Abstract
We present an extended integrated assessment model (IAM) that optimizes climate financing policies over multiple phases of discrete policy action. We build on Semmler et al. (Control systems and mathematical methods in economics. Springer, 2018) which develops a single-phase model of the optimal allocation of infrastructure expenditure to carbon-neutral physical capital, climate change adaptation, and emissions mitigation. That model is solved by discretizing the optimal control problem and applying large-scale optimization techniques. A new algorithm, the arc parameterization method (APM), allows us to extend the model to multiple regimes, operationalized through a 3-phase policy environment. The first policy regime is defined by a limited set of policy tools. In the second regime, green bonds (i.e. climate-focused financing) are introduced, and in the final regime, green bonds are repaid with a new tax. We demonstrate that this multi-phase model incorporating climate, fiscal and financial policies is superior to single-phase models.
This paper was developed while Willi Semmler was a visiting scholar at the IIASA in July and August 2016. He would like to thank the IIASA for its hospitality. A related version of this paper was worked out while Willi Semmler was a visiting scholar at the IMF Research Department in April 2016. The authors would like to thank Prakash Loungani and his colleagues for many helpful insights.
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Notes
- 1.
See Bonen et al. [2] for a further discussion.
- 2.
All variables are in per capita terms.
- 3.
The exponent \(\beta \) is the output elasticity of public infrastructure, \(\nu _{1}g\).
- 4.
Use of R emits carbon dioxide increasing M at the rate \(\gamma \). The stable level of CO2 emissions is \(\kappa >1\) of the pre-industrial level \(\widetilde{M}\). Some CO2 is absorbed into oceanic reservoirs at the rate \(\mu \).
- 5.
Note that instead of an independent damage function mapping climate change into output reductions, (6.7) treats climate change as a direct welfare loss. Adaptation efforts are modelled in a similarly direct fashion. We adopt this approach because the welfare impacts of climate change are not limited to lost productivity. For example, loss of life will increase from changing disease vectors and more intense heat waves.
- 6.
Under a single-regime setting, Semmler et al. [15] demonstrate incorporating the \(\nu _i\) as controls in U improves welfare outcomes versus treating them as fixed parameters.
- 7.
See Eq. (6.6) and accompanying text. We also want to note the long period of no fossil fuel energy extraction comes from the fact that the carbon stock is presumed to start at a low initial level as well as the low efficiency of the fossil fuel-based energy assumed, i.e. \(A_u=100\) (see Sect. 6.6 below).
- 8.
Of course, the initial values apply only to the starting values in phase 1 and the terminal constraints bind only at \(T=70\), at the end of the third phase.
- 9.
DSGE models have also recently allowed for regime switches (see [12], Sect. 7.2), but not address the issue of discontinuities in the control variables.
- 10.
In addition, when green bonds portend reductions in CO\(_{2}\)-emitting energy sources, their issuance might lead to significant devaluation of assets representing fossil fuels if this is expected to increase the risk of these assets becoming (so-called) “stranded” assets. Formally introducing this effect is left for later work.
- 11.
Note that in the present context the Ricardian equivalence theorem, which says that the real side of the economy will not be affected by deficit spending financed through issuing of bonds, is not applicable in this context. This is because green bonds are used to reduce future damages to GDP, and thus carry some future returns from their investments (in particular from public infrastructure). For details, see Orlov et al. [13].
- 12.
In this context, a recent discussion of proposals for central banks to accept climate bonds as collateralizable securities is available in Flaherty et al. [6].
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Appendix: Multi-phase Optimal Control Problems and Their Numerical Solution
Appendix: Multi-phase Optimal Control Problems and Their Numerical Solution
Multi-process (multi-phase) optimal control problems have been studied by Clarke and Vinter [4, 5] and later by Augustin and Maurer [1]. Suppose that a dynamic economic process on a given time interval [0, T] consists of \((s+1)\) phases (regimes) that switch at the transition times \(t_{k}\in (0,T),\,k=1,...,s\). The switching times are ordered according to
In each interval \([t_{k},t_{k+1}],\,k=0,1,\ldots s,\) the dynamics and objectives may be different.
Let \(x\in \mathbb {R}^{n}\) be the state variable and \(u\in \mathbb {R}^{m}\) the control variable. The dimensions of the state vector and control vector may be different in different phases. For simplicity, we refrain here from discussing this general case and assume the same dimensions in each subinterval. Hence, the dynamics of the economic process in the interval \([t_k,t_{t+1}]\) is given by the ordinary differential equation,
where the right-hand side of the ODE is a \(C^{1}\) function \(f_{k}:\mathbb {R}^{n}\times \mathbb {R}^{m}\rightarrow \mathbb {R}^{n}.\) The time \(t_{k}\) in (6.12) is understood from the right, while the time \(t_{k+1}\) is taken from the left. The initial condition and terminal constraints are given as
We further impose control constraints in each interval,
with \(-\infty \le u_{k,\min }<u_{k,\max }\le +\infty \).
A continuous state trajectory x(t) on the whole interval [0, T] is obtained by imposing the continuity condition
Note that the continuity of the state variables in (6.15) does not automatically ensure the continuity of the control variables; in fact, these can jump, as we demonstrate below, when the system transitions between policy phases are studied. Moreover, we can prescribe interior (transition) conditions for the state variables by
with \(C^{1}\) functions \(\varphi _k : \mathbb {R}^n \rightarrow \mathbb {R}.\)
In each interval one may also have different objectives which are defined by functions \(L_{k}:\mathbb {R}^{n}\times \mathbb {R}^{m}\rightarrow \mathbb {R}^{n},\;k=0,1,\ldots ,s\). Then the optimal multi-phase control problem is defined by the following objective:
subject to the constraints (6.12)–(6.15), and \(r_k > 0\) for \(k = 0, 1, \ldots , s\).
To solve the optimal multi-phase control problem, we implement the arc-parametrization in Maurer et al. [12] in conjunction with discretization and nonlinear programming methods. Although they apply the arc-parametrization method (APM) only to bang-bang control problems, the APM can easily be extended to continuous, multi-phase control problems as follows. Let
denote the arc lengths (or, arc durations) of the multi-process. The time interval \([t_{k},t_{k+1}]\) is mapped onto the fixed interval \([k/(s+1),(k+1)/(s+1)]\) by the linear transformation
where \(a_k = t_k - k \xi _k\) and \(b_{k}=(s+1)\xi _{k}\). Taken together, the complete time interval [0, T] is thereby mapped onto the unit interval [0, 1]. Identifying \(x(\tau )=x(a_{k}+b_{k}\tau )=x(t)\) in the relevant intervals, we obtain the scaled ODE system
for \(\tau \in \left[ \frac{k}{s+1},\frac{k+1}{s+1}\right] \). Note that \(\xi _{k}\) are treated as optimization variables if the transition times \(t_{k}\) are free.
The time transformation leads us to rescale the objective function (6.17) as follows:
and subject to (6.12)–(6.15) and rescaled according to (6.19). For the purposes of exposition, we fix the transition points \(t_k\) to reflect the exogenous (and often sub-optimally protracted) nature of introducing and implementing new policies.
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Semmler, W., Maurer, H., Bonen, T. (2021). Financing Climate Change Policies: A Multi-phase Integrated Assessment Model for Mitigation and Adaptation. In: Haunschmied, J.L., Kovacevic, R.M., Semmler, W., Veliov, V.M. (eds) Dynamic Economic Problems with Regime Switches. Dynamic Modeling and Econometrics in Economics and Finance, vol 25. Springer, Cham. https://doi.org/10.1007/978-3-030-54576-5_6
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