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Coping with Multiple Catastrophic Threats

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Abstract

We study intertemporal policies for dealing with multiple catastrophic threats with endogenous hazards, allowing, inter alia, for gradual mitigation efforts that accumulate to reduce occurrence risks. The long-run properties of the optimal policies are characterized in terms of the key parameters (damage, hazard sensitivity and natural degradation rate) associated with each type of catastrophic threat. Effects of background threats on the optimal response to a potential catastrophe are illustrated numerically.

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Notes

  1. More recent examples can be found in Polasky et al. (2011) and Tsur and Zemel (2014b).

  2. A case in point is the debate between advocates of an early vigorous climate policy (Stern 2007) and those supporting a more gradual approach (Nordhaus 2008).

  3. A similar question has been considered by MP in their extension dealing with partial alleviation.

  4. Note that with an iso-elastic utility, the specifications of modifying either consumption or utility by a constant factor are equivalent. To simplify, we assume that \(\eta =2\) and consider a stationary economy. The analysis extends in a straightforward manner to arbitrary \(\eta >1\) at the cost of somewhat more complicated algebra.

  5. The linear specification in (2.3) is made in the interest of simplicity and can be generalized without affecting the nature of our results. In particular, this specification allows us to avert a certain threat completely by reducing the relevant stock to \(P=0\). This possibility might appear unrealistic for some catastrophes, but can be plausible for others. For example, the risk of outbreak of a deadly disease can be eliminated once a cure or vaccine is discovered via sufficient R&D investments. It is easy to model catastrophes which cannot be averted by adding a constant term to (2.3) or by adjusting the parameters such that fixing the state at \(P=0\) involves an unacceptably low consumption rate.

  6. MP assume that \(\varphi \) is random, allowing for a different realization upon each occurrence. This distinction does not affect the model, when \(\varphi \) is interpreted as the expected value of the random factor, because the objective is specified as the expected welfare under a given policy, the damage enters linearly and the random damage and the time of its occurrence are assumed independent.

  7. A similar result is derived in MP (p. 2955) where equation (7) is analogous to our equation (2.10) above in that both equations require that the discount rate is large relative to the expected damage flow in order to avoid infinitely negative welfare. Indeed, this result is typical of models of recurrent events where discounting must offset the cumulative effect of an infinite series of damages [see Eq. (2.12) below]. The equations differ somewhat due to the zero growth rate and the explicit value \(\eta =2\) assumed in the present work. Observe further that (2.10) provides the steady state value only prior to the first occurrence. After n occurrences, the value is multiplied by \(\varphi ^n\) which diverges in the long run. This feature can be traced to the multiplicative damage postulated by MP and adopted also in the present work for ease of comparison. Alternatively, one can specify an additive damage (as in the recurrent events of Tsur and Zemel 1998, 2016a) and obtain a constant steady state value. This change will modify the algebraic details of the corresponding L-function, but hardly affect the nature of the solution.

  8. Noting (2.4), the expected payoff (2.6) can be expressed as \({\int _0^\infty f(P(t),q(t))e^{-\int _0^t[\rho +h(P(\tau ))]d\tau }dt}\). With \(\rho +h(P(t))\) representing the “effective discount rate,” f(Pq) can be interpreted as the “effective utility”.

  9. As in the case of an isolated catastrophe, f(Pq) is interpreted as the “effective utility” corresponding to the expected payoff (3.5).

  10. This simple assumption can hold for all P only under the linear hazard specification. When the derivative \(h_i'(\cdot )\) depends on the state \(P_i\), the damage parameters are equal only under specific arrangements of the states which yield equal marginal hazards. When the functions \(h_i(\cdot )\) are identical, this corresponds to the symmetric arrangement with all \(P_i\) equal.

References

  • Aronsson T, Backlund K, Löfgren K-G (1998) Nuclear power, externalities and non-standard pigouvian taxes: a dynamic analysis under uncertainty. Environ Resour Econ 11:177–195

    Article  Google Scholar 

  • Cai Y, Lenton TM, Lontzek TS (2016) Risk of multiple interacting tipping points should encourage rapid \(\text{ CO }_2\) emission reduction. Nat Clim Change 6:520–525

    Article  Google Scholar 

  • Clarke HR, Reed WJ (1994) Consumption/pollution tradeoffs in an environment vulnerable to pollution-related catastrophic collapse. J Econ Dyn Control 18:991–1010

    Article  Google Scholar 

  • Cropper ML (1976) Regulating activities with catastrophic environmental effects. J Environ Econ Manag 3:1–15

    Article  Google Scholar 

  • Gjerde J, Grepperud S, Kverndokk S (1999) Optimal climate policy under the possibility of a catastrophe. Resour Energy Econ 21:289–317

    Article  Google Scholar 

  • Kemp MC (1976) How to eat a cake of unknown size. In: Kemp MC (ed) Three topics in the theory of international trade. North-Holland, Amsterdam

    Google Scholar 

  • Lemoine D, Traeger CP (2016) Economics of tipping the climate dominoes. Nat Clim Change 6:514–519

    Article  Google Scholar 

  • Long NV (1975) Resource extraction under the uncertainty about possible nationalization. J Econ Theory 10:42–53

    Article  Google Scholar 

  • Martin IWR, Pindyck RS (2015) Averting catastrophes: The strange economics of Scylla and Charybdis. Am Econ Rev 105:2947–2985

    Article  Google Scholar 

  • Nævdal E (2006) Dynamic optimization in the presence of threshold effects when the location of the threshold is uncertain—with an application to a possible disintegration of the western antarctic ice sheet. J Econ Dyn Control 30:1131–1158

    Article  Google Scholar 

  • Nordhaus WD (2008) A question of balance: weighing the options on global warming policies. Yale University Press, New Haven

    Google Scholar 

  • Polasky S, de Zeeuw A, Wagener F (2011) Optimal management with potential regime shifts. J Environ Econ Manag 62:229–240

    Article  Google Scholar 

  • Reed WJ (1984) The effect of the risk of fire on the optimal rotation of a forest. J Environ Econ Manag 11:180–190

    Article  Google Scholar 

  • Reed WJ (1987) Protecting a forest against fire: optimal protection patterns and harvest policies. Nat Resour Model 2:23–54

    Article  Google Scholar 

  • Reed WJ, Heras HE (1992) The conservation and exploitation of vulnerable resources. Bull Math Biol 54:185–207

    Article  Google Scholar 

  • Stern N (2007) The economics of climate change. Cambridge University Press, Cambridge

    Book  Google Scholar 

  • Tsur Y, Zemel A (1994) Endangered species and natural resource exploitation: extinction vs. coexistence. Nat Resour Model 8:389–413

    Article  Google Scholar 

  • Tsur Y, Zemel A (1995) Uncertainty and irreversibility in groundwater resource management. J Environ Econ Manag 29:149–161

    Article  Google Scholar 

  • Tsur Y, Zemel A (1996) Accounting for global warming risks: resource management under event uncertainty. J Econ Dyn Control 20:1289–1305

    Article  Google Scholar 

  • Tsur Y, Zemel A (1998) Pollution control in an uncertain environment. J Econ Dyn Control 22:967–975

    Article  Google Scholar 

  • Tsur Y, Zemel A (2001) The infinite horizon dynamic optimization problem revisited: a simple method to determine equilibrium states. Eur J Oper Res 131:482–490

    Article  Google Scholar 

  • Tsur Y, Zemel A (2014a) Steady-state properties in a class of dynamic models. J Econ Dyn Control 39:165–177

    Article  Google Scholar 

  • Tsur Y, Zemel A (2014b) Dynamic and stochastic analysis of environmental and natural resources. In: Fischer MM, Nijkamp P (eds) Handbook of regional science. Springer, Berlin, pp 929–949

    Chapter  Google Scholar 

  • Tsur Y, Zemel A (2016a) The management of fragile resources: a long term perspective. Environ Resour Econ 65:639–655

    Article  Google Scholar 

  • Tsur Y, Zemel A (2016b) Policy tradeoffs under risk of abrupt climate change. J Econ Behav Organ 132:46–55

    Article  Google Scholar 

  • Tsur Y, Zemel A (2017) Steady state properties of multi-state economic models. Can J Econ 50(2) (in press)

  • van der Ploeg F (2016) Reacting to multiple tipping points. Nat Clim Change 6:442–443

    Article  Google Scholar 

  • Yin R, Newman D (1996) The effect of catastrophic risk on forest investment decisions. J Environ Econ Manag 31:186–197

    Article  Google Scholar 

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Tsur, Y., Zemel, A. Coping with Multiple Catastrophic Threats. Environ Resource Econ 68, 175–196 (2017). https://doi.org/10.1007/s10640-017-0144-5

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