2015
DOI: 10.2139/ssrn.2596609
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Time Scale Externalities and the Management of Renewable Resources

Abstract: The evolution of renewable resources is characterized in many cases by di¤erent time scales where some state variables such as biomass, may evolve relatively faster than other state variables such as carrying capacity. Ignoring this time scale separation means that a slowly changing variable is treated as constant over time. Management rules designed without accounting for time scale separation will result in ine¢ ciencies in resource management. We call this ine¢ ciency time scale externality and we analyze r… Show more

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Cited by 2 publications
(4 citation statements)
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“…In this paper, we contribute to the discussion of optimal resource management under time scale separation by analyzing externalities emerging because of time scale separation and potential inefficiencies of regulation related to harvesting rules, in the context of interacting populations. This extends earlier results of Vardas and Xepapadeas [] to a multispecies renewable resource harvesting model. In particular, we study, by applying the singular perturbation reduction methods (Fenichel []), optimal regulation when emissions cause environmental damages and at the same time cause a slowly varying carrying capacity of the interacting populations, as our first case (case i).…”
Section: Introductionsupporting
confidence: 87%
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“…In this paper, we contribute to the discussion of optimal resource management under time scale separation by analyzing externalities emerging because of time scale separation and potential inefficiencies of regulation related to harvesting rules, in the context of interacting populations. This extends earlier results of Vardas and Xepapadeas [] to a multispecies renewable resource harvesting model. In particular, we study, by applying the singular perturbation reduction methods (Fenichel []), optimal regulation when emissions cause environmental damages and at the same time cause a slowly varying carrying capacity of the interacting populations, as our first case (case i).…”
Section: Introductionsupporting
confidence: 87%
“…The model can be extended to M interacting populations with biomasses xm, m=1,2,..,M. Denoting the interaction coefficients between the μth, νth populations with aμν and the intrinsic growth rates m=1,..,μ,ν,...M with ρm, population dynamics can be written in the general case as: truerightdx=left(ΞH)dtrightdx=left[]dx1..dxM,H=[]h1...hM,hm=j=1Jhmj,m=1,..,MrightΞ=left[]ξ1..ξm..ξM,ξm=ρmxm()1μ=1MamμxμKm(S),rightaitalicmm=left1,μ=1,mμMamμ<1.At this point, we introduce a link between emissions and the evolution of carrying capacity following Vardas and Xepapadeas [] by assuming that the nonfishing sector of the economy generates emissions through production processes. Emissions are generated by a finite number of homogeneous agents i=1,..I, and generate benefits according to a strictly concave benefit function …”
Section: Optimal Regulation When Emissions Cause a Slowly Varying Carmentioning
confidence: 99%
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“…In this section we apply numerical simulations due to the nonlinearity of the hamiltonian system. The following parameterization will be used, following Da-Rocha et al 2014and Vardas & Xepapadeas (2015): a = b = 1 2 , n = 3 or n = 4, p = 10, w = 5, q = 0:045, g = 0:45, K = 7000, r = 0:02. 10 The subjective probability of audition is given by p (x) = 1 (1 x ) , with ( ; ) = (2; 5).…”
Section: Numerical Approximationmentioning
confidence: 99%