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 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).
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2 Note that data on the proportion of these concessions that were operationalized and the quantity of logs harvested are unavailable.
- 3.
3 For a recent review, see Suyanto et al. (2005).
- 4.
4 For details on RES projects, see http://www.worldagroforestry.org/sea/Networks/RUPES/mapsite_indonesia.htm.
- 5.
5 A more general version of the model is presented in Engel and López (2004).
- 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 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 For a more formal treatment of the conflict game, see Engel, López and Palme et al.r (2006).
- 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 More precisely, their inside options (see Appendix).
- 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 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 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 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 Of course, self-reporting may induce problems of asymmetric information, an important issue that is beyond the scope of this paperchapter.
- 16.
16 Auction design would, however, require that communities be aware of the firm’s potential to raise its payments.
- 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.
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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
), 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:
The probability that the community is able to establish de facto property rights (PR) can thus be written as a function of model parameters:
As argued in Engel et al. (2006), inspection of v =
indicates that
As explained in the text, bargaining leading to a logging agreement is possible only when v <
. 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 (
C) and firm (
F) are obtained by solving the following Nash bargaining problem
where
is the community’s bargaining power vis-á-vis the firm (
). The solution to Eq. (3.4) for the community’s payment is
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,
, and:
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
Using the expressions for PR, given in Eqs. (3.2) and (3.3), and considering that
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
and the model parameters:
As shown by Muthoo (1999), the interior solution in Eq. (3.5) holds only if
. Otherwise, the community would receive R C in negotiations. Moreover, if
, 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
The community’s outside option increases with PES:
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:
Moreover, if
, where R C is given by Eq. (3.10), and v <
, negotiations would fail and forest protection would result (Engel et al., 2006). Because P affects
, R C, and possibly
(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
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.
v <
$$ \Omega $$(P) (Community can enforce resource conservation),
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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
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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,
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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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