Abstract
The legislature in many countries requires that short-run risk and long-run risk be considered in making natural resource policy. In this paper, we explore this issue by analyzing how natural resource conservation policy should optimally respond to long-run risks in a resource management framework where the social evaluator has (Duffie and Epstein in Econometrica 60:353–394, 1992; Schroder and Skiadas in J Econ Theory 89:68–126, 1999) continuous-time stochastic recursive preferences. The response of resource conservation policy to long-run risks is reflected into a matrix whose coefficients measure precaution toward short-run risk, long-run risk and covariance risk. Attitudes toward the temporal resolution of risk underly concerns for long-run risks as well as the response of resource conservation policy to future uncertainty. We formally compare the responses of natural resource policy to long-run risks under recursive utility and under time-additive expected utility. A stronger preference for early resolution of uncertainty can prompt a more conservative resource policy as a response to long-run risks. In the very particular case where the social evaluator preferences are represented by a standard time-additive expected utility, long-run risks are not factored in resource conservation policy decisions. Our work also contributes to the so-called Hotelling Puzzle by formally showing that the fundamental Hotelling’s homogeneous resource depletion problem (one without extraction costs, without new discoveries, and without technical progress) can lead to a decreasing shadow price when attitudes toward the temporal resolution of risk are accounted for.
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Notes
In the financial sector, for instance, a growing attention to issues related to natural capital depletion is reflected in the 2012 Natural Capital Declaration (NCD), the 2017 Network of Central Banks and Supervisors for Greening the Financial System (NGFS), and the United Nations Principles for Responsible Investment (UN-PRI). The concept of natural capital defines the global stock of natural resources, including renewable resources such as clean air, water, soil, and living things, or non-renewable resources, such as minerals and fossil fuels (Arrow et al. 2012, 2004; Daily et al. 2000; Dasgupta 1990; Pearce 1988).
For instance, accounting for concerns for long-run risks has provided a reconciliation of the so-called equity premium puzzle with financial theory. See, for instance, Epstein et al. (2014), Bansal (2007), Bansal and Yaron (2004), Sargent (2007), Brown and Kim (2014), Bansal et al. (2010), Bansal and Ochoa (2011), Strzalecki (2013), CóRdoba and Ripoll (2016). In the economics of longevity literature, CóRdoba and Ripoll (2016) analyze how attitudes toward the temporal resolution of uncertainty affect the value of statistical life (VSL) by calibrating a version of a discrete-time recursive utility framework.
See, for instance, Pindyck (1980), Epaulard and Pommeret (2003), Dasgupta and Heal (1974), Howitt et al. (2005), Knapp and Olson (1996), Young and Ryan (1996), Lewis (1977), Sundaresan (1984), Ackerman et al. (2013), Bansal and Ochoa (2011), Peltola and Knapp (2001), Pindyck (2007), Bansal et al. (2016).
To keep matters as simple as possible, we have not admitted a role for technology. However, allowing a role for technology will not change the main insights brought out by this paper.
Thanks to an anonymous reviewer for suggesting this section.
The function N(.) is assumed to be differentiable, linear or concave.
A standard assumption in the aggregate biomass approach to modeling natural resource dynamics in a stochastic setting is that the growth of the resource can be represented as a stochastic Itô differential equation. To keep matters as simple as possible, the volatility does not depend of the size natural resource stock and is assumed to be additive. See Pindyck (1980) for a similar assumption. This specification of the dynamics of uncertainty does not prevent other forms of uncertainty dynamics to be analyzed. The point here is to allow unexpected shocks on the evolution of the natural resource over time.
The Duffie and Epstein (1992) recursive utility is the continuous-time analog of the Epstein and Zin (1989) discrete-time recursive utility (Kraft and Seifried 2014). Using a discrete-time recursive utility would generally make the optimal stochastic dynamic analysis less tractable. The continuous-time approach offers analytical advantages and approximation gets less necessary. As mentioned by Cochrane (2005a), using a continuous-time approach often allows obtaining analytical results that would be unavailable in discrete time.
Allowing the aggregator f(x, V) to satisfy certain continuity-Lipschitz-growth type conditions ensure the existence of the recursive utility (Duffie and Epstein 1992, p. 366).
An alternative way to express the integral Eq. (2) is to view it as the solution of the stochastic differential equation \(dV(t)=-f(x(t),V(t))dt+\sigma _{V}(t)dB(t),\) where \(\sigma _{V}(t)\) is the volatility of the future utility index, given the information available at time t.
For ease of notation, throughout, we shortly use V(t) to refer to V(S(t)), and f(t) to refer to f(x(t), V(t)), unless otherwise stated. The Bellman’s characterization of optimality with a continuous-time recursive utility is shown by Duffie and Epstein (1992, proposition 9). Some general theorems on the existence and the unicity of the solution to the Hamilton–Jacobi–Bellman equation require that the aggregator or both the drift coefficient and the diffusion coefficient of the state variable satisfy certain continuity-Lipschitz-growth types conditions. See, for instance, Duffie and Lions (1992), Schroder and Skiadas (1999).
For the sake of illustration, Fig. 3 in “Appendix 5” displays a numerical computation of the stationary equilibrium of the natural problem resource policy with a Schroder and Skiadas (1999) recursive utility and a nonlinear natural resource stock-growth function. We developed a numerical algorithm (5 pages in length) for computing the stationary equilibrium of the resource problem. The algorithm is available upon request.
In addition, V must satisfy another a transversality, condition of the form
$$\begin{aligned} \lim _{t\rightarrow \infty }V_{S}(t)S(t)=0. \end{aligned}$$Convexity of the intertemporal aggregator in the future utility index expresses a preference for early resolution of uncertainty while concavity of the intertemporal aggregator in the future utility index expresses a preference for late resolution of uncertainty. Later in Sect. 4, we will assume a Schroder and Skiadas (1999) parametric form of the aggregator that simplifies the exposition of this point.
To illustrate the concept of temporal resolution of uncertainty, let us consider the following three options: In the first option, a coin is flipped in each future date. If heads you get a high consumption payoff and if tails a low one. In the second option, a coin is flipped once. If heads you get a high consumption payoff in all future dates and if tails you get a low one in all future dates . In a third option all the coins are tossed at once in the first period, but the timing of the payoffs being the same as in the other two options. A decision maker may not be indifferent about the three options. A decision maker may prefer a late resolution of uncertainty or an early resolution of uncertainty as a result of his/her attitudes toward correlation of payoffs across periods, long-run uncertainty (Duffie and Epstein 1992).
The future utility risk channel embedded in the natural resource policy-making process resembles the “wealth risk” channel mentioned by Sandmo (1970) in financial risk management decisions.
The function trace(A) of a square matrix A is defined to be the sum of its diagonal elements.
Using a different framework, a study by Shogren and Crocker (1992) emphasized the role of endogenous risk inherent in managing environmental and natural resource issues.
Thanks to an anonymous reviewer for emphasizing this point.
The importance of information gathering regarding long-run future trends affecting natural resource dynamics was mentioned by Solow (1974). As concerns over future environmental uncertainty grow, we believe it will become increasingly important to adopt an interdisciplinary approach while incorporating discussions on long-run risks in policy arenas. To give an example, it might be worthwhile revising and broadening the concept of forward-looking information, as defined by SEC (1994) in financial markets, to include endogenous long-run risk factors in environmental and natural resource problems.
Indeed, the derivative of the trace function for the product of two matrices is given by:
$$\begin{aligned} \frac{\partial \, trace\Big ({\mathcal {W}}_{f}(t)\Sigma (t)\Big )}{\partial \Sigma (t)}=transpose ({\mathcal {W}}_{f}(t))={\mathcal {W}}_{f}(t). \end{aligned}$$The transpose of a matrix is a new matrix whose rows are the columns of the original (which makes its columns the rows of the original).
This notion of prudence was first defined by Kimball (1990) as the sensitivity of the optimal choice to risk. The coefficient of absolute prudence of Kimball (1990) is defined as the ratio between the third derivative and the second derivative of the current utility function, while the coefficient of relative prudence is defined as absolute prudence, multiplied by the extraction rate.
When \(\gamma =0\), this aggregator becomes \(f(x,V)=(1+\alpha V)\left[ log(x)-\frac{\beta }{\alpha }log(1+\alpha V)\right]\). The proof of the existence of the Schroder and Skiadas (1999) stochastic recursive utility relies on the theory of backward stochastic differential equations (BSDE).
As already mentioned, the concept of temporal resolution of uncertainty can be intuitively depicted by considering the following three options: In the first option, a coin is flipped in each future date. If heads you get a high consumption payoff and if tails a low one. In the second option, a coin is flipped once. If heads you get a high consumption payoff in all future dates and if tails you get a low one in all future dates . In a third option all the coins are tossed at once in the first period, but the timing of the payoffs being the same as in the other two options. A decision maker may not be indifferent about the three options. A decision maker may prefer a late resolution of uncertainty or an early resolution of uncertainty as a result of his/her attitudes toward correlation of payoffs across periods, long-run uncertainty (Duffie and Epstein 1992).
There is a connection between preferences for the timing of resolution of uncertainty and preferences for information (Skiadas 1998).
The role of the parameter \(\alpha\) in capturing aversion to long-run risks may be connected to the second component of the Swanson (2012, proposition 1) decomposition, which is related to risk aversion toward future utility flows in a stochastic environment with recursive utility.
With a time-additive expected utility, there is a sense that long-run risks are irrelevant to the social evaluator. An intuitive connection can be made with the concept of risk independence defined on multiattributed utility functions by Fishburn (1965), Keeney (1973), Pollak (1973). Broadly this research agenda shows that risk independence implies that the utility function is additive.
More formally, it is assumed that at time t the positive semi-definite matrices \(\Sigma (t)\) and \({\tilde{\Sigma }}(t)\) are equal. In other words, at time t the following equality is satisfied:
$$\begin{aligned} \left( \begin{array}{ccc} \sigma _{x}^{2}(t) &{} \sigma _{xV}(t) \\ &{}\\ \sigma _{xV}(t) &{} \sigma _{V}^{2}(t) \\ \end{array} \right) = \left( \begin{array}{ccc} \sigma _{{\tilde{x}}}^{2}(t) &{} \sigma _{{\tilde{x}}{\tilde{V}}}(t) \\ &{}\\ \sigma _{{\tilde{x}}{\tilde{V}}}(t) &{} \sigma _{{\tilde{V}}}^{2}(t) \\ \end{array} \right) .\end{aligned}$$In addition, the value function V(t) must satisfy a transversality condition of the form
$$\begin{aligned} \lim _{t\rightarrow \infty }e^{-\nu t}E\left( |V(t)|\right) =0, \end{aligned}$$for a suitable constant \(\nu\). See Duffie and Epstein (1992) for details.
Our paper is the first to derive this exact analytical solution to the stochastic resource extraction problem with the Schroder and Skiadas (1999) recursive utility.
While the discount rate and risk preferences are two differently defined concepts, a closer look at the third expression on the right-hand side of Eq. (54) shows that the discount rate does affect the premium for temporal resolution of uncertainty in the shadow pricing of the natural resource. More precisely, increasing the discount rate (\(\beta\)) negatively affects the premium for temporal resolution of uncertainty when \(\alpha >0\), whereas it positively affects the premium for temporal resolution of uncertainty when \(\alpha <0.\)
This result contrasts with most of the theoretical works on non-renewable resources suggesting that the shadow price increases as a resource is depleted. For instance, Pindyck (1980) implicitly assumes indifference to the timing of resolution of uncertainty, implying that under uncertainty the shadow price of the resource (case of zero or linear cost of extraction) would exhibit an increasing trend.
The aggregator would correspond to that of the time-additive expected utility, \(f(x,V)=u(x)-\beta V\), with \(u(x)=\frac{x^{\gamma }}{\gamma }.\)
Under certainty, the Schroder and Skiadas (1999) aggregator reduces to \(f(x,V)=\frac{x^{\gamma }}{\gamma }-\beta V.\)
The set of parameters for which the expected rate of change of the resource shadow price equals zero is not unique. Another example is \(\beta =3\%\), \(\gamma =0.11\), \(\alpha =6.2291\), and \(\sigma =1\). Their corresponding extraction ratio is 0.0077
Our results reinforce the call by Shaw and Woodward (2008) who urged economists working on environmental and resource economics problems to pay attention to alternative models to time-additive expected utility as they have the potential to explain puzzling outcomes. An interesting line of future research would be to explore the role played by attitudes toward the temporal of uncertainty in rationalizing the absence of the basic Hotelling price path observed in cap-trade markets (Aldy and Armitage 2020).
While this paper modeling has focused on natural capital management issues, in future work we plan to extend and adapt a similar approach to investigate long-run risks issues involved in other areas of economics including intergenerational fiscal policy policies under future uncertainty.
In other words, \(\Psi (t)\) is a vector with 2 rows and 1 column.
The algorithm—5 pages in length—is not included here for reasons of conciseness, but is available upon request.
The seminal paper by Barles and Souganidis (1990) uses the concept of viscosity solutions to provide convergence results for numerical approximation of Hamilton–Jacobi–Bellman (HJB) equations.
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Appendices
Appendix
1.1 Deriving Eq. (10)
To derive Eq. (10), differentiate the maximized Hamilton–Jacobi–Bellman equation (7) with respect to S to obtain
Assuming that the optimal extraction policy is represented by a smooth function \(x(t)=h(S(t))\) of the natural resource stock, the right-hand side of Eq. (58) can be computed from (8) as follows:
Plugging Eq. (59) back into Eq. (58) leads to
which can be rewritten as
where the last term on the right hand side vanishes since it contains the first order condition (9).
From Eq. (61), it follows that :
Using the first-order Eq. (9), we may replace \(V_{S}\) by \(f_{x}(x,V)\), to obtain:
Using the Multivariate Itô Lemma, the left-hand side of Eq. (63) can be computed as:
Plugging (64) back into Eq. (63) leads to
It follows that
where
and
Proof of Proposition 4.1
Proof
\((1)\,\rightrightarrows \, (2):\) Assume that at time t, \(\frac{1}{x(t)}\frac{1}{dt}E_{t}dx(t)-\mu (t)\le (\ge ) 0\) for any positive semi-definite matrix \(\Sigma (t).\) Since \(\frac{1}{x(t)}\frac{1}{dt}E_{t}dx(t)-\mu (t)\ge 0 =-\frac{1}{2}trace\Big ({\mathcal {W}}_{f}(t) \Sigma (t)\Big ),\) it follows that
For any given column vector \(\Psi (t)\) of size \(2\times 1\),Footnote 42 assume that the positive semi-definite matrix is of the form \(\Sigma (t)=\Psi (t)\Psi '(t).\) Since \({\mathcal {W}}_{f}(t) \Psi (t)\Psi '(t)=\Psi '(t){\mathcal {W}}_{f}(t)\Psi (t),\) then it follows from (69) that
where the row vector \(\Psi '(t)\), of size \(1\times 2,\) is the transpose of the vector \(\Psi (t).\) The inequalities shown in (70) are satisfied for any \(\Psi (t)\) if and only if the time-t matrix \({\mathcal {W}}_{f}(t)\) is positive semi-definite (negative semi-definite).
\((2)\,\rightrightarrows \,(1)\): The converse is immediate. \(\square\)
Proof of Proposition 4.2
Proof
\((1)\,\rightrightarrows \, (2):\) Assume that \(\left[ \frac{1}{x(t)}\frac{1}{dt}E_{t}dx(t)-\mu _{f}(t)\right] - \left[ \frac{1}{{\tilde{x}}(t)}\frac{1}{dt}E_{t}d{\tilde{x}}(t)-\mu _{g}(t)\right] \le 0\) for any positive semi-definite matrix \(\Sigma (t).\)
Since \(\left[ \frac{1}{x(t)}\frac{1}{dt}E_{t}dx(t)-\mu _{f}(t)\right] - \left[ \frac{1}{{\tilde{x}}(t)}\frac{1}{dt}E_{t}d{\tilde{x}}(t)-\mu _{g}(t)\right] =-\frac{1}{2}trace\Big \{\left[ {\mathcal {W}}_{f}(t)-{\mathcal {W}}_{g}(t)\right] \Sigma (t)\Big \},\) it follows that at time t,
For any column vector \(\Psi (t)\) of size \(2\times 1\), choosing \(\Sigma (t)\) of the form \(\Psi (t)\Psi '(t)\) and pursuing to (71) leads to
where the row vector \(\Psi '(t)\), of size \(1\times 2,\) is the transpose of the vector \(\Psi (t).\)
The inequality (72) holds for any vector \(\Psi (t)\) if and only if the time-t symmetric matrix \({\mathcal {W}}_{f}(t)-{\mathcal {W}}_{g}(t)\) is positive semi-definite. From proposition 4.1, it is readily seen that \({\mathcal {W}}_{f}(t)\) and \({\mathcal {W}}_{g}(t)\) are positive semi-definite.
\((2)\,\rightrightarrows \, (1):\) The converse is immediate. \(\square\)
Derivation of the Closed Form Solution for a Hotelling’s Homogeneous Resource Depletion Problem with Schroder and Skiadas (1999) Recursive Utility
To find a closed-form solution to the Bellman equation, we conjecture that the value function is of the form
for some positive parameter \(\Phi\) to be determined. Substituting the educated guess (73) into (49), it turns out that the optimal extraction policy is given by
Substituting the educated guess (73) into the maximized Bellman equation (50) leads to
It follows that
which gives
Substituting Eqs. (73) and (74) into Eq. (48), the expected rate of change of the shadow price of the resource stock, assuming \(\gamma >0,\) is obtained as:
where the expression of \(\Phi\) is given by Eq. (77).
1.1 The Transversality Condition
Pertaining to (53) and (41), along the optimal path, the stochastic dynamic of the resource stock takes the form
Therefore
Since \(e^{-\nu t} E\left( |V(t)|\right) = e^{-\nu t} E\Big [ (\Phi S(t))^{\gamma (1+\alpha )} \Big ] =e^{-\nu t}\Phi ^{\gamma (1+\alpha )} E\Big [ S(t)^{\gamma (1+\alpha )} \Big ]\), it follows, using Eq. (80), that
Noting that the term \(E\left( e^{ \gamma (1+\alpha )\sigma B(t)}\right)\) is the expected value of a Geometric Brownian Motion, it follows that
Then the transversality condition (see footnote 32) is verified if the exponent in (82) is negative; that is
or
by replacing the term \(|\gamma |^{\frac{1}{\gamma -1}}\Phi ^{\frac{\gamma }{\gamma -1}}\) by its expression obtained from Eq. (77).
Computational Simulation for the Stationary Optimal Policy with a Schroder and Skiadas (1999) Recursive Utility and a Renewable Resource Growing Nonlinearly
For the computational simulation of the stationary optimal policy with Schroder and Skiadas (1999) recursive utility and a renewable resource growing nonlinearly, we have developed an algorithm that combines the Crank and Nicolson (1974) scheme and the numerical techniques by Achdou et al. (2021). The numerical algorithm computes the value function at each step n iteratively as the solution to a system of linear equations, \(L*V^{n+1}=U*V^{n}\), where L and U are large tridiagonal matrices.Footnote 43
The numerical simulations, shown in Fig. 3, suggest that the value function V(S) of the stationary resource problem is concave, and the extraction policy x(S) depends nonlinearly upon the stock.
We use MATLAB to perform the necessary computations. Our numerical algorithm converges after 3768 iterations, as illustrated in Fig. 4.Footnote 44
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Kakeu, J. Concerns for Long-Run Risks and Natural Resource Policy. Environ Resource Econ 84, 1051–1093 (2023). https://doi.org/10.1007/s10640-022-00748-0
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DOI: https://doi.org/10.1007/s10640-022-00748-0
Keywords
- Natural resource policy
- Long-run risk
- Short-run risk
- Continuous-time stochastic recursive utility
- Temporal resolution of uncertainty
- Hotelling Puzzle