y-M (2013) Public perception of climate change in China: results from the questionnaire survey. Nat Hazards 69(1):459–472. https://doi.org/10.1007/s11069-013-0711-1
Zhou L (2008) Rubber forest crisis in Xishuangbanna: policy transmigration of a plant. Ecol Econ 6:16–23
Ziegler AD, Fox JM, Xu J (2009) The rubber juggernaut. Science 324(5930):1024–1025. https://doi.org/10.1126/science.1173833
Acknowledgments
This study was conducted in the framework of the Sino-German “SURUMER Project” funded by the Bundesministerium für Wissenschaft, Technologie und Forschung (BMBF), FKZ: 01LL0919. This work was also supported by National Natural Science Foundation of China (71761137002; 71673008; 71742002; 71603247).
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Appendices
Appendix A tables and figures
Appendix B Models
1.1 Theoretical framework
In this study, we focus on smallholder rubber farmers’ decisions to adopt the EFRP which is proxied by rubber intercropping. This decision is assumed to be made by the farmer after the decision of land allocation for rubber farming has been completed. The farmer’s utility from rubber farming is assumed to include two components: (1) the utility derived from the profit of rubber farming and intercropping, which is affected by the weather condition during the crop season, and (2) the utility derived from improved environmental conditions when adopting rubber intercropping under the weather condition during the crop season. Thus, the farmer should determine the proportion of the rubber plantation to allocate for intercropping to maximize the total utility from rubber farming.
Specifically, the expected profit of rubber farming and intercropping (π) is assumed to be determined as follows:
where the vector x = (x1, x2), where x1 and x2 represent the proportions of rubber plantations allocated for intercropping and monoculture rubber plantations, respectively. L is defined as the planting area of natural rubber available to the farmer. y (y = y(x| L)) is a vector of outputs corresponding to x given the planting area of rubber (L), while c(x) is the cost function corresponding to x. f(y) is the farmer’s subjective probability density function for y, which can be assumed to be solely related to the weather condition (wt) in the coming crop season (Bai et al. 2015). It is assumed that all smallholder rubber farmers in XSBN face the same market prices of rubber, intercrops, and inputs in the observation year; therefore, the price variables are omitted in the profit function (5).
Moreover, we further assume that the environmental utility of the farmer’s rubber farming depends on the planting area of natural rubber (L), the proportions of intercropping and monoculture rubber plantations (x), and the weather condition (wt). Thus, the environmental utility can be expressed as
By combining the profit function (5) and the environmental utility function (6), the farmer’s utility maximization problem can be written as
where U indicates the total utility from rubber farming, while U(π) denotes the utility from the profit of rubber farming and intercropping.
As farmers do not know the weather condition in the coming crop season (wt), they make the decision on x based on their predictions of the weather condition. Here, we assume that farmers’ predictions of weather condition in the coming crop season (\( \hat{w_t} \)) rely on the real weather condition in previous years and their perceptions of weather condition change in previous years. Thus, \( \hat{w_t} \) can be expressed as
where wt − 1 denotes the real weather condition in previous years, while P represents farmers’ perceptions of the weather condition change in previous years.
By incorporating the weather condition prediction function (8) into the utility maximization problem (7), the optimal choice of x can be conceptually derived as
where the real weather condition in previous years (wt − 1) is omitted as there is an implicit assumption that all rubber farmers faced the same weather condition in previous years. Given that temperature is a primary measurement of weather condition, the perception of a change in weather condition (P) can, to some extent, be proxied by the perception of temperature change (P′). Then, the optimal proportion of rubber plantations allocated for intercropping can be expressed as
According to Eq. A6, two hypotheses could be simply derived as follows. First, as x1∗ > 0 indicates that the farmer adopts intercropping, the hypothesis (1) is that the adoption of rubber intercropping is affected by the perception of temperature change (P′). Second, Eq. 10 shows the land allocated for rubber intercropping is a function of farmers’ perceptions of temperature changes; thus, we propose the hypothesis (2) that farmers’ perceptions of temperature change (P′) also influence the adoption intensity of rubber intercropping.
1.1.1 Endogenous switching probit model and counterfactual analysis
According to Lokshin and Glinskaya (2009), a farmer’s propensity to perceive increasing temperature can be expressed in a linear form as
where subscript i represents the farmer. Zi denotes a vector of independent variables reflecting the socioeconomic characteristics of the respondent, household, land, and located village, while γ is a vector of corresponding parameters to be estimated. μi is an error term. Therefore, the observed farmer’s perception of increasing temperature (Pi) can be expressed as
where Pi = 1 represents that the farmer perceives the trend in increasing temperature in the local area, while Pi = 0 denotes that the farmer does not perceive this trend.
The propensity of the farmer’s household to adopt rubber intercropping as a mitigation behavior for the farmer’s perception of increasing temperature is expressed as
where the subscript P denotes the two regimes presented in Eq. 12. Xi is a vector of variables regarding the characteristics of the respondent, household, land, and village, while βPis a regime-specific vector of the parameters to be estimated; viP is a regime-specific error term.
Hence, by combining Eqs. 12 and 13, the observed mitigation behavior regarding rubber intercropping can be written as follows:
where Eqs. 14a and 15b indicate whether the farmer adopts rubber intercropping under the conditions of P = 1 and P = 0, respectively.
According to previous studies (Lokshin and Glinskaya 2009), the error terms (μi, vi0, vi1) from Eqs. 12, 14a, and 14b are assumed to be jointly normally distributed with a zero-mean vector and correlation matrix:
where the terms ρμ0 and ρμ1 are the correlations between vi0, vi1, and μ and ρ01 is the correlation between vi0 and vi1. However, as Ai1 and Ai0 are never observed simultaneously, the joint distribution of (v0, v1) is not identified; accordingly, ρ01 cannot be estimated. Hence, following the study by Lokshin and Sajaia (2011), we further assume that γ is estimable only up to a scalar factor (ρ01 = 1); therefore, this model can be identified by nonlinearities in its functional form. Following the study by Lokshin and Glinskaya (2009), we can express the log likelihood functions for the simultaneous system of Eqs. 12, 14a, and 14b as follows:
where Φ2 is the cumulative function of a bivariate normal distribution. Accordingly, function (20) can be estimated by the FIML method. The ESP model takes into account the unobserved variables that could simultaneously affect the farmer’s perception of increasing temperature and the farmer’s decision to adopt rubber intercropping. The application of the FIML method to simultaneously estimate the functions of these two decisions can yield consistent standard errors of the estimates (Lokshin and Sajaia 2011).
The impact of a farmer’s perception of increasing temperature on the adoption of rubber intercropping can be defined as treatment effects, including the effect of treatment on the treated (TT), the effect of the treatment on the untreated (TU), and the treatment effect (TE). Following previous studies (Lokshin and Glinskaya 2009; Lokshin and Sajaia 2011), the formulas of these treatment effects are given as:
Furthermore, the average treatment effect on the treated (ATT), the average treatment effect on the untreated (ATU), and the average treatment effect (ATE) can be obtained from Eqs. 17, 18, and 19 by averaging TT(x), TU(x), and TE(x) over the sample, respectively. ATT reflects the average difference between the predicted probability of adopting intercropping by a household that perceives increasing temperature and the predicted likelihood of adopting intercropping for the household had they not perceive increasing temperature. ATU is the average expected effect of perceiving increasing temperature on the probability that households with observed characteristic X, which do not perceive increasing temperature, would adopt intercropping. ATE is the average impact of perceiving increasing temperature on the probability that a household randomly drawn from the households with characteristics x would adopt intercropping. Additionally, the ATT, ATU, and ATT for a subgroup of the households are the averages of TT(x), TU(x), and TE(x) for that subgroup (Lokshin and Sajaia 2011).
1.1.2 Endogenous treatment effects model
Following Maddala (1983), the adoption intensity of rubber intercropping can be expressed as a treatment effects model:
where the definitions of Xi and Pi are the same as in Eq. 13. β and γ are parameters to be estimated, while εi is an error term. Meanwhile, εi and μi (in Eq. 11) are assumed to be bivariate normal with zero and covariance matrix:
where ρ is the correlation coefficient between εi and μi. According to Maddala (1983), the log likelihood for observation i can be written as:
where Φ(∙) is the cumulative distribution function of the standard normal distribution. Thus, Eqs 10 and 12 could be simultaneously estimated by maximum likelihood estimation.
Appendix C Test
The estimation results of a falsification test for the validity of the proposed two IVs are reported in Appendix Table 11. The results show that the proposed two instrumental variables significantly affect farmers’ perceptions of increasing temperature. However, for farmers who do not perceive increasing temperature, the proposed two IVs have insignificant impacts on the adoption of rubber intercropping. The proposed two instrumental variables meet the exclusion restriction. Hence, the falsification test empirically confirms the validity of the proposed two instrumental variables to control for the endogeneity of farmers’ perceptions of temperature change in explaining farmers’ implementation of the EFRP model.
Appendix D Unobserved heterogeneity
The effect of perceiving increasing temperature on the adoption of rubber intercropping by households can vary by observed household characteristics X and unobservables μ (Lokshin and Glinskaya 2009). To account for the unobserved heterogeneity, we can further simulate the MTE:
The MTE identifies the effect of perceiving increasing temperature on households induced to adopt rubber intercropping because of perceiving increasing temperature (Heckman and Vytlacil 2001; Lokshin and Glinskaya 2009).
Based on the estimation results of ESR, the simulated MTE is 0.342, nearly equal to the ATE, and heterogeneity in the effects of perceiving increasing temperature based on unobserved characteristics is also found (Fig. 5). Following the MTE framework (Lokshin and Glinskaya 2009), Fig. 5 plots the MTE of perceiving increasing temperature on the adoption of rubber intercropping against the normalized values of unobservable component (μ) at the household means for Xs according to Eq. 14a and 14b. The estimates of the MTE for perceiving increasing temperature on the adoption of rubber intercropping are monotonically increasing in μ, indicating that smallholders who are more likely to perceive increasing temperature are also more likely to adopt rubber intercropping. Additionally, the MTEs of perceiving increasing temperature on the adoption of rubber intercropping are not flat, which confirms the presence of unobservable heterogeneity in the impacts of farmers’ perceptions of increasing temperature on farmers’ decisions to adopt rubber intercropping.
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Min, S., Wang, X., Jin, S. et al. Climate change and farmers’ perceptions: impact on rubber farming in the upper Mekong region. Climatic Change 163, 451–480 (2020). https://doi.org/10.1007/s10584-020-02876-2
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DOI: https://doi.org/10.1007/s10584-020-02876-2