Abstract
Uncertainties inherent in fisheries motivate a precautionary approach to management, meaning an approach specifically intended to avoid bad outcomes. Stochastic dynamic optimization models, which have been in the fisheries literature for decades, provide a framework for decision making when uncertain outcomes have known probabilities. However, most such models incorporate population dynamics models for which the parameters are assumed known. In this paper, we apply a robust optimization approach to capture a form of uncertainty nearly universal in fisheries, uncertainty regarding the values of model parameters. Our approach, developed by Nilim and El Ghaoui (Oper Res 53(5):780–798, 2005), establishes bounds on parameter values based on the available data and the degree of precaution that the decision maker chooses. To demonstrate the applicability of the method to fisheries management problems, we use a simple example, the Skeena River sockeye salmon fishery. We show that robust optimization offers a structured and computationally tractable approach to formulating precautionary harvest policies. Moreover, as better information about the resource becomes available, less conservative management is possible without reducing the level of precaution.
Similar content being viewed by others
Notes
The likelihood ratio is only distributed according to (3) for asymptotically large sample sizes. Nonetheless, NEG argue that it can “serve as a guideline” (p. 797).
They also show a finite horizon problems can be solved in an analogous fashion.
We also acknowledge data provided directly to us by Ray Hilborn, which allowed us to improve the precision of our data that were extracted from the figure in Hilborn and Waters (1992).
This differs from the objective function used by Walters (1975) who sought to minimize the variance of the harvest around a predetermined mean.
Where data are available to estimate these parameters, the robust optimization approach could be extended directly. For other cases (e.g., discount factor or preferences), sensitivity analysis may be required.
Such bounds on the state space are a necessary limitation in numerical solution methods. In some cases, positive lower bounds on the stock are appropriate given the biophysical characteristics of the system. However, if extirpation is a realistic threat, then the model should be adapted to incorporate this concern, possibly by placing a large penalty if this occurs so that optimal policies avoid this state.
The simulation analysis treats the data as observations used to estimate the true distribution. Accordingly, each of the 25 simulations uses a randomly drawn probability distribution, but checked to make sure that it falls within the 90 % likelihood bounds defined by the Walters’ data. Then, in each of the 200 periods, a value for α is drawn from that distribution. For each UL level, a common seed is used so that the series of values for α are identical.
Note that the respective constraint, \(p^{T} {\mathbf{1}} = 1\), will always bind, so μ > 0.
In practice, we use the MATLAB function fminbnd to solve this problem. All computer code used in this paper will be made available as supplementary content via the journal’s Web page.
References
Anderies JM, Rodriguez AA, Janssen MA, Cifdaloz O (2007) Panaceas, uncertainty, and the robust control framework in sustainability science. Proc Natl Acad of Sci 104(39):15194–15199
Andersen P, Sutinen JG (1984) Stochastic bioeconomics: a review of basic methods and results. Mar Res Econ 1(2):117–136
Ascough JC II, Maier HR, Ravalico JK, Strudley MW (2008) Future research challenges for incorporation of uncertainty in environmental and ecological decision-making. Ecol Model 219:383–399
Bewley TF (2011) Knightian decision theory and econometric inferences. J Econ Theory 146(3):1134–1147
Cai Y, Huang GH, Nie XH, Li YP, Tan Q (2007) Municipal solid waste management under uncertainty: a mixed interval parameter fuzzy-stochastic robust programming approach. Environ Eng Sci 24(3):338–352
Chen C, Huang GH, Li YP, Zhou Y (2013) A robust risk analysis method for water resources allocation under uncertainty. Stoch Environ Res Risk Assess 27(3):713–723
Ciriacy-Wantrup SV (1952) Resource conservation: economics and policies. University of California Press, Berkeley
Doole G, Kingwell R (2010) Robust mathematical programming for natural resource modeling under parametric uncertainty. Nat Res Model 23(3):285–302
Doyen L, Béné C (2003) Sustainability of fisheries through marine reserves: a robust modeling analysis. J Environ Manag 69(1):1–13
Ellsberg D (1961) Risk, ambiguity and savage axioms. Q J Econ 75(4):643–679
FAO (1996) Precautionary approach to fisheries management, part 1: guidelines on the precautionary approach to capture fisheries and species introductions. Lysekil, Sweden, June 6–13. FAO Fisheries Technical Paper, No. 350, Part 1. Rome
Gaivoronski AA, Sechi GM, Zuddas P (2012) Balancing cost-risk in management optimization of water resource systems under uncertainty. Phys Chem Earth 42:98–107
Gilboa I, Schmeidler D (1989) Maxmin expected utility with non-unique prior. J Math Econ 18(2):141–153
Gilboa I, Postlewaite AW, Schmeidler D (2008) Probability and uncertainty in economic modeling. J Econ Perspect 22(3):173–188
Gollier C, Jullien B, Treich N (2000) Scientific progress and irreversibility: an economic interpretation of the ‘precautionary principle’. J Public Econ 75(2):229–253
Hansen LP, Sargent TJ (2001) Robust control and model uncertainty. Am Econ Rev 91(2):60–66
Hansen LP, Sargent TJ (2007) Robustness. Princeton University Press, Princeton, NJ
Hansen LP, Sargent TJ, Turmuhambetova G, Williams N (2006) Robust control and model misspecification. J Econ Theory 128(1):45–90
Hanson FB, Ryan D (1998) Optimal harvesting with both population and price dynamics. Math Biosci 148(2):129–146
Hilborn R, Walters CJ (1992) Quantitative fisheries stock assessment: choice, dynamics and uncertainty. Chapman and Hall, London
Jin D, Herrera GE (2010) A stochastic bioeconomic model with research. Mar Res Econ 20(3):249–261
Johnson FA (2011) Learning and adaptation in the management of waterfowl harvests. J Environ Manag 92(5):1385–1394
Lempert RJ, Collins MT (2007) Managing the risk of uncertain threshold responses: comparison of robust, optimum, and precautionary approaches. Risk Anal 27(4):1009–1026
Manski CF (2011) Policy analysis with incredible certitude. Econ J 121(554):F261–F289
McAllister M, Kirchner C (2002) Accounting for structural uncertainty to facilitate precautionary fishery management: illustration with Namibian orange roughly. Bull Mar Sci 70(2):499–540
McCarthy MA, Possingham HP (2007) Active adaptive management for conservation. Conserv Biol 21(4):956–963
Nilim A, El Ghaoui L (2005) Robust control of Markov decision processes with uncertain transition matrices. Oper Res 53(5):780–798
Punt AE (2006) The FAO precautionary approach after almost 10 years: have we progressed towards implementing simulation-tested feedback-control management systems for fisheries management? Nat Res Model 19(4):441–464
Randall A (2011) Risk and precaution. Cambridge University Press, New York
Regan HM, Ben-Haim Y, Langford B, Wilson WG, Lundberg P, Andelman SJ, Burgman MA (2005) Robust decision-making under severe uncertainty for conservation management. Ecol Appl 15(4):1471–1477
Ricker WE (1954) Stock and recruitment. J Fish Res Board Can 11:559–623
Rodriguez AA, Cifdaloz O, Anderies JM, Janssen MA, Dickeson J (2011) Confronting management challenges in highly uncertain natural resource systems: a robustness–vulnerability trade-off approach. Environ Model Assess 16(1):15–36
Roseta-Palma C, Xepapadeas A (2004) Robust control in water management. J Risk Uncertain 29(1):21–34
Savage LJ (1954) The foundations of statistics. Wiley, New York
Sethi G et al (2005) Fishery management under multiple uncertainty. J Environ Econ Manag 50(2):300–318
Shaw WD, Woodward RT (2008) Why environmental and resource economists should care about non-expected utility models. Res Energy Econ 30(1):66–89
Tyre AJ, Michaels S (2011) Confronting socially generated uncertainty in adaptive management. J Environ Manag 92(5):1365–1370
Vardas G, Xepapadeas A (2010) Model uncertainty, ambiguity and the precautionary principle: implications for biodiversity management. J Environ Res Econ 45(3):379–404
Wald A (1950) Statistical decision functions. Wiley, New York
Walters C (1975) Optimal harvest strategies for salmon in relation to environmental variability and uncertain production parameters. J Fish Res Board Can 32(10):1777–1785
Williams BK (1996) Adaptive optimization and the harvest of biological populations. Math Biosci 136(1):1–20
Williams BK (2011) Adaptive management of natural resources—framework and issues. J Environ Manag 92(5):1346–1353
Woodward RT, Shaw WD (2008) Allocating resources in an uncertain world: water management and endangered species. Am J Agric Econ 90(3):593–605
Xepapadeas A, Roseta-Palma C (2003) Instabilities and robust control in fisheries. Discussion paper, Department of Economics, University of Crete, Greece
Acknowledgments
This research was conducted with support from Maryland Sea Grant under award R/FISH/EC-103 from the National Oceanic and Atmospheric Administration, US Department of Commerce, and Texas AgriLife Research with support from the Cooperative State Research, Education & Extension Service, Hatch Project TEX8604. We acknowledge the help of Ray Hilborn who provided some of the data used in the empirical application, Michele Zinn for editorial assistance, and reviewers for many helpful comments.
Author information
Authors and Affiliations
Corresponding author
Electronic supplementary material
Below is the link to the electronic supplementary material.
Appendix: Detailed Explanation of Solution Algorithm
Appendix: Detailed Explanation of Solution Algorithm
Nilim and El Ghaoui use the one-to-one mapping between the likelihood function and the approximate probability level to specify their robust optimization problem. Hence, rather than using the likelihood ratio directly, they use the corresponding value of a parameter, β, which is defined such that for a given value of α, \(\Pr \left( {p_{i}^{a} } \right) \ge \alpha \Leftrightarrow \ln \left( {L\left( {p_{i}^{a} } \right)} \right) \ge \beta\) with \(p_{ij}^{a} \ge 0{\text{ and }}\sum\nolimits_{j} {p_{ij}^{a} = 1}\).
The Lagrangian of the inner problem, (4), can be written as
where we suppress the subscript i and the superscript a so that V, k, and p refer to vectors. There is a separate Lagrangian of this form for each action, a, and starting point in the state space, i = 1,…,n. The Lagrange multipliers are \(\zeta\), the shadow price on the inequality constraints; \(\mu\), the multiplier on the constraint requiring that the probabilities sum to one; and \(\lambda\), the multiplier on the constraint that defines the bounds.
Using the first-order condition of (8) with respect to p j gives
Because of the log function, p j > 0 so \(\zeta_{j} = 0\) for all j, leaving only two unknown parameters, λ and μ.
Nilim and El Ghaoui solve for λ and μ by first replacing p j in the Lagrangian (8) using (9),
This can be simplified as follows:
Letting \(K = \sum\nolimits_{j} {k_{j} }\), this becomes
Since the objective of the inner problem is to minimize over p, the solution of the optimization problem is found by maximizing (10) over the shadow prices. Taking the first-order conditions with respect to μ and setting equal to zero,Footnote 8 we obtain
Since (11) can be substituted into (10), each inner problem can be reduced to finding a single parameter, μ, after which all other parameters can be found algebraically. As long as \(V\left( {x_{i} } \right) \ne V\left( {x_{j} } \right)\) for at least one pair, i, j, the inner problem’s solution will occur along the edge of the allowed likelihood range as defined by (3). At the optimal value of μ, (3) holds with an equality or \(\ln \left( {L\left( {p_{i}^{a} } \right)} \right) = \beta\). While NEG propose a bisection algorithm to find μ, in our experience, the log likelihood function is monotonic in μ, meaning that a simple root-finding algorithm (Newton’s method) will quickly and accurately find the correct value for μ.Footnote 9
Rights and permissions
About this article
Cite this article
Woodward, R.T., Tomberlin, D. Practical Precautionary Resource Management Using Robust Optimization. Environmental Management 54, 828–839 (2014). https://doi.org/10.1007/s00267-014-0348-1
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s00267-014-0348-1