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The Impact of Unilateral Commitment on Transboundary Pollution

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Abstract

To reach a common target of environmental quality, countries can choose to commit to a stream of pollution abatement right from the beginning of the game or decide upon abatement at each moment of time. Though most of the previous literature studies homogeneous strategies where no country or all countries commit to a (same) predefined policy, reality goes along a different way: some countries make more efforts than others to reduce pollutant emission. The main novelty of this paper resides in the introduction of this kind of heterogeneous strategic behavior currently observed among large pollution nations. We find that the pollution level can be lower under heterogeneous than under homogeneous strategies. A stringent environmental quality target will induce the committed player to produce an abatement effort that more than compensates the free-riding attitude of the non-committed player.

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Notes

  1. After the 2015 United Nations Climate Change Conference in Paris the effects of unilateral commitment to environmental issues received a lot of attention. A whole section of the SURED 2016 conference was devoted to this topic, see http://ces.univ-paris1.fr/SURED2016/Programme.htm.

  2. See Long [16] for a complete survey about the application of differential games in economics studies. An early contribution regarding the choice of strategy space can be found in the seminal paper of Reinganum and Stokey [18].

  3. Reasons for the lack of efficient action so far can be traced back to a number of difficulties in setting up efficient policies in light of climate change. Many of those that may have contributed to the dead end of negotiations so far have been highlighted by experts from the IPCC ([14], Aflaki [1]); as, e. g., disagreements on the long-term consequences of GHG emissions on climate (and the ensuing costs) or the asymmetric divide of costs of climate change and benefits of mitigation thereof.

  4. Our heterogeneous strategy setting should be distinguished from an asymmetric setting where both players still adopt the same strategy space (e.g., Markovian) but do not take the same action. For example, Reinganum [19] develops a model, where two identical players play asymmetric Markovian strategies.

  5. More details on our heterogeneous strategy setting are provided in Section 3.

  6. Copenhagen Accord [20], p.2, http://unfccc.int/resource/docs/2009/cop15/eng/l07.pdf.

  7. If we take into account uncertainty, this law of motion of pollution accumulation could be presented by an Ito stochastic differential equation and the objective function would change to expected utility.

  8. Notice that in the present paper all players make their decisions simultaneously. In contrast, in the context of unilateral commitment one could also think of a situation in which the committed player moves first and announces her strategy (the Stackelberg leader), while the non-committed player decides subsequently on her strategy (the follower). This game structure would give rise to a Stackelberg differential game in which we distinguish between two solution concepts: open-loop Stackelberg equilibrium and Markovian Stackelberg equilibrium. A drawback of open-loop Stackelberg equilibria is that, in general, they are not time consistent even for infinite time horizon. Similarly, there is no general method of finding non-degenerate Markovian Stackelberg equilibria. An early application of Stackelberg differential games to a problem of pollution control can be found in Long [15]. Calvo and Rubio [4] provide a more recent discussion of the Stackelberg differential games in the pollution control problem.

  9. For a detailed definition consult Dockner et al. [7] or Reinganum and Stokey [18].

  10. Guessing techniques are used very often in the application of differential games. See more in Long [16].

  11. Sufficiency can be found, for example, in Dockner et al. ([7]; Theorem 3.2)).

  12. It is straightforward to see that the latter is indeed a non-degenerate Markovian Nash Equilibrium.

  13. The numerical solutions for the cases in which both play Markovian or heterogeneous strategies are obtained analogously.

  14. Our special setting makes this two-step procedure possible. Generally, state and costate equations should be solved simultaneously, which is more difficult. However, applying an intermediate matrix to keep record of the intermediate process is essentially the same. For more details about the methodology see Camacho et al. [5].

  15. We discuss further below findings for cases where countries are asymmetric, see Tables 2 and 3.

  16. We could impose another terminal condition along the lines of the target of the EU 2020 energy package, which is defined as a 20 per cent reduction in EU greenhouse gas emissions from 1990 levels. Economically, such a condition is not problematic, however, mathematically, it raises severe issues. Notice that this way of setting a terminal condition (see Goldman [11], Chiang [6] and references therein, for more and systematic statements of different types of transversality conditions) by imposing both a terminal time T and a terminal stock, x(T), implicitly imposes also \(\lambda _{m,i}(T)= \lambda _{m,j}(T)= {\partial S(x^{*}(\overline {T}))\over \partial x}\). With the initial condition, x(0), being given at the same time, this lead to a rather more complicated terminal condition on the costate variables (See Theorem 8.2 and 4.1, Hartl et al. [12].). Thus, to avoid this difficulty and to be consistent with the theoretical part developed in the previous section, we choose to impose the terminal conditions on the costate variables, \(\lambda _{m,i}(\overline {T})\) and \(\lambda _{m,j}(\overline {T})\), in system (11).

  17. Another possibility to choose this function would have consisted in taking the same function as in the utility function (2), that is, \(S(x(\overline {T}))=-e^{-r\overline {T}}x(\overline {T}) \). Though this is a straightforward choice from the utility function, it is hard to justify the long-run solution if S(x(T)) → 0 as T → + .

  18. Note that we could assume also a scenario with different α’s but this has a similar effect that different r’s.

  19. Notice that the exogenous function E(t) may depend on time t, in particular during the short-run. The dynamic programming HJB equation becomes a real partial differential equation with term V t , given there is no boundary (or transversality) condition and non-linear-quadratic setting. In general, this makes the search for a solution more difficult, and stationarity usually does not hold any more. From this point of view, with E(t) a given function of time t, Pontryagin’s maximum principle provides richer results.

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Acknowledgments

This paper should not be reported as represen ting the views of the Central Bank of Luxembourg or the Eurosystem. The views expressed are those of the authors and may not be shared by other research staff or policymakers in the Central Bank of Luxembourg or the Eurosystem. This project was initiated when Luca Marchiori was researcher at the University of Luxembourg.

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Correspondence to Luisito Bertinelli.

Appendix A: Homogenous strategies:

Appendix A: Homogenous strategies:

1.1 A.1 Open-loop strategies

For simplicity, we suppose the two countries are symmetric, commit to an abatement strategy based only upon time t and ignore the actual state of pollution. Player i’s objective function consists in maximizing her utility with respect to u i (t),

$$ \max_{u_{i}(t)}{\int}_{0}^{\overline{T}} e^{-r_{i} t}\left( -x(t)-{\alpha_{i}\over 2}{u^{2}_{i}} \right)dt+ S(x(\overline{T})),\;\; $$
(12)

subject to the state constraint (1).

It is easy to see that player i’s Hamiltonian functionFootnote 19 is

$$\begin{array}{@{}rcl@{}} H_{i}(x,u_{i},\lambda_{i}, t)&=&\left( -x(t)-{\alpha_{i}\over 2}{u^{2}_{i}} \right)\\ &&+\lambda_{i}\left[E(t)-(u_{i}+u_{j}^{*}(t))\sqrt{x(t)}-\delta x(t) \right], \end{array} $$

where \(u_{j}^{*}\) represents the optimal strategy of variable u j of player j.

Pontryagin’s maximum principle leads to

$$ u_{i}(t)=-{\lambda_{i}(t)\sqrt{x(t)} \over \alpha_{i}}, $$
(13)

and the costate variable, the shadow value here, is

$$ \dot{\lambda}_{i}(t)=r_{i}\lambda_{i}(t)-{\partial H_{i}\over \partial x}=(r_{i}+\delta)\lambda_{i}+{u_{i}+u_{j}^{*} \over 2\sqrt{x}}\lambda_{i}+1, $$
(14)

with transversality condition

$$ \lim_{t\to \infty} e^{-r_{i} t} \lambda_{i}(t) x(t)=0, \;\;\text{or} \;\; \lambda(T)= S_{x}(x^{*}(T)). $$
(15)

Remark

From Eq. 14, we can see that the natural absorption rate δ has the same effect as the time preference r i . In the following calculation, we will set δ = 0, i.e., set r i = r i + δ, while referring to it when interpreting our results.

Furthermore, supposing symmetry between countries, i.e., r i = r j = r, α i = α j = α, we have

$$u_{i}(t)=u_{j}(t)=u(t),\; \lambda_{i}(t)=\lambda_{j}(t)=\lambda(t). $$

This symmetry is preserved for the optimal values, such that the above analysis yields the following system

$$ \left\{ \begin{array}{l} u^{*}(t)=-{\lambda(t) \sqrt{x(t)}\over \alpha},\\[.12in] \dot{x}= E(t)+{2\lambda x(t)\over \alpha}-\delta x(t),\\[.12in] \dot{\lambda}= 1+r\lambda -{\lambda^{2}\over \alpha}, \end{array} \right. $$
(16)

with the initial condition and the transversality condition (15) given. The shadow price λ (which comes from a Riccati equation) can be solved explicitly, while pollution state x is a linear equation. Hence, we obtain the explicit solution for the open-loop problem. For the long-run steady state, it yields,

$$ \left\{ \begin{array}{ll} \displaystyle \lambda(t)&= \displaystyle \overline{\lambda}={\alpha r\over 2}-A (<0),\;\;\overline{T}=\infty, \\[.2in]\;\; \displaystyle x_{o}(t) & = \displaystyle e^{{2 \overline{\lambda} \over \alpha}t} \left[x(0)+{{\int}_{0}^{t}} e^{-{2 \overline{\lambda} \over \alpha} s}E(s)ds \right],\;\;\overline{T}=\infty \end{array} \right. $$
(17)

with \(A= \sqrt {\alpha + \left ({ r\alpha \over 2}\right )^{2}}\).

While, if \(\overline {T}=T<\infty \), the short-run dynamics are given as follows: for 0 < t < T,

$$ \left\{ \begin{array}{l} \displaystyle \lambda(t) = \left\{ \begin{array}{l} \displaystyle {r\alpha\over 2}+A- {2A \over C_{o} e^{2At\over \alpha}+1} , \;\text{if} \;S_{x}(x^{*}(T)) \not= {r\alpha\over 2}-A, \\[.2in] \displaystyle {r\alpha\over 2}-A (=\overline{\lambda} ),\;\text{if} \; S_{x}(x^{*}(T))={r\alpha\over 2}-A, \end{array} \right.\\[.35in] \displaystyle x_{o}(t) \!= \displaystyle e^{{{\int}_{0}^{t}} {2\lambda(s)\over \alpha}ds}\left[ x(0)\,+\, {{\int}_{0}^{t}} e^{-{\int}_{0}^{\tau{2 \lambda(s) \over \alpha} }ds}E(\tau)d\tau\right], \;\;\overline{T}=T\!<\infty, \end{array} \right. $$
(18)

with \( \displaystyle C_{o}= {A+\left [S_{x}(x^{*}(T))-{r\alpha \over 2}\right ] \over A- \left [S_{x}(x^{*}(T))-{r\alpha \over 2}\right ]}\;e^{-{2A\over \alpha }T}\).

The above explicit solutions provide the short-run dynamics of the system under the open-loop strategy. Compared with the infinite time horizon, where the shadow price is always a constant over time, if there is a finite time target for the pollution level, S(x(T)), the shadow value, λ(t), changes over time to match this final target. The explicit solution yields

$$\dot{ \lambda}(t) = \left\{ \begin{array}{l} >0, \;\text{if} \;0>S_{x}(x^{*}(T))>{r\alpha\over 2}-A, \\[.2in] \displaystyle 0,\;\text{if} \; S_{x}(x^{*}(T))={r\alpha\over 2}-A, \\[.2in] \displaystyle <0, \;\; \text{if} \;S_{x}(x^{*}(T))<{r\alpha\over 2}-A(<0). \end{array} \right. $$

Recall the shadow value λ measures the unit effect of pollution, hence, it is not surprising to notice that the short-run dynamics depend essentially on the slope of the terminal condition S x , rather than on the terminal condition itself. Except in a perfect setting where the dynamics are constant and equal to exactly the long-run steady state, we have either over-shooting by imposing a too fast change at the end (∣S x (x (T))∣ is too large, \(S_{x}(x^{*}(T))<{r\alpha \over 2}-A\)) or under-shooting by imposing a too slow change at the end (∣S x (x (T))∣ is too small, \({r\alpha \over 2}-A<S_{x}(x^{*}(T))<0\) ). In any of these two cases, the shadow price will not converge to its long-run steady state. Therefore, the short-run target may mislead the shadow value function during the transition, unless it is already at its steady-state level.

We can conclude the above analysis as follows.

Proposition 1

The optimal open-loop strategies yield:

  1. (I)

    In the short-run, the dynamics of the shadow value and the level of pollution depend on the terminal condition and the slope of the terminal condition, and are given by Eq. 18 .

  2. (II)

    In the long-run, the shadow value is a constant and the level of pollution is changing over time, as noted in Eq. 17 .

    Moreover, there are three possibilities based on the emission of pollution.

    1. (II.1)

      If pollution emission \(E=\overline {E}\) is a constant, there is a unique steady state, where states of pollution and abatement are constants and given by

      $$x^{*}_{o}=-{\alpha \overline{E}\over 2\lambda^{*}},\;\; u^{*}_{o}=-{\lambda^{*}\sqrt{x^{*}}\over \alpha}. $$
    2. (II.2)

      If pollution emissions E = E(t)are increasing (or decreasing) over time with constant growth rate g E ,the pollution state will increase (or decrease) at the same rate g E while abatement increases(or decreases) at rate \({g_{E}\over 2}\).But the shadow value of the pollution is the same constant as above.

    3. (II.3)

      If pollution emission E = E(t)is neither of the above cases, then there is no balanced growth path nor a steady state.

1.2 A.2 Markovian Nash Equilibrium

Now suppose that both countries can change the abatement strategies based on the pollution state. Then each player is facing the same problem as above by choosing the abatement strategy u i (t) =Ψ i (x(t),t) for a given guessing optimal strategy of player j, \({\Phi }_{j}(x, t), \forall (x,t)\in \mathbb {R}_{+}^{2}\). In the sequel, we will employ similar conjecturing methods as in the heterogeneous strategies case to look at one particular symmetric Markovian Nash Equilibrium.

Player i’s Hamiltonian function is

$$\begin{array}{@{}rcl@{}} &&{} H_{i}(x,u_{i}, \phi_{i}, {\Phi}_{j}(x,t), t)=\left( -x(t)-{\alpha_{i}\over 2}{u^{2}_{i}} \right)\\ &&+\phi_{i}\left[E(t)-\left( \!\!\right.u_{i}+{\Phi}_{j}(x,t)\sqrt{x(t)} \right], \end{array} $$

with ϕ i being player i’s costate variable and Φ j (x,t) being player i’s guess of player j’s optimal strategy.

Pontryagin’s maximum principle yields

$$ u_{i}(t)=-{\phi_{i}(t)\sqrt{x(t)} \over \alpha_{i}}, $$
(19)

and

$$\begin{array}{@{}rcl@{}} \dot{\phi}_{i}(t)&=&r_{i}\phi_{i}(t)-{\partial H_{i}\over \partial x}=r_{i}\phi_{i}+1+ {u_{i}+{\Phi}_{j}(x,t) \over 2\sqrt{x}}\phi_{i}\\ &&+ \phi_{i} \sqrt{x}{\partial {\Phi}_{j}(x,t)\over \partial x}, \end{array} $$
(20)

and its terminal condition. By conjecturing the optimal strategy of player j, \( {\Phi }_{j}(x, t)=-{\phi _{j}(t)\sqrt {x} \over \alpha _{j}}\), together with the symmetry assumption and the search for a symmetric solution, it follows that the optimal strategy and costate variable check

$$ \left\{ \begin{array}{l} u_{i}^{*}(t)=u_{j}^{*}(t)=u^{*}(t)= -{\phi(t)\sqrt{x}\over \alpha} ,\\[.12in] \dot{x}= E(t)+ {2\phi x \over \alpha},\\[.12in] \dot{\phi}= 1+r\phi-{3\phi^{2}\over 2\alpha}, \end{array} \right. $$
(21)

with the initial condition and the transversality condition given.

Using similar methods to the ones used to obtain (18), we could get a similar explicit solution for the short-run and long-run dynamics, especially for the effect of the short-run target on the dynamics.

The long-run explicit solution to the Markovian strategy is given by

$$\begin{array}{@{}rcl@{}} \phi(t)&=&\overline{\phi}={1\over 3}\left( \alpha r- \sqrt{(\alpha r)^{2}+6\alpha} \right)(<0), \;\;\; x_{m}(t)\\ &=&e^{{2 \overline{\phi} \over \alpha}t} \left[x(0)+{{\int}_{0}^{t}} e{-{2 \overline{\phi} \over \alpha} s}E(s)ds \right]. \end{array} $$
(22)

And the short-run dynamics based on the terminal condition are

$$ \left\{ \begin{array}{l} \displaystyle \phi(t) = \left\{ \begin{array}{l} \displaystyle {r\alpha\over 3}+B- {2B \over C_{m} e^{3Bt\over \alpha}+1} , \;\text{if} \;S_{x}(x^{*}(T)) \not= {r\alpha\over 3}-B, \\[.2in] \displaystyle {r\alpha\over 3}-B (=\overline{\lambda} ),\;\text{if} \; S_{x}(x^{*}(T))={r\alpha\over 3}-B, \end{array} \right.\\[.35in] \displaystyle x_{o}(t) = \displaystyle e^{{{\int}_{0}^{t}} {2\phi(s)\over \alpha}ds}\left[ x(0)\,+\, {{\int}_{0}^{t}} e^{-{\int}_{0}^{\tau{2 \phi(s) \over \alpha} }ds}E(\tau)d\tau\right], \;\;\overline{T}=T<\infty, \end{array} \right. $$
(23)

with \( \displaystyle C_{m}= {B+\left [S_{x}(x^{*}(T))-{r\alpha \over 3}\right ] \over B- \left [S_{x}(x^{*}(T))-{r\alpha \over 3}\right ]}\;e^{-{3B\over \alpha }T}\) and \(B=\sqrt { \left (r\alpha \over 3\right )^{2} +{2\alpha \over 3}} \).

That finishes the proof.

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Bertinelli, L., Marchiori, L., Tabakovic, A. et al. The Impact of Unilateral Commitment on Transboundary Pollution. Environ Model Assess 23, 25–37 (2018). https://doi.org/10.1007/s10666-017-9558-2

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