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Designing Payments for Environmental Services with Weak Property Rights and External Interests

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Payment for Environmental Services in Agricultural Landscapes

Part of the book series: Natural Resource Management and Policy ((NRMP,volume 31))

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Abstract

Payments for environmental services (PES) are often promoted as a mechanism for alleviating poverty and providing environmental benefits. This chapter analyzes PES design in a context where actors such as forest-dependent communities have only weak property rights over the forest, and where firms interested in commercial resource exploitation are present. A game-theoretical model of community-firm interactions is applied to the Indonesian setting where communities have been observed to negotiate logging deals with firms. As an alternative, PES design could focus on those communities with the lowest expected payments from logging deals. But these communities may not be able to enforce a PES agreement, while others would conserve the forest anyhow. Most importantly, the introduction of PES may increase a community’s expected payoff from a logging deal. A failure to consider this endogeneity in expected payoffs would lead to communities opting for logging deals despite PES, simply allowing communities to negotiate better logging deals. Potential trade-offs are shown to exist between maximizing environmental benefits and poverty alleviation, which implies the need for two policy tools, and not just one.

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Notes

  1. 1.

    1 These were taken from 65 community-level and 687 household interviews, although for direct comparison the sample was reduced to 62 communities (see Palmer,, 2006).

  2. 2.

    2 Note that data on the proportion of these concessions that were operationalized and the quantity of logs harvested are unavailable.

  3. 3.

    3 For a recent review, see Suyanto et al. (2005).

  4. 4.

    4 For details on RES projects, see http://www.worldagroforestry.org/sea/Networks/RUPES/mapsite_indonesia.htm.

  5. 5.

    5 A more general version of the model is presented in Engel and López (2004).

  6. 6.

    6 This implies that the player that would lose the conflict withdraws immediately. Actual conflict is possible with imperfect information, although the outcome will generally depend on the same parameters listed here (see Burton, (2004) , for a related model with imperfect information).

  7. 7.

    7 This assumption can be justified on the basis that communities are poor (have low savings) and have a disadvantage in the credit market vis-à-vis the firm, associated with capital market imperfections (see, e.g.for example, Bose, 1998).

  8. 8.

    8 For a more formal treatment of the conflict game, see Engel, López and Palme et al.r (2006).

  9. 9.

    9 In reality a pro forma agreement may still be negotiated and a minimum payment made to the community. This minimum payment is motivated by the idea that firms maintain political capital with the government officials who issued the logging permits (Palmer, 2005). However, this consideration does not affect the qualitative results that are of relevance for our purposes.

  10. 10.

    10 More precisely, their inside options (see Appendix).

  11. 11.

    11In practice, of course, ES provided by a hectare of standing forest may differ according to geographic and ecological conditions, an aspect that is ignored here as it is beyond the scope of this chapter.

  12. 12.

    12 Note that if PES is are ineffective in inducing forest conservation for a low pay-off community, , then it may not receive any payment, i.e., the PES program would have achieved zero environmental gains but at zero cost. Thus, where PES is are ineffective, it is not necessarily inefficient. In reality of course, upfront payments may be made before any conservation outcome is observed and there may be high transactions costs from negotiating the original PES agreement.

  13. 13.

    13 In the Indonesian context, where all households regularly go to the market to sell surplus produce for cash income regardless of distance, and where other employment opportunities are negligible, opportunity costs are likely to increase with distance to the market (Palmer, 2006). This is in contrast to other contexts where household participation is elastic to distance from market and greater distance implies lower opportunity costs.

  14. 14.

    14 If estimates only on some of the variables are available, then the average observed sample value could be used for the other variables for simplicity.

  15. 15.

    15 Of course, self-reporting may induce problems of asymmetric information, an important issue that is beyond the scope of this paperchapter.

  16. 16.

    16 Auction design would, however, require that communities be aware of the firm’s potential to raise its payments.

  17. 17.

    17 Following Engel and Palmer (in pressforthcoming2008), we abstract here from possible differences in the logging area between unilateral logging and a negotiated agreement.

References

  • Arifin B (2005) Institutional constraints and opportunities in developing environmental service markets: Lessons from institutional studies on RUPES in Indonesia. World Agroforestry Centre (ICRAF), Bogor, Indonesia.

    Google Scholar 

  • Barr C, Resosudarmo IAP (2002) Decentralization of forest administration in Indonesia: Community livelihoods and economic development. Center for International Forestry Research, Bogor, Indonesia.

    Google Scholar 

  • Barr C, Wollenberg E, Limberg G, Anau N, Iwan R, Sudana M, Moeliono M, Djogo T (2001) The impacts of decentralisation on forests and forest-dependent communities in Malinau district, East Kalimantan, Decentralisation and forests in Indonesia series: Case study 3. Center for International Forestry Research (CIFOR), Bogor, Indonesia.

    Google Scholar 

  • Binmore K (1985) Bargaining and coalitions. In: Roth A (ed.) Game-theoretic models of bargaining. Cambridge University Press, Cambridge.

    Google Scholar 

  • Bose P (1998) Formal-informal sector interaction in rural credit markets. J Dev Econ 56:265–280.

    Article  Google Scholar 

  • Bulow J, Rogoff K (1989) A constant recontracting model of sovereign debt. J Politi Econ 97:155–178.

    Article  Google Scholar 

  • Burton PS (2004) Hugging trees: Claiming de facto property rights by blockading resource use. Environ Resour Econ 27:135–163.

    Article  Google Scholar 

  • Casson A, Obidzinski K (2002) From new order to regional autonomy: Shifting dynamics of “illegal” logging in Kalimantan, Indonesia. World Dev 30:2133–2151.

    Article  Google Scholar 

  • Engel S, López R (2004) Exploiting common resources with capital-intensive technologies: The role of external forces. ZEF-Discussion Papers on Development Policy 90. Center for Development Research, Bonn (ZEF).

    Google Scholar 

  • Engel S, Palmer C (2006) Who owns the right? The determinants of community benefits from logging in Indonesia. For Policy Econ 8:434–446.

    Google Scholar 

  • Engel S, Palmer C (2008) Payments for environmental services as an alternative to logging under weak property rights: The case of Indonesia. Ecol Econ 65(4):799–809.

    Article  Google Scholar 

  • Engel S, López R, Palmer C (2006) Community-industry contracting over natural resource use in a context of weak property rights: The case of Indonesia. Environ Resour Econ 33:73–93.

    Article  Google Scholar 

  • Forest Watch Indonesia/Global Forest Watch (FWI/GFW) (2002) The state of the forest: Indonesia. Forest Watch Indonesia, Washington DC. Global Forest Watch, Bogor, Indonesia.

    Google Scholar 

  • Iwan R (2004) Mobilizing community conservation. A community initiative to protect its forest against logging in Indonesia. Paper prepared for the 10th Biennial Conference of the International Association for the Study of Common Property (IASCP), Oaxaca, Mexico.

    Google Scholar 

  • Landell-Mills N (2002) Developing markets for forest environmental services: An opportunity for promoting equity while securing efficiency? Philos Transact A Math Phys Eng Sci 360:1817–1825.

    Article  Google Scholar 

  • Landell-Mills N, Porras I (2002) Silver bullet or fools’ gold? A global review of markets for forest environmental services and their impact on the poor. International Institute for Environment and Development (IIED), London.

    Google Scholar 

  • Muthoo A (1999) Bargaining theory with applications. Cambridge University Press, Cambridge.

    Book  Google Scholar 

  • Pagiola S, Arcenas A, Platais G (2005) Can payments for environmental services help reduce poverty? An exploration of the issues and the evidence to date from Latin America. World Dev 33:237–253.

    Article  Google Scholar 

  • Palmer C (2004) The role of collective action in determining the benefits from IPPK logging concessions: A case study from Sekatak, East Kalimantan, Working Paper No. 28. Center for International Forestry Research (CIFOR), Bogor, Indonesia.

    Google Scholar 

  • Palmer C (2006) The outcomes and their determinants from community-company contracting over forest use in post-decentralization Indonesia. Dev Econ Policy 52, Peter Lang, Frankfurt.

    Google Scholar 

  • Palmer C, Obidzinski K (2002) Indonesia case study prepared for the report: Higher international standards or rent-seeking race to the bottom? The impacts of forest trade liberalisation of forest governance. Food and Agriculture Organisation (FAO), Project GCP/INT/775/JPN. Mimeo, Center for Development Research, Bonn, Germany.

    Google Scholar 

  • Resosudarmo IAP (2004) Closer to people and trees: Will decen-tralisation work for the people and the forests of Indonesia? Eur J Dev Res 16:110–132.

    Article  Google Scholar 

  • Ribot J (2002) Democratic decentralization of natural resources, institutionalizing popular participation. World Resources Institute, Washington, DC.

    Google Scholar 

  • Siikamäki J, Layton DF (2006) Potential cost-effectiveness of incentive payment programs for biological conservation. Discussion Paper No. 06-27, Resources for the Future, Washington, DC.

    Google Scholar 

  • Suyanto S, Leimona B, Permana RP, Chandler FJC (2005) Review of the development of an environmental services market in Indonesia. RUPES Working Paper. World Agroforestry Centre, South East Regional Office.

    Google Scholar 

  • Wollenberg E, Kartodihardjo H (2002) Devolution and Indonesia’s new forestry law. In: Colfer CJP, Resosudarmo P (eds.) Which way forward? People, forests and policymaking in Indonesia, pp. 81–109. Resources for the Future, Center for International Forestry Research (CIFOR) and Institute for Southeast Asian Studies (ISEAS).

    Google Scholar 

  • World Resources Institute (WRI) (2005) World resources 2005: The wealth of the poor – managing ecosystems to fight poverty. United Nations Development Programme, United Nations Environment Programme, World Bank, World Resources Institute, Washington, DC.

    Google Scholar 

  • Wünscher T, Engel S, Wunder S (2006) Payments for environmental services in Costa Rica: Increasing efficiency through spatial differentiation. Q J Int Agric 45(4):319–337.

    Google Scholar 

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Acknowledgment

Funding for this research was provided by the Robert Bosch Foundation, Germany (Grant No. 32.5.8041.0003.0).

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Appendix

Appendix

Let b denote per period values from the undisturbed forest to the community. If the firm wins the conflict, it receives profits v from logging unilaterally. The discount rates of the community and the firm are, respectively, r C and r F. Let c denote the firm’s fixed logging costs in each period it attempts to log unilaterally. The community can blockade firm activities at a cost of s per period. Where s > b/r C (in which

$$ \int\limits_{t = 0}^\infty {be^{ - rt} dt} = \frac{b}{{r_C }} $$

), the community never fights and the firm logs as long as v − c > 0. Where s < b, the community always fights, and the firm, knowing this, withdraws. For intermediate values of b (sr C < b < s), the boundary condition is found by equating the time that each actor can stay in conflict and still obtain non-negative net benefits:

$$ v = \Omega ,{\rm{ }}where{\rm{ }}\Omega \equiv \frac{c}{{r^F }}\left[ {\left( {\frac{{s\left( {1 - r^C } \right)}}{{s - b}}} \right)^{\frac{{\ln \left( {1 - r^F } \right)}}{{\ln \left( {1 - r^C } \right)}}} - 1 + r^F } \right] $$
((3.1))

The probability that the community is able to establish de facto property rights (PR) can thus be written as a function of model parameters:

$$ PR = g\left( {v,b,r_C ,r_F ,c,s} \right) $$
((3.2))

As argued in Engel et al. (2006), inspection of v =

$$ \Omega $$

indicates that

$$ \frac{{\partial PR}}{{\partial v}} \le 0,\;\frac{{\partial PR}}{{\partial b}} \ge 0,\;\frac{{\partial PR}}{{\partial r_C }} \le 0,\;\frac{{\partial PR}}{{\partial r_F }} \ge 0,\;\frac{{\partial PR}}{{\partial c}} \ge 0,\;\frac{{\partial PR}}{{\partial s}} \le 0 $$
((3.3))

As explained in the text, bargaining leading to a logging agreement is possible only when v <

$$ \Omega $$

. We distinguish two types of reservation utilities. Inside options are the payoffs obtained by each player while parties temporarily disagree and negotiations are ongoing (Bulow & Rogoff, 1989), denoted by d C and d F, for the community and the firm, respectively. Outside options, denoted by R C and R F, are the parties’ payoffs available when bargaining fails permanently (Binmore, 1985).

For an interior solution, the negotiation outcome in an alternating-offers bargaining game is given by the NBS (Muthoo, 1999). Thus, the negotiated payments to the community (

$$ \Pi $$

C) and firm (

$$ \Pi $$

F) are obtained by solving the following Nash bargaining problem

$$ \mathop {\max }\limits_{\Pi ^C ,\Pi ^F } \quad \left[ {\Pi ^C - d^C } \right]\,^\tau \;\left[ {\Pi ^F - d^F } \right]^{1 - \tau } \quad {\rm{s}}{\rm{.t}}{\rm{.}}\quad \Pi ^C + \Pi ^F = v - c $$
((3.4))

, 17 Footnote 17

where

$$ \tau $$

is the community’s bargaining power vis-á-vis the firm (

$$ 0 \le \tau < 1 $$

). The solution to Eq. (3.4) for the community’s payment is

$$ \tilde \Pi ^C = d^C + \tau \left( {v - c - d^C - d^F } \right) $$
((3.5))

The total “cake” to be divided in negotiations is v − c. The community’s inside option in the case where the community is able to self-enforce its property rights is given by the present value of the standing forest to the community. Thus,

$$ d^C = \frac{b}{{r_C }} $$

, and:

$$ \tilde \Pi ^C = \frac{b}{{r_C }} + \tau \left( {v - c - \frac{b}{{r_C }} - d^F } \right) $$
((3.6))

Equation (3.6) implies that community payoffs from a logging agreement are increasing in b and decreasing in r C . Engel and López (2004) show that the community’s payment can be written as

$$ \Pi ^C = h\left( {v,c,b,\tau ,d^F ,PR} \right)\quad {\rm{with}}\quad \frac{{\partial \Pi ^C }}{{\partial v}} \ge 0,\;\frac{{\partial \Pi ^C }}{{\partial c}} \le 0,\;\frac{{\partial \Pi ^C }}{{\partial b}} \ge 0,\;\frac{{\partial \Pi ^C }}{{\partial \tau }} \ge 0,\;\frac{{\partial \Pi ^C }}{{\partial d^F }} \le 0,\;\frac{{\partial \Pi ^C }}{{\partial PR}} \ge 0 $$
((3.7))

Using the expressions for PR, given in Eqs. (3.2) and (3.3), and considering that

$$ \tau $$

is itself increasing (decreasing) in the firm’s (community’s) discount rate, and increasing in other factors associated with higher bargaining power (p), Engel and Palmer (2006) obtain the following reduced-form relationship between

$$ \Pi ^C $$

and the model parameters:

$$ \Pi ^C = \tilde h\left( {v,c,b,r_F ,r_C ,\bar d^F ,s,p} \right)\quad {\rm{with}}\quad \frac{{\partial \Pi ^C }}{{\partial v}}\frac{ > }{ < }0,\;\frac{{\partial \Pi ^C }}{{\partial c}}\frac{ > }{ < }0,\frac{{\partial \Pi ^C }}{{\partial b}} \ge 0,\;\frac{{\partial \Pi ^C }}{{\partial r_F }} \ge 0,\;\frac{{\partial \Pi ^C }}{{\partial r_C }} \le 0,\;\frac{{\partial \Pi ^C }}{{\partial \bar d^F }} \le 0,\;\;\frac{{\partial \Pi ^C }}{{\partial s}} \le 0,\;\frac{{\partial \Pi ^C }}{{\partial p}} \ge 0 $$
((3.8))

As shown by Muthoo (1999), the interior solution in Eq. (3.5) holds only if

$$ \tilde \Pi ^C > R^C $$

. Otherwise, the community would receive R C in negotiations. Moreover, if

$$ R^C + R^F > v - c $$

, then negotiations will fail and the actors obtain their outside options.

Let P denote the per-period payment made under PES, which is conditional on the conservation of the forest, and b 0 is the community’s per-period valuation of the standing forest in the absence of PES. Thus, the community’s total valuation of the standing forest is

$$ b = b_0 + P $$
((3.9))

The community’s outside option increases with PES:

$$ R^C = \frac{{b_0 + P}}{{r_C }} $$
((3.10))

By raising b PES also raise the community’s willingness and ability to stay in a potential conflict. In summary, community payoffs from interacting with the logging firm are:

$$ \Pi ^C = \left\{ \begin{array}{l} 0\;\quad \;{\kern 1pt} {\kern 1pt} {\kern 1pt} {\kern 1pt} {\rm{if}}\quad v > \Omega \\ \tilde \Pi ^C \quad {\rm{if}}\quad v \le \Omega \quad {\rm{and}}\quad \tilde \Pi ^C > R^C \\ R^C \quad {\rm{if}}\quad v \le \Omega \quad {\rm{and}}\quad \tilde \Pi ^C \le R^C \\ \end{array} \right. $$
((3.11))

Moreover, if

$$ R^C + R^F > v - c $$

, where R C is given by Eq. (3.10), and v <

$$ \Omega $$

, negotiations would fail and forest protection would result (Engel et al., 2006). Because P affects

$$ \Omega $$

, R C, and possibly

$$ \tilde \Pi ^C $$

(the latter if and only if inside options are also affected by PES), the community’s expected payoff from a logging agreement is also affected by PES. More specifically, Eqs. (3.1), (3.6), (3.9), (3.10), and (3.11), together imply that

$$ \Pi ^C $$

are (weakly) increasing in P.

The conditions for effective PES can be summarized as follows:

Proposition: An effective PES scheme with per-period payment P conditional on resource conservation requires

  1. 1.

    v <

    $$ \Omega $$

    (P) (Community can enforce resource conservation),

  2. 2.
    $$ \frac{{b_0 }}{{r_C }} + R^F < v - c $$

    and v> c (Additionality, i.e., no negotiation failure in the absence of PES and logging is profitable), and

  3. 3.
    $$ \frac{{b_0 + P}}{{r_C }} + R^F > v - c $$
    ((3.12))

    (PES induce a breakdown of any potential resource extraction agreement).

With secure property rights, condition (1) in the proposition would be satisfied by default. Effective PES then have to satisfy conditions (2) and (3). Solving for the minimum effective payment (from condition 3), P min,

$$ P_{\min } = r_C \left[ {v - c - R^F } \right] - b_0 $$
((3.13))

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Engel, S., Palmer, C. (2009). Designing Payments for Environmental Services with Weak Property Rights and External Interests. In: Lipper, L., Sakuyama, T., Stringer, R., Zilberman, D. (eds) Payment for Environmental Services in Agricultural Landscapes. Natural Resource Management and Policy, vol 31. Springer, New York, NY. https://doi.org/10.1007/978-0-387-72971-8_3

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