Abstract
There is a growing tendency to consider marine reserves as a management and conservation tool. We investigate a spatial bio-economic model to determine fishery profits under conservation efforts. Rather than imposing a marine reserve on our model, we ask, “When and where should a marine reserve be implemented ?” For one-dimensional habitat, we determine conditions under which marine reserves emerge as a part of the optimal policy. Depending upon the size of the habitat, the optimal strategy is either to avoid fishing or to fish at maximum rate. The effect of ocean currents is analyzed through numerical simulations. We find that in the presence of strong currents, a marine reserve may become ineffective. If the currents are at low rate, a marine reserve could emerge as a variable management tool.
Similar content being viewed by others
References
Ami, D., Cartigny, P., & Rapaport, A. (2005). Can marine protected areas enhance both economic and biological situations?. Comptes Rendus Biologies, 328, 357–366.
Agardy, M.I. (1997). Marine protected areas and ocean conservation. San diego CA: Academic Press.
Bensenane, M., Moussaoui, A., & Auger, P. (2013). On the optimal size of marine reserves. Acta Biotheoretica, 61(1), 109–118.
Moussaoui, A., Bensenane, M., Auger, P., & Bah, A. (2015). On the optimal size and number of reserves in a multi-site fishery model. Journal of Biological Systems, 23(1), 1–17.
Bohnsack, J.A. (1996). Maintenance and recovery of reef fishery productivity. In Poulini, N.V.C., & Roberts, C.M. (Eds.) Reef Fisheries (pp. 283–313). London: Chapman and Hall.
Botsford, L.W., & et al. (2009). Connectivity, sustainability and yield:Bringing the gap between conventional fisheries,management and marine protected areas. Reviews in Fisheries, 19, 69–95.
Brochier, T., Auger, P., Thiam, N., Sow, M., Diouf, S., Sloterdijk, H., & Brehmer, P. (2015). Ecological Modelling, 297, 98–106.
Brown, C.J., & et al. (2015). Fisheries and biodiversities benefits of using static versus dynamic models for designing marine reserve networks. Ecosphere, 6(10), 182. 1–14.
Brown, G.M., & Rougharden, J. (1997). A metapopulation model with private property and a common pool. Ecological Economics, 30, 293–299.
Costello, C., & et al. (2010). The value of spatial information in MPA network design. Proceedings of the National Academy of Sciences USA, 107, 18294–18299.
Clark, C.W. (1976). The optimal management of renewable resources. New York: Wiley.
Claudet, J. (2011). Marine Protected Areas: a multidisciplinary approach. Cambridge UK: Cambridge University Press.
Davies, C.R. (1995). Patterns movement of three species of coral reef fishon the Great Barrier Reef. Townsville, Australia: Ph.D.diss.James Cook University of North Queensland.
Ding, W., & Lenhart, S. (2009). Optimal harvesting of a spatially explicit fishery model. Natural Resource Modelling, 22(2), 173–211.
Dugan, J.E., & Davies, G.E. (1993). Introduction to the international symposium on marine harvest refugia. Canadian Journal of Fisheries and Aquatic Sciences, 50, 1991–1992.
Chakraborty, K., & Kar, T.k. (2012). Economic perspective of marine reserves in fisheries a bioeconomic model. Mathematical Biosciences, 240, 212–222.
Dunlop, E.S., Baskett, M.L., Heino, M., & Dieckmann, U. (2009). Propensity of marine reserves to reduce the evolutionary effects of fishing in a migratory species. Evolutionary Applications, 2(3), 371–393.
Gaines, S.D., White, C., Carr, M.H., & Palumbi, S.R. (2010). Designing marine reserves networks for both conservation and fisheries management. PNAS, 107(43), 1886–1893.
Eakin, C.M. (2001). A tale of two ENSO events:Carbonate budgets and the influence of two warming disturbances and intervening varaiability. UVA. island Panama. Bulletin of Marine Sciences, 69, 171–186.
Edgar, G., & et al. (2014). Global conservation outcomes depend on marine protected areas with five key features. Nature, 506, 216—220.
Fogarty, M.J., Bohnsack, J.A., & Dayton, P.K. (2000). Marine reserves and resource management. In Sheppard, C. (Ed.) Seas at the Millenium: An environmental evaluations, (Vol. 3 pp. 375–392): Elsevier.
Halpern, B.S. (2014). Conservation: making marine protected areas work. Nature, 506, 167–168.
Halpern, B.S. (2003). The impact of marine reserves:Do reserves work and does reserve size matter. Ecological Applications, 13(1), supplS117-S137.
Halpern, B.S., Lester, S.E., & Kellner, J.B. (2009). Spillover from marine reserves and the replenishment of fished stocks. Environmental Conservation, 36, 268–276.
Halpern, & et al. (2008). A global map of human impact on a marine ecosystems. Science, 319, 948–952.
Hasting, A., & Botsford, L.W. (2003). comparing designs of marine reserves for fisheries and biodiversity. Ecological Applications, 13, 65–70.
Kellner, J.B., Tetrault, I., Gaines, S.D., & Nisbet, R.M. (2007). Fishing the line near marine reserves in single multispecies fisheries. Ecological Applications, 17, 1039–1054.
Knowler, D., Barbier, E.B., & Strand, I (2001). An open access-Model of fisheries and Nutrient Enrichment in the Black Sea. Marine Resource Economics, 16(3), 195–217.
De Leenheer, P. (2014). Optimal placement of marine protected areas: a trade-off between fisheries goals and conservation efforts. IEEE Transactions on Automatic Control, 6, 59.
Lester, S.E., & et al. (2009). Biological effects within no-take marine reserves: a global synthesis. Marine Ecology Progress Series, 384, 33–46.
Gilbarg, D., & Trudinger, N. (1983). Elliptic Partial Differential Equations, 2nd edn. Berlin: Springer-Verlag.
Gell, F., & Robert, C. (2003). Benefits beyond boundaries: the fishery effect of marine reserves. Trends in Ecology and Evolution, 18, 448–455.
Gruss, A. (2014). Modelling the impact of marine protected areas for mobile exploited fish populations and their fisheries: what we recently learnt and where we should be going. Aquatic Living Resources 12, 27(3-4), 107–133.
Joshi, H., Herrera, G., Lenhart, S., & Neubert, M. (2008). Optimal dynamics harvest of a mobile renewable resource. Natural resource Modelling, 10(40), 322–343.
Kelly, M.R., Xing, Y., & Lenhart, S. (2015). Optimal fish harvesting for a population modeled by a nonlinear parabolic partial differential equations, Natural resource Modelling. to appear.
Kirk, D.F. (1970). Optimal Control Theory. Englewood Cliff NJ: Printice-Hall.
Lubchenco, J., Palumbi, S.R., Gaines, S.D., & Andelman, S. (2003). Plugging a hole in the ocean: the emerging science of marine reserves. Ecological Applications, 13, S3–S7.
Mangel, M. (1998). No-take areas for sustainability of harvested species and conservation invariant for marine reserves. Ecology Letters, 1, 90–97.
Neubert, M.G. (2003). Marine reserves and optimal harvesting. Ecology Letters, 6, 843–849.
Okubo, A. (1980). Diffusion and ecological problems: Mathematical Models. New York: Springer.
O’Reilly, & et al. (2003). Climate change decreases aquatic ecosytem productivity of Lake Tanganyika, Africa. Nature, 424, 766–768.
Roberts, C.M., & et al. (2003). Ecological criteria for evaluating candidate site for marine reserves. Ecological Applications, 13, 199–214.
Pauly, D., Christensen, V., Guénette, S., Pitcher, T.J., Sumaila, U.R., Walters, C.J., Watson, R., & Zeller, D. (2002). Towards sustainability in world fisheries. Nature, 418, 689–95.
Russ, G.R., Alcala, A.C., & Maypa, A.P. (2003). Spillover from marine reserves:The case of Nas.Vlamingii at Apo Island, The Philippine. Marine Ecology Progress Series, 264, 15–20.
Sale, P.F. (2008). Coral Reef Fishes, Dynamics and Diversity in a Complex Ecosystem, 2nd Edn. San Diego Calif.: Academic Press.
Sale, P.F. (1977). Maintenance of high diversity in coral reef fish communities. American Naturalist, 111, 337–359.
Sale, P.F. (1978). Coexistence of coral reef fishes, a lottery for living space. Environmental Biology of Fishes, 3(1), 85–102.
Sanchiro, J.N. (2004). Designing a cost effective marine reserve network: a bioeconomic metapopulation analysis. Marine Resource Economics, 19, 41–65.
Sanchirico, J.N., Malvadkar, U., Hasting, A., & Willen, J.E. (2006). When are no-take zones an economically optimal fishery management strategy? Ecological Applications, 16(5), 1643–1659.
Sanchiro, J.N., & Willen, J.E. (1999). Bioeconomics of spatial exploitation in a patchy environment. Journal of Environmental Economics and Management, 37, 129–150.
Sanchiro, J.N., & Willen, J.E. (2001). A bioeconomic model of marine reserve creation. Journal of Environmental Economics and Management, 42, 257–276.
Smith, H.L. (1995). Monotone Dynamical Systems: An Introduction to the Theory of Competitive and Cooperative Systems Mathematical Surveys and monographs. AMS. vol.41. providence.
Smoller, J. (1994). Shock Waves and Reaction -Diffusion Equations, 2Nd edn. Berlin: Springer-Verlag.
Sontag, E.D., & Theory, Mathematical Control. (1998). Deterministic finite Dimensional Systems. New York: Springer.
Stockhausen, W.T., & Lipscius, R.N. (2001). Single large or several small marine reserves for the Caribbean spiny lobster. Marine and Freshwater Research, 52, 1605–1614.
Tuck, G.N., & Possingham, H.P. (2000). Marine protected areas for spatially structured exploited stocks. Marine Ecology Progress Series, 192, 89–101.
Vellinga, M., & Wood, R.A. (2002). Global climate impacts of a collapse of the atlantic thermohaline circulation. Climate change, 54, 251–267.
White, C., & et al. (2008). Marine reserves effects on fishery profit. Ecology Letters, 11(4), 370–379.
Acknowledgments
The authors are very grateful to the reviewers for their valuable comments.
Author information
Authors and Affiliations
Corresponding author
Appendices
Appendix A: Proof of Theorem 2.1
To this end, we consider the control set
By standard elliptic theory, for every \(E\in L_{\infty }\), problem (M) has a unique positive solution u \(\in W^{2,p}\left ( \left ] 0,L\right [ \right ) \), ∀p>1. Moreover, there exists a positive constant M ∗ = M ∗(L,r,k,μ)>0 such that \(\left \Vert u\right \Vert _{W^{2,p}}\leq M^{\ast };\) see for instance [31] and [53]. Since J(E)≤C, where C is a constant, we can choose a maximizing sequence \(\left \{ E_{n}\right \} \subset F\) such that
For every \(E_{n}\in L_{\infty }\), problem (M) has a unique positive solution u n \(\in W^{2,p}\left ( \left ] 0,L\right [ \right ) \), ∀p>1. Using u n as a test function in (M), we obtain
for some positive constant C. Since \({H_{0}^{1}}\subset L^{2}\), with compact injection, then after passing to a subsequence, there exists u ∗ such that \(u_{n}\rightarrow \) u ∗ strongly in \(L^{2}\left ( \left ] 0,L \right [ \right ) \). Note that \(\left \Vert u_{n}\right \Vert _{W^{2,p}}\leq M^{\ast }\) and from the compact injection \(W^{2,p}\left ( \left ] 0,L\right [ \right ) \subset C^{0}\left ( \left [ 0,L\right ] \right ) \) for p large enough, it follows that \(\left \Vert u^{\ast }\right \Vert _{\infty }\) ≤M ∗. Similarly, since E n is uniformly bounded in L 2, then there exists a subsequence such that \(E_{n}\rightharpoonup \) E ∗, weakly. We need to prove that
The quantity \(J\left ( E_{n}\right ) \) can be written
hence
We deduce that
Appendix B: Proof of Lemma 2.1
We follow [29], by contradiction, assuming, that there exist an interval \([a ; b]\subset [ 0; L]\) such as
This implies that
From the second equation of \(\left ( S\right )\), we obtain
which gives that
Then
Hence,
It means that \(\left ( \lambda _{1},\lambda _{2}\right ) \) is at equilibrium \( \left ( -kp,-p\right ) \) on [a;b].
Consequently,
this constitutes a contradiction with the transversality condition.
We conclude that for each x∈[0;L], \(\lambda _{2}\left ( x\right ) \neq -p\).
Appendix C: Proof of Lemma 3.1
-
(i)
Transversality conditions implies that \(\frac {d\lambda _{2}^{{}}}{dx} \left ( 0\right ) =-\lambda _{1}\left ( 0\right ) \). This gives that
$$\left\{ \begin{array}{c} s_{1}c_{1}+s_{2}c_{2}=-\lambda_{1}\left( 0\right) , \\ c_{1}+c_{2}=\frac{pE_{\max }+Q}{\mu +E_{\max }}. \end{array} \right. $$
It follows that
Therefore, the function
satisfies
Now, it is clear that the transversality condition
will be satisfied if and only if
Note that
with
and
Hence,
Let
then \(\left ( \lambda _{1},\lambda _{2}\right ) \) is the desired solution.
-
(ii)
The stable manifold is a line through P λ with slope \(\frac {1}{ s_{2}}\) and unstable manifold is a line through P λ with slope \( \frac {1}{s_{1}}.\ \)The intercept of stable manifold with λ 1-axis is the point \(-s_{1}\left ( \frac {pE_{\max }+Q}{\mu +E_{\max }}\right )\) . The intercept of unstable manifold with λ 1-axis is the point \(-s_{2}\left ( \frac {pE_{\max }+Q}{\mu +E_{\max }}\right ) .\ \)The region that lies above the stable and unstable manifold is positively invariant. The lowest point of this region is the equilibrium point \( P_{\lambda }=\left ( \lambda _{1}^{\ast },\lambda _{2}^{\ast }\right ) \). It follows that when \(-s_{2}\left ( \frac {pE_{\max }+Q}{\mu +E_{\max }}\right ) \) ≤ λ 1(0)\(\leq -s_{1}\left ( \frac {pE_{\max }+Q}{\mu +E_{\max }}\right ),\) then \(\lambda _{2}(x)\geq \lambda _{2}^{\ast }\), for all \(x\in \left [ 0,L\right ] \). In order to establish the existence of a minimum, we write λ 2 as a function of λ 1, λ 2 = f(λ 1). We do not know the function f, but we can deduce its variation using the adjoint system. For the variation, we have
$$\frac{d\lambda_{2}}{d\lambda_{1}}=\frac{k\lambda_{2}+\lambda_{1}}{ pE_{\max }+Q+\lambda_{2}\left( \mu +E_{\max }\right) }, $$it vanishes on the line
$$\lambda_{2}=\frac{-1}{k}\lambda_{1} $$It is clear that\(\frac {d\lambda _{2}}{d\lambda _{1}}>0\) if \(\lambda _{2}> \frac {-1}{k}\lambda _{1}\) and \(\frac {d\lambda _{2}}{d\lambda _{1}}<0\) if \( \lambda _{2}<\frac {-1}{k}\lambda _{1}\). Moreover,
$$\frac{d^{2}\lambda_{2}}{d{\lambda_{1}^{2}}}=\frac{\left\{ k(k\lambda_{2}+\lambda_{1})\left( pE_{\max }+Q+\lambda_{2}\left( \mu +E_{\max }\right) \right) +\left( pE_{\max }+Q+\lambda_{2}\left( \mu +E_{\max }\right) \right)^{2}-\left( \mu +E_{\max }\right) \left( k\lambda_{2}+\lambda_{1}\right)^{2}\right\} }{\left( pE_{\max }+Q+\lambda_{2}\left( \mu +E_{\max }\right) \right)^{2}}, $$when k λ 2 + λ 1=0, then
$$\frac{d^{2}\lambda_{2}}{d{\lambda_{1}^{2}}}=1>0, $$and the function is convex in a neighborhood of the minimum.
-
(iii)
From the relation
$$\begin{array}{@{}rcl@{}} \lambda_{2}\left( x\right) =&-&\frac{\lambda_{1}\left( 0\right) +s_{2}\left( \frac{pE_{\max }+Q}{\mu +E_{\max }}\right) }{s_{1}-s_{2}}e^{s_{1}x}\\&+&\frac{ \lambda_{1}\left( 0\right) +s_{1}\left( \frac{pE_{\max }+Q}{\mu +E_{\max }} \right) }{s_{1}-s_{2}}e^{s_{2}x}\\&-&\frac{pE_{\max }+Q}{\mu +E_{\max }}, \end{array} $$it follows that
$$\begin{array}{@{}rcl@{}} \frac{\lambda_{2}\left( x\right) }{dx}=&-&\frac{\lambda_{1}\left( 0\right) +s_{2}\left( \frac{pE_{\max }+Q}{\mu +E_{\max }}\right) }{s_{1}-s_{2}} s_{1}e^{s_{1}x}\\&+&\frac{\lambda_{1}\left( 0\right) +s_{1}\left( \frac{ pE_{\max }+Q}{\mu +E_{\max }}\right) }{s_{1}-s_{2}}s_{2}e^{s_{2}x}. \end{array} $$
The minimum is achieved when
This implies that
and
and the minimal value is
Appendix D: Proof of Corollary 4.1
Since the equilibrium \(P_{\lambda }=\left ( \lambda _{1}^{\ast },\lambda _{2}^{\ast }\right ) \) is a saddle point, then \(\lambda _{2}^{\min }>\lambda _{2}^{\ast }\) . From the expression of \(\lambda _{2}^{\ast }\), it is clear that \(\lambda _{2}^{\ast }\) ≥−p. Hence \(\lambda _{2}^{\min }>-p\).
Appendix E: Proof of Corollary 4.2
Let \(\left ( \lambda _{1},\lambda _{2}\right )\) be a solution of(S) satisfying \(\lambda _{2}\left ( 0\right ) =\lambda _{2}\left ( L\right ) =0\) and \(\left ( \omega _{1},\omega _{2}\right ) \) be a solution of (S) with k=0, and satisfying \(\omega _{2}\left ( 0\right ) =\omega _{2}\left ( L\right ) =0\). We obtain that
Then by comparison principle, we deduce that
From theorem 3 and inequality 34, in [29], it follows that there exists a real value L c r i such that if L>L c r i , the solution corresponding to k=0, hits the switching line ω 2=−p for some \( x\in \left [ 0,\frac {L}{2}\right ] \). This implies that \(\lambda _{2}^{\min }<-p\).
Rights and permissions
About this article
Cite this article
Bouguima, S.M., Hellal, M. Marine Reserve Design with Ocean Currents and Multiple Objectives. Environ Model Assess 22, 397–409 (2017). https://doi.org/10.1007/s10666-016-9543-1
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10666-016-9543-1