Abstract
In decentralized water management with earmarked budgets financed by user taxes and distributed back in the form of subsidies, net gains are often heterogeneous across user categories. This paper explores the role of negotiation over budget allocation and coalition formation in water boards, to provide an explanation for such user-specific gaps between tax payments and subsidies. We propose a bargaining model to represent the sequential nature of the negotiation process in water districts, in which stakeholder representatives may bargain upon a fraction of the budget only. The structural model of budget shares estimated from the data on French Water Agencies performs well as compared with reduced-form estimation. Empirical results confirm the two-stage bargaining process and provide evidence for systematic net gains from the system for agricultural water users.
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Notes
Several empirical analyses of the BF bargaining model have been conducted, including Knight (2004, 2005) on decisions of the US House Committee on Transportation and Infrastructure, Ferejohn (1974) and Lewitt and Poterba (1999) on federal spending and representation by congressional delegations, Eraslan (2008) on bargaining in the BF vein in corporate finance, and Diermeier and Merlo (2004) on the analysis of the formation of coalition governments in Europe.
For any real number x, \(\left\lfloor x\right\rfloor \) denotes the smallest integer greater than x.
A coalition S is a winning one if and only if \(\sum _{i\in S}q_{i}\ge Q\). If, moreover, by dropping any player j we reverse the inequality, i.e., \( \sum _{i\in S\backslash \left\{ j\right\} }q_{i}<Q\) for any \(j\in S\), then such a coalition S is called minimal winning.
The component \(x_{ij}\) is the share of the budget offered to player i by proposer j.
This result implies that if n is odd, then the equilibrium is unique. However, if n is even, there is no single middle value, and the median is then can be defined as the mean of the two middle values.
In our setting, a difference is that the disagreement payoffs correspond to the relative amount of taxes paid.
This evidence is provided by interviews conducted by the authors with the deputy-CEO of the Adour-Garonne water agency on April 24, 2012, officials of the same Agency’s economic division, and members of the Adour-Garonne RBC on April 1, 2011.
According to the representative of industrial water users, Mr. Yves Casenove, “it is only with a global evaluation of subsidies and taxes that an objective comparison across user categories can be achieved. Such procedure has no other goal but to make sure the distribution of the budget is organized within reasonable bounds, in order to make progress in the concertation” (Adour-Garonne River Basin Committee meeting, July 4, 2011, Toulouse).
Subsidy figures from Water Agencies are detailed by final user but, from a non-budgetary point of view, there may be indirect beneficiaries to projects. For example, abatement projects for livestock farmers may be beneficial in terms of raw water quality to residential users; extension of a water distribution network may benefit industrial plants within city bounds, etc. We acknowledge this can be a source of bias which cannot be corrected given available data, but from a strictly budgetary point of view, final beneficiaries from subsidy decisions are correctly identified.
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The authors gratefully acknowledge financial support from the Adour-Garonne Water Agency. They wish to thank Bruno Cinotti, Frédéric Caméo-Ponz, Jean-Michel Grandmont, Kerry Krutilla, Cuong Le Van and Stéphane Robichon for helpful comments and discussions. We thank Michel Le Breton for very helpful discussions on a first version of this paper.
Appendices
Appendix 1: Proof of Proposition 1
Taking derivatives of V with respect to \(\alpha \) one gets:
and
Since \(u_{i}^{\prime \prime }(\cdot )<0\) it follows from (24) that \( V_{i}^{\prime \prime }\left( \alpha \right) \le 0\).
From (23) it follows that:
Therefore, for \(\gamma _{i}\ge \overline{\gamma }_{i}=\left( \widehat{p}_{i}\sum _{j\in N\backslash (S_{i}\cup \left\{ i\right\} )}\gamma _{j}\right) /\left( 1- \widehat{p}_{i}-P_{i}\right) \), the function \(V_{i}^{\prime }\left( 1\right) \ge 0\), and for \(\gamma _{i}\le \overline{\gamma }_{i}\) the opposite inequality holds true.
The derivative of V at \(\alpha =0\) is:
One can check that: \(V_{i}^{\prime }\left( 0\right) \le 0\) if and only if \( \gamma _{i}\le \underline{\gamma }_{i}\), where \(\underline{\gamma }_{i}\) satisfies (14).
Since \(u_{i}^{\prime \prime }\le 0\) we can deduce that \(u_{i}^{\prime }(0)\ge u_{i}^{\prime }\left( \sum _{j\in N\backslash S^{i}}\gamma _{j}\right) \). Substituting this into (14) we prove that \( \underline{\gamma }_{i}\le \overline{\gamma }_{i}\).
Summing up, for \(0\le \gamma _{i}\le \underline{\gamma }_{i}\) the function \(V_{i}\left( \alpha \right) \) is decreasing on the whole interval \(\left[ 0,1 \right] \), for \(\gamma _{i}\ge \overline{\gamma }_{i}\) it is increasing on the whole interval, and for \(\underline{\gamma }<\gamma _{i}<\overline{ \gamma }_{i}\) it has unique maximum on the interval \(\left[ 0,1\right] \).
Appendix 2: Derivation of Optimal \(\alpha ^* \)
From Proposition 1, the thresholds for group 2 are:
Therefore, the behavior of player 2 can be described as follows:
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for \(\displaystyle {\frac{\gamma _{3}}{\gamma _{2}} < \frac{\widehat{p}_{3}}{ \widehat{p}_{2}}}\), function \(V_{2}\left( \alpha \right) \) increases on the whole interval \(\left[ 0,1\right] \) and therefore \(\alpha _{2}^{*}=1\);
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for \(\displaystyle {\frac{\widehat{p}_{3}}{\widehat{p}_{2}} < \frac{\gamma _{3}}{\gamma _{2}}<\frac{\widehat{p}_{3}}{\widehat{p}_{2}}\frac{ u_{2}^{\prime }(0)}{u_{2}^{\prime }\left( \gamma _{2}+\gamma _{3}\right) }}\) , function \(V_{2}\left( \alpha \right) \) has an inferior maximum \(\alpha _{2}^{*}\) on \(\left[ 0,1\right] \) which is defined from the equality \( V_{2}^{\prime }\left( \alpha \right) =0\), that is,
$$\begin{aligned} -\widehat{p}_{2}u_{2}^{\prime }\left( \alpha \gamma _{2}+(1-\alpha ) \left( 1-\gamma _{1}\right) \right) \gamma _{3}+\widehat{p}_{3}u_{2}^{\prime }(\alpha \gamma _{2})\gamma _{2}=0\text {;} \end{aligned}$$(25) -
for \(\displaystyle {\frac{\gamma _{3}}{\gamma _{2}} > \frac{\widehat{p}_{3}}{ \widehat{p}_{2}}\frac{u_{2}^{\prime }(0)}{u_{2}^{\prime }\left( \gamma _{2}+\gamma _{3}\right) }}\), function \(V_{2}\left( \alpha \right) \) is decreasing on the whole interval \(\left[ 0,1\right] \) and therefore \(\alpha _{2}^{*}=0\).
In a similar way, the thresholds on the tax share for player 3 can be expressed as follows:
The behavior of player 3 can be summarized as:
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for \(\displaystyle {\frac{\gamma _{3}}{\gamma _{2}} < \frac{\widehat{p}_{3}}{ 1-\widehat{p}_{3}}\frac{u_{3}^{\prime }\left( \gamma _{2}+\gamma _{3}\right) }{u_{3}^{\prime }(0)}}\) function \(V_{3}\left( \alpha \right) \) is decreasing on the whole interval \(\left[ 0,1\right] \) and therefore \(\alpha _{3}^{*}=0\);
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for \(\displaystyle {\frac{\widehat{p}_{3}}{1-\widehat{p}_{3}}\frac{ u_{3}^{\prime }\left( \gamma _{2}+\gamma _{3}\right) }{u_{3}^{\prime }(0)}< \frac{\gamma _{3}}{\gamma _{2}}<\frac{\widehat{p}_{3}}{1-\widehat{p}_{3}}}\), function \(V_{3}\left( \alpha \right) \) has an inferior maximum \(\alpha _{3}^{*}\) on \(\left[ 0,1\right] \) and it is defined from \(V_{3}^{\prime }\left( \alpha \right) =0\):
$$\begin{aligned} -\widehat{p}_{3}u_{3}^{\prime }\left( \alpha \gamma _{3} + (1-\alpha ) \left( 1-\gamma _{1}\right) \right) \gamma _{2}+(1-\widehat{p}_{3})u_{3}^{\prime }(\alpha \gamma _{3})\gamma _{3}=0\text {;} \end{aligned}$$(26) -
for \(\displaystyle {\frac{\gamma _{3}}{\gamma _{2}} > \frac{\widehat{p}_{3}}{ 1-\widehat{p}_{3}}}\), function \(V_{3}\left( \alpha \right) \) is increasing on the whole interval \(\left[ 0,1\right] \) and therefore \(\alpha _{3}^{*}=1\).
We can identify the median voter: it is either player 2 if \(\displaystyle { \frac{\gamma _{3}}{\gamma _{2}} > \frac{\widehat{p}_{3}}{\widehat{p}_{2}}}\) or player 3 if the opposite inequality holds.
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Thomas, A., Zaporozhets, V. Bargaining Over Environmental Budgets: A Political Economy Model with Application to French Water Policy. Environ Resource Econ 68, 227–248 (2017). https://doi.org/10.1007/s10640-016-0013-7
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DOI: https://doi.org/10.1007/s10640-016-0013-7