Skip to main content

Advertisement

Log in

Additionality When REDD Contracts Must be Self-Enforcing

  • Published:
Environmental and Resource Economics Aims and scope Submit manuscript

Abstract

This paper examines self-enforcing contracts as a financial mechanism for reducing carbon emissions from deforestation and forest degradation when the opportunity cost of the land (i.e., landholder type) is private information and is imperfectly correlated over time (i.e., partially persistent types). Because self-enforcement limits the feasible incentives, the conservation levels are constrained by the surplus created. Regardless of the degree of persistence of such opportunity costs across contracting periods, a first-best self-enforcing contract can deliver “additional” carbon sequestration beyond the business as usual scenario only if the value of forest conservation is sufficiently high. Otherwise, self-enforcing contracts can induce some, suboptimal level of carbon sequestration. The degree of persistence of opportunity costs across periods does not affect the amount of total payments provided in the optimal menu of contracts, but greater persistence of opportunity cost types leads to contracts that feature more of the total payment as a bonus in contracts for landholders with a high opportunity cost for their land and more of the total payment as an upfront fixed payment for landholders with a low opportunity cost.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Fig. 1
Fig. 2

Similar content being viewed by others

Notes

  1. Specifically, Thomas and Worrall (1994) analyzed the use of self-enforcing contracts in the context of direct foreign investment.

  2. Buyers of carbon credits may also be interested in afforestation. The model here can be modified to address afforestation contracts and should be considered for future research; however, the contract issues relating to afforestation are distinct from those of conservation so are beyond the scope of this study.

  3. In this paper we address the pure objective of carbon sequestration by avoiding deforestation and degradation. We recognize that in some cases a stakeholder may be interested in afforestation contracts or in other objectives of REDD+ such as poverty reduction and biodiversity conservation (see Delacote et al. (2014) for more details on the various objectives of REDD+). The model here can be modified to include afforestation and other REDD+ goals. We do consider additional REDD+ objectives in Cordero Salas and Roe (2012). Nevertheless, these topics should be considered for future research.

  4. The optimal contract is designed to reward equally for either avoiding deforestation or avoiding degradation. However, we acknowledge that in practice there could be large cost differences in observing deforestation and degradation.

  5. Because the contracts are for forest conservation there are no upfront costs associated with the activity, in contrast to afforestation projects, in which there would be an upfront investment.

  6. We assume that the buyer’s net value of the conservation is positive for a certain level of observation costs. The key focus here is on formal contract enforcement, which we assume is weak and inefficient.

  7. We recognize that there may be two sources of asymmetric information: one on opportunity cost, and one related to the deforestation at the business as usual scenario. For simplicity, in this paper we assume that the business-as-usual deforestation is directly correlated to opportunity costs; this assumption allows us to assume that there is only one source of asymmetric information. Nevertheless, opportunity cost and BAU deforestation may not be positively related. A landholder with high opportunity costs may have relatively low deforestation levels if the marginal productivity of land is rapidly decreasing while a landholder with low opportunity costs, may have relatively high deforestation levels if the marginal productivity of land is slowly decreasing (see for example, Leplay et al. 2011).

  8. In practical terms, knowing if the landowner is a farmer or a timber producer provides information about the landholder’s type; however, historical information about land-use patterns or specific characteristics of the products and markets in which the landowner participates may better estimate the landholder’s type. Furthermore, a landholder’s type can also be applied if the landowner is a government. For instance, if the government has a strong conservation policy, it represents an \( h -type\) landholder, while if the government is characterized by low conservation effort then it is an \( l -type\) landholder. Contracting with governments may decrease the information asymmetry about the landholder’s type because the type may be easier to observe through government-conservation history and policies.

  9. Notice that a landholder places \(\theta _i\) in forest in the absence of carbon payments.

  10. Note that \(d { g} / d { f}_{ i}=\omega -c'(1-\theta _i-(f_i-\theta _i); \theta _i)\) and \(\omega \ge c'(1-\theta _i-(f_i-\theta _i); \theta _i)~ \forall ~f_i \in [\theta _i,1]\).

  11. The requested area in forest, \(f^{*}_i\), depends on the marginal benefit and marginal cost of keeping additional land as forest. It may be the case that the marginal cost of keeping all forest (mass 1) is greater than its marginal benefit. Therefore, it may be optimal to contract for \(f^{*}_i<1\).

  12. In practice, the contract defines a period, which can be a year or any convenient time unit. The buyer observes the forest conservation with some positive but low cost, such that the net value of conservation is positive.

  13. We have omitted the time subscripts throughout the paper where expressions relate to the stage game and where it is not confusing. When we refer to types in the past period we keep using \(t-1\).

  14. \(\Delta _ l \) can be thought of as the buyer’s expected additional per-period cost due to asymmetric information. Hence, it sets the upper limit on per-period expenditures the buyer would save by eliminating information asymmetries.

  15. When the buyer’s objectives include poverty alleviation, he may approve of giving the landholder larger information rents than if his only objective is carbon sequestration.

References

  • Abreu D (1988) On the theory of infinitely repeated games with discounting. Econometrica 56(2):383–396

    Article  Google Scholar 

  • Angelsen A (2008) Moving ahead with REDD: issues, options, and implications. Center for International Forestry Research (CIFOR), Bogor, Indonesia

  • Baker G, Gibbons R, Murphy K (1994) Subjective performance measures in optimal incentive contracts. Q J Econ 109:1125–1156

    Article  Google Scholar 

  • Baron DP, Besanko D (1984) Regulation, asymmetric information, and auditing. RAND J Econ 15(4):447–470

    Article  Google Scholar 

  • Bushnell JB (2011) Adverse selection and emissions offsets. Unpublished, https://ei.haas.berkeley.edu/research/papers/WP222

  • Chambers R (1992) On the design of agricultural policy mechanisms. Am J Agric Econ 74(3):646–654

    Article  Google Scholar 

  • Chiroleu-Assouline M, Poudou JC, Roussel S: North/South contractual design through the REDD+ Scheme. Unpublished, https://ideas.repec.org/p/mse/cesdoc/12059.html (2012)

  • Claassen R, Cattaneo A, Johansson R (2008) Cost-effective design of agri-environmental payment programs: US experience in theory and practice. Ecol Econ 65(4):737–752

    Article  Google Scholar 

  • Corbera E, Schroeder H (2011) Goverening and implementing REDD+. Environ Sci Policy 14:89–99

    Article  Google Scholar 

  • Cordero Salas P, Roe BE (2012) The role of cooperation and reciprocity in structuring carbon sequestration contracts in developing countries. Am J Agric Econ 94(2):411–418

    Article  Google Scholar 

  • de Koning F, Aguinaga M, Bravo M, Chiu M, Lascano M, Lozada T, Suarez L (2011) Bridging the gap between forest conservation and poverty alleviation: the ecuadorian socio bosque program. Environ Sci Policy 14:531–542

    Article  Google Scholar 

  • Delacote P, Palmer C, Bakkegaard RK, Thorsen BJ (2014) Unveiling information on opportunity costs in REDD: Who obtains the surplus when policy objectives differ? Resour Energy Econ 36(2):508–527

    Article  Google Scholar 

  • Ferraro PJ (2008) Asymmetric information and contract design for payments for environmental services. Ecol Econ 65:810–821

    Article  Google Scholar 

  • Fraser, R.: Land heterogeneity, agricultural income forgone and environmental benefit: an assessment of incentive compatibility problems in environmental stewardship schemes. J Agric Econ, pp 190–201 (2009)

  • Gjertsen H, Groves T, Miller DA, Niesten E, Squires D, Watson J: A contract-theoretic model of conservation agreements. Unpublished (2010)

  • Guiteras RP, Jack BK, Oliva P (2011) Additionality in developing countries: optimal contracts for avoided deforestation. Unpublished (2011)

  • Holloway V, Giandomenico E (2009) The history of REDD policy

  • Kerr S, Shuguang L, Pfaff A, Hendy J (2004) Tropical forest protection, uncertainty and the environmental integrity of carbon mitigation policies. Unpublished, Motu Working paper 04-03 (2004)

  • Laffont JJ, Martimort D (2002) The theory of incentives: the principal-agent model. Princeton University Press, Princeton

    Google Scholar 

  • Latacz-Lohmann U, Van derHamsvoort C (1997) Auctioning conservation contracts: a theoretical analysis and an application. Am J Agric Econ 79:407–418

    Article  Google Scholar 

  • Leplay S, Busch J, Delacote P, Thoyer S (2011) Implementation of national and international REDD mechanism under alternative payments for environemtal services: theory and illustration from Sumatra. Unpublished, https://ideas.repec.org/p/lam/wpaper/11-02.html

  • Levin J (2003) Relational incentive contracts. Am Econ Rev 93:835–847

    Article  Google Scholar 

  • Lewis TR, Sappington DE (1988) Regulating a monopolist with unknown demand and cost functions. RAND J Econ 19(3):438–457

    Article  Google Scholar 

  • MacKenzie IA, Ohndorf M, Palmer C (2012) Enforcement-proof contracts with moral hazard in precaution: ensuring ‘permanence’ of carbon sequestration. Oxf Econ Pap 64:350–374

    Article  Google Scholar 

  • MacLeod WB. (2006) Reputations, relationships and the enforcement of incomplete contracts. In: Working paper, IZA Discussion Paper 1978, Institute for the Study of Labor (IZA)

  • MacLeod WB, Malcomson J (1989) Implicit compatibility, and involuntary unemployment. Econometrica 57:447–480

    Article  Google Scholar 

  • MacLeod WB, Malcomson J (1998) Motivation and markets. Am Econ Rev 88:388–441

    Google Scholar 

  • Mason C, Plantinga A (2011) Contracting for impure public goods: carbon offsets and additionality. In: NBER working paper 16963 (2011)

  • Moxey A, White B, Ozanne A (1999) Efficient contract design for agri-environmental policy. J Agric Econ 50(2):187–202

    Article  Google Scholar 

  • Ozanne A, Hogan T, Colman D (2001) Moral hazard, risk aversion and compliance monitoring in agri-environmental policy. Eur Rev Agric Econ 28:329–347

    Article  Google Scholar 

  • Peterson JM, Boisvert RN (2004) Incentive-compatible pollution control policies under asymmetric information on both risk preferences and technology. Am J Agric Econ 86(2):291–306

    Article  Google Scholar 

  • Robalino J, Pfaff A, Sanchez-Azofeifa A, Alpizar F, Leon C, Rodriguez CM (2008) Deforestation impacts of environmental services payments: Costa Rica PSA Program 2000–2005. Discussion Paper Series, Environment for Development

  • Sanchez-Azofeifa A, Pfaff A, Robalino JA, Boomhower JP (2007) Costa Rica’s payment for environmental services program: intention, implementation, and impact. Conserv Biol 21(5):1165–1173

    Article  Google Scholar 

  • Sohngen B, Beach RH (2008) Avoided deforestation as a greenhouse gas mitigation tool: economic issues for consideration. J Environ Qual 37:1368–1375

    Article  Google Scholar 

  • Spulber DF (1988) Optimal environmental regulation under asymmetric information. J Public Econ 35:163–181

    Article  Google Scholar 

  • Strassburg JBB, Cattaneo A, Lubowski R, Bruner A, Rice R, Creed A, Ashton R, Boltz F (2009) Comparing climate and cost impacts of reference levels for reducing emissions from deforestation. Environ Res Lett 4 (2009)

  • Thomas J, Worrall T (1994) Foreign direct investment and the risk of expropriation. Rev Econ Stud 61:81–108

    Article  Google Scholar 

  • van Benthem A, Kerr S (2010) Optimizing voluntary deforestation policy in the face of adverse selection and costly transfers. Motu Economic and Public Policy Research

  • Wu J, Babcock BA (1996) Contract design for the purchase of environmental goods from agriculture. Am J Agric Econ 78:935–945

    Article  Google Scholar 

  • Yano Y, Blandford D (2009) Use of compliance rewards in agri-environmental schemes. J Agric Econ 60(3):530–545

    Article  Google Scholar 

Download references

Acknowledgments

This paper was prepared for the Development Economics Group of the World Bank as part of the project “A Mechanism for Reducing Emissions from Deforestation and Degradation (REDD): A Framework to Design Cost-effective Contracts.” The Bank’s Trust Fund for Environmentally and Socially Sustainable Development provided financial support. The views expressed in the paper are the authors’ alone and do not necessarily reflect views of the World Bank or its member countries. We are also grateful to Mike Toman for very useful comments and valuable feedback.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Paula Cordero Salas.

Additional information

REDD: Reducing Emissions from Deforestation and Forest Degradation.

Appendix

Appendix

Proof of Proposition 1

Following the arguments for incentive compatibility constraint (ICC) the \( h -type\) IRC does not bind while the ICC binds. From the ICCs we get equation: \(P_ h \ge g(f_ h ; \theta _ h )+ \Delta _ l \) as \(P_{\theta _ l }=0\). A buyer makes the highest payment to the \( h -type\) landholder and the lowest payment to the \( l -type\) landholder. Self-enforcement dictates that the difference between the highest possible payment and the lowest payment should be lower or equal to the gains from the contracts \(\frac{\delta }{1-\delta } (E(S(\theta ^ h _{t-1}))-r) \ge P_{ h }\) and \(\frac{\delta }{1-\delta } (E(S(\theta ^ l _{t-1}))-r) \ge P_{ h }\), where \(E(S(\theta ^ h _{t-1}))=\frac{\delta }{1-\delta } (\Phi ^ h _{t-1} S_ h + (1-\Phi ^ h _{t-1}) S_ l ) \) and \(E(S(\theta ^ l _{t-1}))=\frac{\delta }{1-\delta } (\Phi ^ l _{t-1}) S_ h + (1-\Phi ^ l _{t-1}) S_ l )\) are the expected surplus given that the landholder was a \( h -type\) or \( l -type\) in the previous period respectively. Combining this with ICCs we get the relationships in Proposition 1.

Proof of Proposition 2

To get the payment structure for the \( l -type\), we combine the IRC into the DICC as the ICC does not bind: \(p_ l =g(f_ l ; \theta _ l )- b_ l \) and as \(U_ h =\Delta _ l \) and \(U_ l =0\), \(b_ l \ge g(f_ l ; \theta _ l )- \frac{\delta \Phi ^ l _{t-1} \Delta _ l }{1-\delta }\). Substituting and arranging we get the minimum bonus and the maximum fixed price that satisfy the constraints. By solving in the buyer’s DICC and using the total payments derived by the landholder’s IRC constraints we obtain the maximum bonus and the minimum fixed price:

$$\begin{aligned}&g(f_ l ^{*}; \theta _ l ) +\frac{\delta (\Phi ^ l _{t-1}\Delta _ l ^*-ES(\theta ^ l _{t-1})-r)}{1-\delta } \le p^*_{ l } \le \frac{\delta \Phi ^ l _{t-1} \Delta _ l ^*}{1-\delta } \text {; and} \end{aligned}$$
(22)
$$\begin{aligned}&\quad \frac{\delta ( ES(\theta ^ l _{t-1})-r-\Phi ^ l _{t-1}\Delta _ l ^*)}{1-\delta }\ge b_ l \ge g(f_ l ^{*}; \theta _ l )- \frac{\delta \Phi ^ l _{t-1} \Delta _ l ^*}{1-\delta } \text {; and} \end{aligned}$$
(23)
$$\begin{aligned}&\quad P_ l = g(f_ l ^{*}; \theta _ l ). \end{aligned}$$
(24)

Similarly, to get the payment structure for the \( h -type\), we take the same steps but use the ICC and DICC as the IRC does not bind: \(p_ h =\Delta _ l +g(f_ h ; \theta _ h )- b_ h \) and \(b_ h \ge g(\theta _ h ; \theta _ h )- \frac{\delta \Phi ^ h _{t-1} \Delta _ l }{1-\delta }\). This results in the minimum bonus and the maximum fixed price that satisfy the constraints. By solving in the buyer’s DICC and using the total payments derived by the landholder’s ICC constraint we obtain the maximum bonus and the minimum fixed price:

$$\begin{aligned}&g(f_ h ^{*}; \theta _ h )+\frac{\Delta _ l ^*(1-\delta +\delta \Phi ^ h _{t-1}) -\delta (ES(\theta ^ h _{t-1})-r)}{1-\delta } \le p^*_{ h } \le \frac{ \Delta _ l ^*(1-\delta +\delta \Phi ^ h _{t-1}) }{1-\delta } \text {; and} \nonumber \\\end{aligned}$$
(25)
$$\begin{aligned}&\quad \frac{\delta (ES(\theta ^ h _{t-1})-r-\Phi ^ h _{t-1} \Delta _ l ^*)}{1-\delta }\ge b_ h \ge g(f_ h ^{*}; \theta _ h )- \frac{\delta \Phi ^ h _{t-1} \Delta _ l ^*}{1-\delta } \text {; and} \end{aligned}$$
(26)
$$\begin{aligned}&\quad P_ h = g(f_ h ^{*}; \theta _ h )+ \Delta _ l ^* \end{aligned}$$
(27)

The payments in Proposition 2 are derived by assuming that the buyer pays the minimum bonus required to meet the landholders’ DICC constraints. Finally, self-enforcement is sustainable if inequalities (17) and (18), are satisfied. The maximization problems that are set in the paper lead to the following Lagrangians. The first Lagrangian is given by:

$$\begin{aligned} L= & {} \frac{ \Phi ^ h _{t-1}(V(f_ h -\theta _ h )-g(f_ h ; \theta _ h ))+ (1- \Phi ^ h _{t-1})(V(f_ l -\theta _ l )-g(f_ l ; \theta _ l ))}{1-\delta }\\&+\mu \Big [\frac{\delta }{1-\delta } (\Phi ^ h _{t-1} (V(f_ h -\theta _ h )-g(f_ h ; \theta _ h )) + (1-\Phi ^ h _{t-1})(V(f_ l -\theta _ l )-g(f_ l ; \theta _ l )) -r)\\&- g(f_ h ; \theta _ h )-\Delta _ l \Big ]+\beta (f_ h -f_ l ) \end{aligned}$$

where \(\mu \) and \(\beta \) are the Lagrangian multipliers. The following are the FOC

$$\begin{aligned} \frac{d L}{d f_ h }= & {} \frac{ \Phi ^ h _{t-1} }{1-\delta } \left( \frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h }\right) \\&+\mu \left[ \frac{\delta }{1-\delta } \Phi ^ h _{t-1} \left( \frac{d V(f_ h -\theta _ h )}{d f_ h } - \frac{d g(f_ h ; \theta _ h )}{d f_ h }\right) - \frac{d g(f_ h ; \theta _ h )}{d f_ h }\right] \\&+\beta =0 \frac{d L}{d f_ l } = \frac{(1-\Phi ^ h _{t-1})}{1-\delta } \left( \frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l }\right) \\&+\mu \bigg [\frac{\delta }{1-\delta } (1-\Phi ^ h _{t-1}) \left( \frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l }\right) \\&-\left( \frac{d g(f_ l ; \theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _H)}{d f_ l }\right) \bigg ]-\beta =0 \\ \frac{d L}{d \mu }= & {} \frac{\delta }{1-\delta } (\Phi ^ h _{t-1} (V(f_ h -\theta _ h )-g(f_ h ; \theta _ h ))\\&+(1-\Phi ^ h _{t-1})(V(f_ l -\theta _ l )-g(f_ l ; \theta _ l )) -r) - g(f_ h ; \theta _ h )-\Delta _ l =0\\ \frac{d L}{d \beta }= & {} f_ h - f_ l =0 \end{aligned}$$

Case 1 Suppose \(\mu =0\).

This means that the self-enforcing constraint is slack at the solution: \(\frac{\delta }{1-\delta } ( \Phi ^ h _{t-1} S_ h + (1- \Phi ^ h _{t-1}) S_ l -r) \ge g(f_ h ; \theta _ h )+ \Delta _ l \). We consider maximizing the joint surplus subject to the monotonicity constraint, \(f_ h \ge f_L\). If \(\beta >0\), \(f_ h =f_ l \). This condition implies that \(\frac{ \Phi ^ h _{t-1} }{1-\delta }(\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })+ \frac{(1- \Phi ^ h _{t-1} )}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })=0\) which is not possible. As f is increasing in the type, it maximizes the joint surplus at the optimum for both types and satisfies monotonicity. That is, if \(\beta =0\) then \(f_ h ^{*}>f_ l ^{*}\); and from \(\frac{d L}{d f_ h }\), \(\frac{d V(f_ h -\theta _ h )}{d f_ h }=\frac{d g(f_ h ; \theta _ h )}{d f_ h }\) and from \(\frac{d L}{d f_ l }\), \(\frac{d V(f_ l -\theta _ l )}{d f_ l }= \frac{d g(f_ l ; \theta _ l )}{d f_ l }\). Then, \(f_ l =f_ l ^{*}\) and \(f_h=f_ h ^{*}\) and \(f_ h ^{*}>f_ l ^{*}\).

Case 2 Suppose \(\mu >0\).

This means that the self-enforcement constraint is binding at the solution: \(\frac{\delta }{1-\delta } ( \Phi ^ h _{t-1} S_ h + (1- \Phi ^ h _{t-1}) S_ l -r) \ge g(f_ h ; \theta _ h )+ \Delta _ l \). To have \(f_ h >f_ l \), \(\beta =0\) and the self-enforcing constraint must allow to cover for information rents for the \( h -type\). This implies that \(\frac{d L}{d f_ h }=\frac{\Phi ^ h _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })+\mu [\frac{\delta }{1-\delta } \Phi ^ h _{t-1} (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })- \frac{d g(f_ h ; \theta _ h )}{d f_ h }] =0\) and \(\frac{d L}{d f_ l } = \frac{(1-\Phi ^ h _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _ l )}{d f_ l })+\mu [\frac{\delta (1-\Phi ^ h _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })-(\frac{d g(f_ l ; \theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _ h )}{d f_ l }]=0\). Solving from each constraint we get \(\frac{d V(f_ h -\theta _ h )}{d f_ h }=\frac{d g(f_ h ; \theta _ h )}{d f_ h } [(1+\frac{\mu (1-\delta )}{\Phi ^ h _{t-1} (1+\mu \delta )}]\) which implies that \(f_ h <f_ h ^{*}\) and \(\frac{d V(f_ l -\theta _ l )}{d f_ l }=\frac{d g(f_ l ; \theta _ l )}{d f_ l } (1+ \frac{\mu (1-\delta )}{(1-\Phi ^ h _{t-1}) (1+\mu \delta )})+ \frac{d g(f_ l ; \theta _ h )}{d f_ l } \frac{\mu (1-\delta )}{(1-\Phi ^ h _{t-1}) (1+\mu \delta )} \) which implies that \(f_ l <f_ l ^{*}\). Therefore, \(f_ h >f_ l \) if the self-enforcing constraint is not too restrictive and the expected surplus is enough to cover some information rents.

If the self-enforcement constraint is too restrictive, forest conservation decreases up to the level in which incentives are cover by such constraint, resulting in the same level forest conservation delivered by both landholders. That is \(\beta >0\), \(\frac{d L}{d f_ h }=\frac{\Phi ^ h _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h }) +\mu [\frac{\delta \Phi ^ h _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })- \frac{d g(f_ h ; \theta _ h )}{d f_ h }] +\beta =0\) and \(\frac{d L}{d f_ l } = \frac{(1-\Phi ^ h _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l }) +\mu [\frac{\delta (1-\Phi ^ h _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })-(\frac{d g(f_ l ; \theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _ h )}{d f_ l }]-\beta =0\). This implies that \(\Phi ^ h _{t-1} (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })+ (1-\Phi ^ h _{t-1}) (\frac{d V(f_L-\theta _L)}{d f_L}- \frac{d g(f_L; \theta _L)}{d f_L})=\frac{\mu (1-\delta )}{(1+\mu \delta )} (\frac{d g(f_ h ; \theta _ h )}{d f_ h }+\frac{d g(f_L; \theta _L)}{d f_L}-\frac{d g(f_L; \theta _ h )}{d f_L}\) and \(\frac{\delta }{1-\delta } (E(S)_ l -r) = g(f_i; \theta _ l )\). Then, \(f_ h =f_ l \) is possible.

The second Lagrangian is given by:

$$\begin{aligned} L= & {} \frac{\Phi ^ l _{t-1}(V(f_ h -\theta _ h )-g(f_ h ; \theta _ h ))+(1-\Phi ^ l _{t-1})(V(f_ l -\theta _ l )-g(f_ l ; \theta _ l ))}{1-\delta }\\&\quad +\mu \bigg [\frac{\delta }{1-\delta } (\Phi ^ l _{t-1} (V(f_ h -\theta _ h )-g(f_ h ; \theta _ h ))\\&\quad +(1-\Phi ^ l _{t-1})(V(f_ l -\theta _L)-g(f_ l ; \theta _ l )) -r) \\&\quad - g(f_ h ; \theta _ h )-\Delta _ l \bigg ]+\beta (f_ h -f_ l ) \end{aligned}$$

where \(\mu \) and \(\beta \) are the Lagrangian multipliers. The following are the FOC

$$\begin{aligned} \frac{d L}{d f_ h }= & {} \frac{\Phi ^ l _{t-1}}{1-\delta } \left( \frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h }\right) \\&\quad + \mu \left[ \frac{\delta \Phi ^ l _{t-1}}{1-\delta } \left( \frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h }\right) - \frac{d g(f_ h ; \theta _ h )}{d f_ h }\right] \\&\quad +\beta =0 \frac{d L}{d f_ l } = \frac{(1-\Phi ^ l _{t-1})}{1-\delta } \left( \frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l }\right) \\&\quad +\mu \left[ \frac{\delta (1-\Phi ^ l _{t-1})}{1-\delta } \left( \frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l }\right) -\frac{d g(f_ l ; \theta _ l )}{d f_ l }\right. \\&\quad \left. -\frac{d g(f_ l ; \theta _ h )}{d f_ l }\right] -\phi =0\\ \frac{d L}{d \mu }= & {} \frac{\delta }{1-\delta } (\Phi ^ l _{t-1} (V(f_ h -\theta _ h )-g(f_ h ; \theta _ h ))\\&+(1-\Phi ^ l _{t-1})(V(f_ l -\theta _ l )-g(f_ l ; \theta _ l )) -r) - g(f_ h ; \theta _ h )\\&-\Delta _ l =0 \frac{d L}{d \beta } = f_ h - f_ l =0 \end{aligned}$$

Case 1: Suppose \(\mu =0\).

This means that the self-enforcing constraint is slack at the solution: \(\frac{\delta }{1-\delta } (E(S(\theta _{t-1}^ l )-r)> g(f_ h ; \theta _ h )+ \Delta _ l \). We consider maximizing the joint surplus subject to the monotonicity constraint, \(f_ h \ge f_ l \). If \(\beta >0\), \(f_ h =f_ l \). This condition implies that \(\frac{\Phi ^ l _{t-1}}{1-\delta }(\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })+ \frac{(1-\Phi ^ l _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })=0\) which is not possible. As f is increasing in the type, it maximizes the joint surplus at the optimum for both types and satisfies monotonicity. That is, if \(\phi =0\) then \(f_ h ^{*}>f_ l ^{*}\); and from \(\frac{d L}{d f_ h }\), \(\frac{d V(f_ h -\theta _ h )}{d f_ h }=\frac{d g(f_ h ; \theta _ h )}{d f_ h }\) and from \(\frac{d L}{d f_ l }\), \(\frac{d V(f_ l -\theta _ l )}{d f_ l }= \frac{d g(f_ l ; \theta _ l )}{d f_ l }\). Then, \(f_ l =f_ l ^{*}\) and \(f_h=f_ h ^{*}\) and \(f_ h ^{*}>f_ l ^{*}\).

Case 2: Suppose \(\mu >0\).

This means that the self-enforcement constraint is binding at the solution: \(\frac{\delta }{1-\delta } (E(S(\theta _{t-1}^ l )-r)> g(f_ h ; \theta _ h )+ \Delta _ l \). To have \(f_ h >f_ l \), \(\beta =0\) and the self-enforcing constraint must allow to cover for information rents for the \( h -type\). This implies that \(\frac{d L}{d f_ h }=\frac{\Phi ^ l _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })+\mu [\frac{\delta \Phi ^ l _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })- \frac{d g(f_ h ; \theta _ h )}{d f_ h }] =0\) and \(\frac{d L}{d f_ l } = \frac{(1-\Phi ^ l _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _ l )}{d f_ l })+\mu [\frac{\delta (1-\Phi ^ l _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })-(\frac{d g(f_ l ; \theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _ h )}{d f_ l }]=0\). Solving from each constraint we get \(\frac{d V(f_ h -\theta _ h )}{d f_ h }=\frac{d g(f_ h ; \theta _ h )}{d f_ h } [(1+\frac{\mu (1-\delta )}{\Phi ^ l _{t-1} (1+\mu \delta )}]\) which implies that \(f_ h <f_ h ^{*}\) and \(\frac{d V(f_ l -\theta _ l )}{d f_ l }=\frac{d g(f_ l ; \theta _ l )}{d f_ l } (1+ \frac{\mu (1-\delta )}{(1-\Phi ^ l _{t-1}) (1+\mu \delta )})+ \frac{d g(f_ l ; \theta _ h )}{d f_ l } \frac{\mu (1-\delta )}{(1-\Phi ^ l _{t-1}) (1+\mu \delta )} \) which implies that \(f_ l <f_ l ^{*}\). Therefore, \(f_ h >f_ l \) if the self-enforcing constraint is not too restrictive and the expected surplus is enough to cover some information rents.

If the self-enforcement constraint is too restrictive, the levels of forest conservation must decrease up to the level in which incentives are cover by such constraint. This means that it is possible that both landholders are required to deliver the same level forest conservation. That is \(\beta >0\), \(\frac{d L}{d f_ h }=\frac{\Phi ^ l _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h }) +\mu [\frac{\delta \Phi ^ l _{t-1}}{1-\delta } (\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })- \frac{d g(f_ h ; \theta _ h )}{d f_ h }] +\beta =0\) and \(\frac{d L}{d f_ l } = \frac{(1-\Phi ^ l _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l }) +\mu [\frac{\delta (1-\Phi ^ l _{t-1})}{1-\delta } (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })-(\frac{d g(f_ l ; \theta _ l )}{d f_ l }-\frac{d g(f_ l ; \theta _ h )}{d f_ l }]-\beta =0\). This implies that \(\Phi ^ l _{t-1}(\frac{d V(f_ h -\theta _ h )}{d f_ h }- \frac{d g(f_ h ; \theta _ h )}{d f_ h })+ (1-\Phi ^ l _{t-1}) (\frac{d V(f_ l -\theta _ l )}{d f_ l }- \frac{d g(f_ l ; \theta _ l )}{d f_ l })= \frac{\mu (1-\delta )}{(1+\mu \delta )} (\frac{d g(f_ h ; \theta _ h )}{d f_ h }+\frac{d g(f_ l ; \theta _ l )}{d f_ l }-\frac{d g(f_v; \theta _ h )}{d f_ l }\) and \(\frac{\delta }{1-\delta } (E(S(\theta ^ l _{t-1})-r) = g(f_i; \theta _ l )\). Then, \(f_ h =f_ l \) is possible.

Rights and permissions

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Cordero Salas, P., Roe, B.E. & Sohngen, B. Additionality When REDD Contracts Must be Self-Enforcing. Environ Resource Econ 69, 195–215 (2018). https://doi.org/10.1007/s10640-016-0072-9

Download citation

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s10640-016-0072-9

Keywords

JEL Classification

Navigation