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# Stochastic optimization model of aquacultured fish for sale and ecological education

*Journal of Mathematics in Industry*
**volumeÂ 7**, ArticleÂ number:Â 8 (2017)

## Abstract

A stochastic optimization model for management of aquacultured fish for sale and ecological education is established. Population dynamics of the fish is described with a system of stochastic differential equations assuming that they are stochastically harvested after an opening time: the variable to be optimized. A remarkable difference between the present and conventional models for the aquaculture is that the former considers the harvesting for ecological education, which is a key for current inland fishery especially in Japan. Finding the cost-effective optimal opening time effectively reduces to solving an algebraic equation. Mathematical analysis on the optimal opening time clearly reveals its unique existence and qualitative behavior, such as its dependence on the model parameters, which have practical implications. A demonstrative application example of the model is also presented focusing on an aquaculture of *Plecoglossus altivelis* in Japan.

## 1 Introduction

Aquaculture is one of the most profitable fisheries sectors that conventionally farms, harvests, and sells fishery resources [1]. Cost-effective and sustainable management strategies for aquaculture have been studied from both scientific and engineering viewpoints. Clarke et al. [2] reviewed fish vaccine development using plant genetic engineering techniques for sustainable aquaculture. Mazid et al. [3] investigated cost-effective feeding strategy for aquacultured fish using locally available ingredients.

Population dynamics models can efficiently simulate behavior and dynamics of aquatic organisms [4â€“6]. For modeling the dynamics related to aquaculture, stochastic models turned out to be able to compute cost-effective, environmentally- and/or ecologically-sound management strategies of fishery resources under a variety of conditions [7â€“11]. Stochastic differential equations (SDEs) [12] have served as one of the most important tools for optimization problems in aquaculture because of their power to effectively handle population dynamics subject to uncertainties. NÃ¸stbakken [13] numerically computed optimal management rules of aquaculture systems subject to regime-switching stochastic stocks and prices of farmed fishes. Reed and Clarke [14] derived optimal harvesting and pricing rules for aquacultured fishes with the stochastic and size-dependent growth rate. LeÃ³n-Santana et al. [15] analytically derived formulae to achieve environmentally-sound aquaculture based on linear SDEs.

Inland fishery resources, many of which are aquacultured, have long been of central importance as food sources of humans [16, 17]. Currently, establishment of adequate management policies for aquacultured fishes is an urgent issue for inland Fisheries Cooperatives (FCs) because of their severe financial and operational difficulties, which are considered due to decrease of the fish catches and aging of officers. Recently, the authors proposed deterministic [18] and stochastic [19] optimization models to achieve cost-effective management of artificial aquaculture systems (pools). Their models can find the optimal opening (stopping) time [20], which gives the most cost-effective management strategy of aquacultured fishes. The models, however, lack one important factor in the aquaculture of inland fishery resources that some FCs have to manage harvesting not for sale. The most important purpose of the harvesting not for sale is the ecological education [21, 22]. Actually, each FC in Japan has a duty of ecological and environmental conservation and education around the river where it authorizes [23]. Some FCs in Japan harvest aquacultured fishes for the exchange meetings of ecological education where local residents and their children learn about and enjoy ecology and environment of neighboring rivers [24]. For example, the harvested fishes are used for catching competition of the fishes by the children of local residents in exchange meetings (FigureÂ 1). Through the ecological education, FCs teach about the fishes they farm and aquatic organisms living in their river. Throughout communications between the authors and an FC in Japan during 2016-2017, we found that the effect of ecological education should be considered in optimization models of aquacultured fishes of FCs in Japan, in which fishes are harvested for both sale and ecological education. Furthermore, we also found that FCs consider that the ecological education can be a critical factor to continue inland fishery sustainably. However, to the authorsâ€™ knowledge, such mathematical modelling of an aquaculture considering the harvesting not for sale, despite its importance, has not been carried out so far. This is the strong motivation for writing this paper.

The purpose of this paper is to develop a new, tractable stochastic process model for aquaculture considering the harvesting not for sale, which can be utilized for decision-making of the cost-effective and ecologically conscious aquaculture. Stochastic population dynamics in an artificial aquaculture system is described with a system of SDEs that govern the total number of the population and its representative weight. The opening time of harvesting is set as the variable to be optimized. The decision-maker in our optimization problem is the manager of an FC. The opening time is optimized by the manager so that the performance index, which is a net profit by the aquaculture, is maximized. The main difference between the present and conventional models [18, 25â€“27] is that fishes are harvested not only for sale but also for ecological education to local residents. This effect is incorporated into both the population dynamics model and the performance index. Mathematical analysis on the optimal opening time is carried out and its results are verified with numerical computation focusing on *Plecoglossus altivelis*, which is one of the most important inland fishery resources in Japan, managed by Hii River Fisheries Cooperative (HRFC). This paper is the first attempt to model aquaculture considering harvesting for ecological education.

The rest of the paper is organized as follows. SectionÂ 2 presents the mathematical model for cost-effective management of aquacultured fishes without reproduction. SectionÂ 3 presents mathematical analysis results on the model. SectionÂ 4 performs numerical computation to verify the mathematical analysis results with an application to *Plecoglossus altivelis* (Ayu), which is an important inland fishery resource in Japan. SectionÂ 5 concludes this paper and presents future perspectives of our research.

## 2 Methods: mathematical model

The population dynamics model in this paper is not significantly different from the conventional ones [18] except for that it is driven by Poisson noises. On the other hand, the performance index to be maximized, which has a term on profit by harvesting the fish for ecological education, distinguishes the present model from the conventional ones. Hereafter, \(a \wedge b\) for \(a, b \in \mathbb{R}\) represents the smaller value between *a* and *b*.

### 2.1 Governing equations

The time is denoted as \(t \in [ 0, T ]\) where \(t = 0, T\) are the initial and terminal times of an aquaculture, respectively. The fish is introduced into the system only at \(t = 0\). The population dynamics in an artificial aquaculture system is reasonably considered to be non-renewable [18]. The dynamics is described with the representative (average) weight of individuals \(W_{t} \ge 0\) and the total number of individuals \(N_{t} \ge 0\). The governing equations of \(W_{t}\) and \(N_{t}\) are assumed to be independent with each other. This is a reasonable assumption for realistic aquaculture system operated by well-experienced managers with a controlled, sufficiently large pool. The representative weight \(W_{t}\) monotonically increases throughout the period. On the other hand, the total number of individuals \(N_{t}\) monotonically decreases at the same time. All the stochastic integrals in what follow are defined in the ItÃ´â€™s sense [28].

There is an opening time \(\tau \in [ 0, T ]\) of harvesting after which the population is harvested for sale and for exchange meetings for ecological education between FCs and local residents. The exchange meetings are hosted by FCs for ecological education, so that the residents can learn about their fishes and the contents of their works. At each exchange meeting, several hundred individuals of the aquacultured fishes are used for the catching competition by children of local residents: the main event of the meeting (FigureÂ 1). In addition, several lectures on ecology and biology of aquatic organisms including fishes living in and around rivers, lakes, the seas, and in the aquaculture system are held at each meeting. Selling events during \([ \tau, T )\) is modelled with a Poisson process \(P_{t}^{ ( 1 )}\) with the intensity \(\lambda^{ ( 1 )} > 0\). The total number of potentially harvested individuals for sale, the demand, at the time *t* follows a non-negative continuous-time stationary Markov processÂ \(c_{t}^{ ( 1 )}\). The exchange meetings are held during \([ \tau, T )\), which is also modelled as a Poisson process \(P_{t}^{ ( 2 )}\) with the intensity \(\lambda^{ ( 2 )} > 0\). The total number of potentially harvested individuals for ecological education at the time *t* follows a non-negative continuous-time stationary Markov process \(c_{t}^{ ( 2 )}\). Scheduled date and time of each exchange meeting are usually determined before \(t = 0\), but they are possibly held on different date and time due mainly to climate stochasticity. The mean values of \(c_{t}^{ ( 1 )}\) and \(c_{t}^{ ( 2 )}\) are assumed to exist and are denoted as \(C^{ ( 1 )} > 0\) and \(C^{ ( 2 )} > 0\), respectively. The stochastic processes \(P_{t}^{ ( 1 )}\), \(P_{t}^{ ( 2 )}\), \(c_{t}^{ ( 1 )}\), and \(c_{t}^{ ( 2 )}\) are assumed to be independent with each other. The stochastic population dynamics is considered under usual filtration generated by the processes \(P_{t}^{ ( 1 )}\), \(P_{t}^{ ( 2 )}\), \(c_{t}^{ ( 1 )}\), and \(c_{t}^{ ( 2 )}\) as in the conventional stochastic process models. Mathematical properties and applications of Poisson processes are presented in Ross [29].

The initial conditions of \(W_{t}\) and \(N_{t}\) at the time \(t = 0\) are assumed to be given as non-negative numbers. The governing equation of \(W_{t}\) is given by

with the growth rate *g*. This paper assumes the constant \(g = r > 0\) or the generalized Verhulst model (theta-logistic model) given as [30]

with the intrinsic growth rate \(r > 0\), the maximum body weight \(K > 0\), and the nonlinearity parameter \(\theta > 0\). This model is more realistic than that with \(g = r\) since the latter gives unbounded exponential growth. Setting \(\theta = 1\) in (2) yields the conventional Verhulst model. Behavior of solutions to the generalized Verhulst model and its related models has been investigated in detail [30, 31].

Denote the natural mortality rate of the fish as *R*. The governing equation of \(N_{t}\) is given by the SDE

which is explicitly solved with stochastic integrals (ChapterÂ 15 of [29]) as

where \(\chi_{ \{ t \ge \tau \}}\) is the indicator function such that \(\chi_{ \{ t \ge \tau \}} = 1\) for \(t \ge \tau\) and \(\chi_{ \{ t \ge \tau \}} = 0\) otherwise. Hereafter, \(\mathrm{E} [ \cdot ]\) represents expectation. The mean \(\mathrm{E} [ N_{t} ]\) is calculated as

with \(B = R^{ - 1} ( C^{ ( 1 )}\lambda^{ ( 1 )} + C^{ ( 2 )}\lambda^{ ( 2 )} )\).

### 2.2 Performance index

The performance index that quantifies optimality of each management strategy is established from the viewpoint of the manager of an FC as the decision-maker. The performance index consists of (statistically) known variables and parameters so that the decision-maker can choose a strategy before they start an aquaculture. We then assume that the decision-maker can predict the (mean) extinction time \(T_{\mathrm{ex}}\) of \(\mathrm{E} [ N_{t} ]\):

This assumption is natural under the situation where the decision-maker can empirically predict laws of the stochastic processes \(P_{t}^{ ( 1 )}\), \(P_{t}^{ ( 2 )}\), \(c_{t}^{ ( 1 )}\), and \(c_{t}^{ ( 2 )}\), but not their paths. It is then reasonable to give the performance index, which is net benefit of the FC by the aquaculture, as an expectation of a functional of stochastic processes. The present performance index assumes a situation where the population is stochastically harvested with fluctuating demands.

The present performance index is formulated as an extended, stochastic counterpart of that in Yoshioka and Yaegashi [18]:

where \(\alpha^{ ( 1 )}\), \(\alpha^{ ( 2 )}\), and *Î²* are positive weight parameters *a priori* determined by the manager, and *p* is the cost of farming the fish per unit time. As presented in (7), the performance index consists of the three terms. The first term is the profit by selling the fish during the period \([ \tau, T ]\). The second term is the profit by providing the fish for exchange meetings for ecological education during the period \([ \tau, T ]\). The second term is possibly difficult to financially evaluate. This term indirectly represents the profit by the exchange meetings. Officers of HRFC consider that harvesting the aquacultured fish for ecological education can indirectly lead to conservation of environment and ecology of rivers by local residents, which consequently becomes beneficial for the FC. Finally, the third term is the cost of farming the fish during the whole period \([ 0, T ]\), which involves feeding cost of the fish and cleaning cost of their excrements in the pool, both of which would be larger for larger total biomass \(N_{t}W_{t}\). As described above, \(J_{\tau}\) is not purely monetary one whose weights involve the attitude of the decision-maker. Importance of each term can be modulated by the decision-maker based on his/her consideration that which term is of importance for the FC. Therefore, different FCs would have different values of the weight parameters.

Since \(J_{\tau}\) is a function of the opening time \(\tau \in [ 0, T ]\), and it is continuous with respect to *Ï„*, there exists at least one maximizer \(\tau = \tau^{*}\) of \(J_{\tau}\) such that

### Remark 2.1

In practice, the orders of \(\lambda^{ ( 1 )}\) and \(\lambda^{ ( 2 )}\) are significantly different. As an example of *P. altivelis* farmed by HRFC during 2016, the exchange meetings for ecological education were held at most several times in each month. During the same year, the aquacultured fishes were sold almost every day. Therefore, we infer that \(\lambda^{ ( 1 )} = O ( 10^{0} )\) (1/day) to \(O ( 10^{1} )\) (1/day) and \(\lambda^{ ( 2 )} = O ( 10^{ - 2} )\) (1/day) to \(O ( 10^{ - 1} )\) (1/day). We also infer \(C^{ ( 1 )} = O ( 10^{0} )\) to \(O ( 10^{1} )\) and \(C^{ ( 2 )} = O ( 10^{2} )\) to \(O ( 10^{3} )\) based on interviews from HRFC during 2016.

## 3 Mathematical analysis

Mathematical analysis on existence and uniqueness of the optimal opening time \(\tau^{*}\) is carried out. A primitive stochastic process model is also analyzed in this section. Practical implications of the mathematical analysis results are presented as well, which are verified numerically in the next section.

### 3.1 Primitive model

Theoretical behavior of a primitive population dynamics model is briefly studied in order to get insights on the behavior of the presented model. Let *k* be a fixed natural number. Let \(P_{t}^{ ( n )}\) (\(n = 1, 2,\ldots, k\)) be independent Poisson processes with the intensities of \(\lambda^{ ( n )} > 0\). The amplitude of \(P_{t}^{ ( n )}\) is modulated by the stationary and continuous-time non-negative stochastic process \(c_{t}^{ ( n )}\) having the mean value \(C^{ ( n )}\). The processes \(P_{t}^{ ( n )}\) and \(c_{t}^{ ( n )}\) are assumed to be independent with each other. Consider the primitive model that governs a stochastic process \(M_{t}\):

The SDE is subject to the initial condition \(M_{0}\) at the initial time \(t = 0\).

The SDE (9) can be solved as

Since \(P_{s}^{ ( n )}\) and \(c_{s}^{ ( n )}\) are independent, the mean \(\mathrm{E} [ M_{t} ]\) is calculated as

with

The extinction time \(T_{\mathrm{ex}, 0}\) of \(M_{t}\) is defined as

which is exactly calculated as follows by (11). The extinction time \(T_{\mathrm{ex},0}\) is calculated as

### Remark 3.1

The variance of the process \(M_{t}\) is explicitly expressed for some \(c_{t}^{ ( n )}\), although it has less simpler expression than that of the mean value (11). Assume that each \(c_{t}^{ ( n )}\) follows a Cox-Ingersoll-Ross (CIR) model [32]

subject to the initial condition \(c_{0}^{ ( n )} = C^{ ( n )}\) where \(a^{ ( n )} > 0\) and \(\sigma^{ ( n )} \ge 0\), and \(B_{t}^{ ( n )}\) (\(n = 1, 2,\ldots, k\)) are standard 1-D Brownian motions independent with each other. For a positive initial condition, the process is strictly positive if [33]

which is assumed throughout this paper. The CIR model is a minimal model that has a stationary distribution with exact mean and variance [34, 35]. Assume that the process \(c_{t}^{ ( n )}\) satisfies \(c_{0}^{ ( n )} = C^{ ( n )}\). Then, the mean and variance of \(c_{t}^{ ( n )}\) for \(t > 0\) are \(\mathrm{E} [ c_{t}^{ ( n )} ] = C^{ ( n )}\) and \(\operatorname{Var} [ c_{t}^{ ( n )} ] = \frac{C^{ ( n )} ( \sigma^{ ( n )} )^{2}}{2a^{ ( n )}}\), respectively. Actually, \(c_{0}^{ ( n )} = C^{ ( n )}\) is a possible candidate of the initial condition, but may not be realized in practice. For the sake of simplicity of mathematical analysis, the mean value of the process \(c_{t}^{ ( n )}\), which is weak stationary and has a finite invariant measure, can be approximated by \(C^{ ( n )}\). A similar treatment is applied to the variance of \(c_{t}^{ ( n )}\). This approximation does not significantly affect the numerical analysis results presented later because of the condition \(a^{ ( n )}T \gg 1\) where the influences of the initial condition rapidly decay. By (16), the variance \(\operatorname{Var} [ c_{t}^{ ( n )} ]\) is bounded from above as

The variance of the process \(M_{t}\) is then exactly calculated with the help of the isometry formula for Poisson processes (ChapterÂ 14 of [29]). The exact expression of the variance of \(M_{t}\) is presented in AppendixÂ 1, which is utilized in SectionÂ 4.

### 3.2 Existence and uniqueness of optimal opening time

Existence of the optimal opening time \(\tau^{*}\), which is a maximizer of the performance index \(J_{\tau}\), is mathematically analyzed. Several auxiliary results for analyzing \(\tau^{*}\) are firstly presented. By (14), the extinction time \(T_{\mathrm{ex}} = T_{\mathrm{ex}} ( \tau )\) for \(N_{t}\) is given as follows. The extinction time \(T_{\mathrm{ex}} = T_{\mathrm{ex}} ( \tau )\) for \(N_{t}\) is

A straightforward calculation shows that the first- and second-order derivatives of \(T_{\mathrm{ex}} = T_{\mathrm{ex}} ( \tau )\) with respect to *Ï„* are

and

respectively. Therefore, \(T_{\mathrm{ex}}\) is convex and increasing with respect to *Ï„*. Equation (19) leads to \(T_{\mathrm{ex}} ( \tau ) \ge T_{\mathrm{ex}} ( 0 )\) for \(\tau \ge 0\), showing that \(T_{\mathrm{ex}} ( \tau ) \ge T\) for \(\tau \ge 0\) if \(T_{\mathrm{ex}} ( 0 ) \ge T\). Therefore, \(T_{\mathrm{ex}} \ge T\) if

The inequality (21) means that there are remaining individuals at the terminal time *T* when sufficiently large number of the individuals are introduced into the system.

It is shown below that behavior of the optimal opening time \(\tau^{*}\) is qualitatively different between the exclusive cases \(T_{\mathrm{ex}} \ge T\) and \(T_{\mathrm{ex}} < T\). In both cases, the performance index \(J_{\tau}\) can be rewritten as

with \(\tilde{A} = \lambda^{ ( 1 )}\alpha^{ ( 1 )}C^{ ( 1 )} + \lambda^{ ( 2 )}\alpha^{ ( 2 )}C^{ ( 2 )}\). The first-order of partial derivative of \(J_{\tau}\) with respect to *Ï„* is calculated as (Appendix 2)

for \(T_{\mathrm{ex}} \ge T\). \(\frac{\mathrm{d}J_{\tau}}{\mathrm{d}\tau}\) is calculated as

for \(T_{\mathrm{ex}} < T\). Here,

and

with \(\eta = \frac{\beta pBR}{\tilde{A}}\).

The equation (23) immediately gives the following proposition since \(J_{\tau}\) is monotonically decreasing with respect to *Ï„* when \(T_{\mathrm{ex}} \ge T\). Define the critical opening time \(\tau_{\mathrm{ex}}\) as

The critical opening time \(\tau_{\mathrm{ex}}\) is the unique positive solution to

when the condition (21) does not hold, which certainly exists by (19) and (20). In addition, \(0 < \tau_{\mathrm{ex}} < T\). On the other hand, \(\tau_{\mathrm{ex}} = 0\) if (21). From a mathematical viewpoint, it is important to remark that \(\tau^{*} \le \tau_{\mathrm{ex}}\) when \(T_{\mathrm{ex}} \ge T\), \(J \in C ( [ 0, T \wedge T_{\mathrm{ex}} ] ) \cap C^{2} ( 0, \tau_{\mathrm{ex}} ) \cap C^{2} ( \tau_{\mathrm{ex}}, T \wedge T_{\mathrm{ex}} )\), \(\tau^{*} = 0\) when (21). The condition \(\tau^{*} \le \tau_{\mathrm{ex}}\) when \(T_{\mathrm{ex}} \ge T\) shows that it is optimal to set \(\tau^{*} = 0\) if \(N_{0}\) is too large. Although this is theoretically optimal for such a case, it has not been employed in conventional aquacultures. Therefore, this strategy is not reasonable from the viewpoint of managing fishery resources. We thus assume that the condition (21) is not satisfied in what follows. The mathematical analysis below focus on the case \(T_{\mathrm{ex}} < T\). The possible range of \(\tau^{*}\) is then \([ 0, \tau_{\mathrm{ex}} ]\). In the above-mentioned sense, \(\tau_{\mathrm{ex}}\) is an upper bound of \(\tau^{*}\).

A sufficient condition for \(\tau^{*} > 0\), which is consistent with the actual strategies for managing aquaculture systems by FCs, is presented below. Practical implications of the condition are presented as well.

### Proposition 3.1

\(\tau^{*} > 0\)
*if*

### Proof

\(\tau^{*} > 0\) if \(\frac{\mathrm{d}J_{\tau}}{\mathrm{d}\tau}|_{\tau = 0} > 0\) since \(J_{\tau}\) is continuously differentiable with respect to \(\tau \ge 0\). Substituting (25) and (26) into \(\frac{\mathrm{d}J_{\tau}}{\mathrm{d}\tau} |_{\tau = 0} > 0\) leads to (29) since \(\tilde{A} > 0\).â€ƒâ–¡

Based on PropositionÂ 3.1, the conditions to guarantee \(\tau^{*} > 0\) for several growth models are derived.

### Proposition 3.2

*For*
\(g = r\ ( = \mathrm{const} ) > 0\), *the condition* (29) *is satisfied for sufficiently large*
*r*
*and*
\(\eta^{ - 1}\).

### Proof

The condition (29) is satisfied if its left-hand side is positive and *Î·* is sufficiently small. The latter is always possible because the parameters *p*, *Î²*, \(\alpha^{ ( 1 )}\), and \(\alpha^{ ( 2 )}\) involved in *Î·* do not appear in the left-hand side of (29). Actually, choosing sufficiently small *pÎ²* or sufficiently large \(\tilde{A} = \lambda^{ ( 1 )}\alpha^{ ( 1 )}C^{ ( 1 )} + \lambda^{ ( 2 )}\alpha^{ ( 2 )}C^{ ( 2 )}\) can achieve arbitrary small and positive *Î·*.

Since \(W_{t} = W_{0}\exp ( rt )\) in the present case, the left-hand side of (29) becomes

The right-hand side of (29) becomes

if \(r > R\). The condition (29) is thus satisfied if

which holds true for sufficiently large *r* and \(\eta^{ - 1}\), which completes the proof.â€ƒâ–¡

PropositionÂ 3.2 then leads to the following theorem for the generalized Verhulst model:

which behaves for sufficiently small \(W_{0}K^{ - 1}\) as

### Theorem 3.1

*For the generalized Verhulst model*, *the condition* (29) *is satisfied for sufficiently large*
*r*
*and sufficiently small*
\(W_{0}K^{ - 1}\)
*and*
*Î·*.

### Proof

Following the proof of PropositionÂ 3.2, to prove the proposition, it is sufficient to show that the left-hand side of (29) can be made positive for sufficiently large *r* and sufficiently small \(KW_{0}^{ - 1}\). By (30) and (34), the left-hand side of (29) is evaluated as

On the other hand, the right-hand side of (29) is evaluated as

Therefore, the condition (29) is satisfied if

which holds true for sufficiently large *r* and sufficiently small \(W_{0}K^{ - 1}\) and *Î·*.â€ƒâ–¡

### Remark 3.2

Proposition 3.2 and TheoremÂ 3.1 show that the optimal opening time \(\tau^{*}\) is positive, which is in accordance with the reality, if the aquacultured fishes grow sufficiently fast and large and the demand of harvesting them is sufficiently large. A practical implication of the analysis results on management of aquacultured fish is that the decision-maker should carefully observe their growth. Similar results have been theoretically derived in Yoshioka and Yaegashi [18] using a different population dynamics model based on an optimization approach. This fact implies that there exists an underlying universal principle for cost-effective management of aquacultured fish harvested at a certain rate after an opening time.

Uniqueness results of \(\tau^{*}\) for small *p* are finally presented in this sub-section. Key propositions for the case \(p = 0\), which seem to be not reasonable from a practical viewpoint but actually serve as the basis for dealing with the case with sufficiently small \(p > 0\), are presented below.

### Proposition 3.3

*For*
\(p = 0\), \(g = r\ ( = \mathrm{const} ) > 0\)
*and*
\(r \ne R\), \(\tau^{*} \in [ 0, \tau_{\mathrm{ex}} ]\)
*exists uniquely*.

### Proof

By (24) and \(\eta = 0\),

By (18) and (19), (38) is rewritten as

showing

Therefore, by (23), \(\tau^{*}\) is determined uniquely as

â€ƒâ–¡

### Proposition 3.4

*Assume*
\(p = 0\), *g*
*is given by the generalized Verhulst model* (2) *with*
\(r > R\)
*and*
\(\theta \ge 1\). *Then*, \(\tau^{*} \in [ 0, \tau_{\mathrm{ex}} ]\)
*exists uniquely*.

### Proof

In this case, \(\eta = 0\) as in PropositionÂ 3.3 and

by (18) and (19). In addition,

when \(\tau = \tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\) exists (PropositionÂ A.1 in AppendixÂ 3). Therefore, \(J_{\tau}\) does not have local minimum in \(( 0, \tau_{\mathrm{ex}} )\). This follows that \(\tau^{*} \in [ 0, \tau_{\mathrm{ex}} ]\) is determined uniquely with the help of the classical intermediate value theorem as

where *Ï„Ìƒ* is the unique solution of \(F_{\tau} = 0\).â€ƒâ–¡

Now, an application of the classical implicit function theorem with the smoothness of \(F_{\tau} - \eta G_{\tau}\) with respect to *Ï„* and *p* immediately shows the following unique existence theorem of \(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\) such that \(\frac{\mathrm{d}J_{\tau}}{ \mathrm{d}\tau}\) for small \(p > 0\).

### Theorem 3.2

*Assume* (29). *Then*, *under the assumption of PropositionÂ *
3.4
*where â€˜*
\(p = 0\)
*â€™ is replaced by â€˜sufficiently small*
\(p > 0\)
*â€™*, \(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\)
*exists uniquely*.

TheoremÂ 3.2, although it can effectively characterize \(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\), is possibly not sharp as the numerical computation results demonstrate later.

### 3.3 Comparative statics of the critical and optimal opening times

Comparative statics of the critical opening time \(\tau_{\mathrm{ex}}\) and the optimal opening time \(\tau^{*}\) such that \(0 < \tau^{*} < \tau_{\mathrm{ex}}\), namely their dependences on model parameters, is carried out. The comparative statics of \(\tau_{\mathrm{ex}}\) is firstly carried out. A straightforward calculation shows the following proposition.

### Proposition 3.5

*The critical opening time*
\(\tau_{\mathrm{ex}}\)
*satisfies*

*and*

### Proof

Partially differentiating both-hand sides of the governing equation of \(\tau_{\mathrm{ex}}\), which is

with respect to *R* leads to

which is (45) since \(0 < \tau_{\mathrm{ex}} < T\). Other inequalities are derived in a similar way.â€ƒâ–¡

PropositionÂ 3.5 indicates that the critical opening time \(\tau_{\mathrm{ex}}\) increases as the natural mortality rate of the fish *R*, the mean harvesting rates \(C^{ ( n )}\), or the intensities \(\lambda^{ ( n )}\). On the other hand, \(\tau_{\mathrm{ex}}\) decreases as the initial total number of individuals \(N_{0}\) increases. The results thus indicate that the critical opening time \(\tau_{\mathrm{ex}}\), which is interpreted as an upper bound of the optimal opening time \(\tau^{*}\), is larger (smaller) for relatively sparse (abundant) population in the aquaculture system.

Secondly, comparative statics of \(\tau^{*}\) is carried out. Let *u* be one of the parameters *p*, *Î²*, \(\alpha^{ ( 1 )}\), or \(\alpha^{ ( 2 )}\). Assume the interior solution \(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\). This \(\tau^{*}\) solves

In addition, assuming \(\tau^{*}\) is an optimizer that gives a strict maximum of \(J_{\tau}\) yields the second-order condition of optimality

The following propositions reveal dependence of the above-mentioned \(\tau^{*}\).

### Proposition 3.6

*Assume*
\(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\). *Then*, \(\tau^{*}\)
*satisfies*

### Proof

Partially differentiating both-hand sides of (51) with respect to *u* yields

which is (53).â€ƒâ–¡

PropositionÂ 3.6 leads to the following theorem.

### Theorem 3.3

*Assume*
\(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\). *Then*, \(\tau^{*}\)
*satisfies*

### Proof

Substituting \(\eta = \frac{\beta pBR}{\tilde{A}}\) and (52) into (53) with the positivity of \(G_{\tau}\) leads to (55).â€ƒâ–¡

TheoremÂ 3.3 has significant practical implications to management of aquacultured fish. Larger *p* or *Î²* gives smaller optimal opening time \(\tau^{*}\), meaning that increasing the cost of farming the fishes makes the manager harvest them earlier. This is a consequence of the fact that the cost by farming, which is mainly for feeding the fishes and for cleaning up their excrements decreases as the total number of individuals decreases. On the other hand, larger \(\alpha^{ ( 1 )}\) or \(\alpha^{ ( 2 )}\) gives larger optimal opening time \(\tau^{*}\). This implies that increasing the profit by harvesting the fishes, for sale and for exchange meetings for ecological education, makes the manager harvest them later. The aquacultured fishes are used for catching competition by children of local residents, and utility of the children can be larger with better-grown fishes since they can eat the caught fishes after the competition. Therefore, the dependence of \(\tau^{*}\) on the parameters \(\alpha^{ ( 1 )}\) or \(\alpha^{ ( 2 )}\) is considered to be consistent with the reality. It should be noted that similar comparative statics results have been obtained in the deterministic optimization model for aquacultured fish [18].

### 3.4 Analogy with a model for managing non-renewable released fish

This sub-section shows an analogy between the present model for managing aquacultured fish and that for released fish, *P. altivelis* in particular. The fish has been the major inland fishery resource in Japan for recreational and fishery purposes. *P. altivelis* is an endemic fish in Japan and has an annual life history, which is reviewed in detail in the literature and the references therein [36â€“39]. In Japan, in each spring, FCs release juvenile *P. altivelis* into the rivers that they authorize. Harvesting the fish starts at the coming summer. The harvesting period is closed at the end of the autumn, on which the fishes spawn. The important point is that the released fish is often non-renewable possibly due to genetic and environmental reasons [40].

As a simple model we can hypothesize that the population dynamics of released *P. altivelis* in a river follows the SDEs (1) and (3) where the parameters and variables have different meanings. Under this setting, *R* is the mortality rate of the fish by natural death and predation from waterfowls such as *Phalacrocorax carbo* [41]. The stochastic processes \(P_{t}^{ ( 1 )}\) and \(P_{t}^{ ( 2 )}\) represent the events of harvesting the fish for recreational and fishery purposes, respectively. We assume that the FC wants to choose the opening time of harvesting so that a performance index with the form (7) is maximized. The parameter *p* in this case represents the cost of exterminating the predators; the parameters *R* and *p* may be dependent with each other. The weight parameters *Î²*, \(\alpha^{ ( 1 )}\), and \(\alpha^{ ( 2 )}\) depend on the attitude of the decision-maker as in the presented model for aquaculture. The above discussion implies that the present framework of mathematical modeling can be used not only for aquacultured fishes but also for some of the non-renewable released fishes.

## 4 Results and discussion

The present optimization model is applied to a demonstrative numerical computation of management of aquacultured *P. altivelis*.

### 4.1
*P. altivelis* and HRFC

In each year, farming juveniles of *P. altivelis* in an aquaculture system in Japan starts in spring (early to middle May) and they mature in summer around which harvesting opens (beginning of July). The harvesting ends in the coming autumn (late August to early October). HRFC in Shimane Prefecture, Japan farms *P. altivelis* from May to October in each year. Recently, officers of HRFC measured mean body weight of the individuals in the aquaculture system to track their growth. Both feeding the fish and cleaning up the pool are constantly carried out by the officers. According to the officers of HRFC, aquaculture of *P. altivelis* is one of the most indispensable sources of its income. They are trying to find cost-effective and ecologically sound management strategy of harvesting aquacultured *P. altivelis*.

### 4.2 Parameter identification

The previous research [18, 19] implied that the growth of *P. altivelis* in HRFC is reasonably described with the conventional Verhulst equation

FigureÂ 2 shows the measured and fitted \(W_{t}\) in each growth period from 2012 to 2016. The circles are measured values and the curves are fitted growth curves based on the Verhulst model.

TableÂ 1 summarizes the initial time \(t = 0\). The table also shows the identified values of the parameters \(W_{0}\), *K*, and *r* for each year using a nonlinear least squares method with the \(\mathrm{R}^{2}\) value between the measured and identified \(W_{t}\). The order of the parameters \(W_{0}\), *K*, and *r* are same in each year, while their values are slightly different between different years. FigureÂ 2 and TableÂ 1 show that the growth of aquacultured *P. altivelis* in each year is accurately approximated with the conventional Verhulst model (56). The identified result suggests \(K = O ( 10^{2} )\) (g), \(W_{0} = O ( 10^{0} )\) (g), and \(rT = O ( 10^{0} )\) (-); the last one follows from the discussion below. In what follows the data in 2016 is used in the numerical computation as a demonstrative application of the present model.

The terminal time is set as \(T = 150\) (day) considering current management strategy by HRFC. The optimal opening time \(\tau^{*}\) is computed directly from (51) using the classical Simpsonâ€™s rule. The time increment for integration Î”*Ï„* is set as 0.01 (day). The total number of individuals at the time \(t = 0\) is specified as \(N_{0} = 20\text{,}000\) based on an actual management strategy by HRFC. This \(N_{0}\) has been empirically determined by HRFC considering the size of the pool used for their aquaculture.

The variance \(\operatorname{Var} [ N_{t} ]\), which is an index used for verifying optimal management strategy, is obtained with the formula (69) in AppendixÂ 1 as

for \(t \ge \tau\) and \(\operatorname{Var} [ N_{t} ] = 0\) for \(0 \le t < \tau\) with \(M_{0} = N_{0}\). The standard deviation is then computed as \(\sqrt{\operatorname{Var} [ N_{t} ]}\). The variance \(\operatorname{Var} [ N_{t} ]\) is increasing with respect to each \(\lambda^{ ( n )}\), \(C^{ ( n )}\), and \(\sigma^{ ( n )}\), while it is decreasing with respect to each \(a^{ ( n )}\). Comparing the magnitude of the three terms of \(\operatorname{Var} [ N_{t} ]\) (right-hand side of the formula (69) in AppendixÂ 1) can quantify and qualify uncertainties involved in the management strategy.

Based on the personal communications with the officers of HRFC and their accounting book during 2016, the parameters \(\lambda^{ ( n )}\) and \(C^{ ( n )}\) are set as \(\lambda^{ ( 1 )} = 10\) (1/day), \(\lambda^{ ( 2 )} = 0.05\) (1/day), \(C^{ ( 1 )} = 25\) (kg), \(C^{ ( 2 )} = 1\text{,}000\) (kg), respectively. The parameters \(a^{ ( n )}\) and \(\sigma^{ ( n )}\) are set as \(a^{ ( 1 )} = a^{ ( 2 )} = 1\) (1/day), \(\sigma^{ ( 1 )} = 3\) (1/day), and \(\sigma^{ ( 2 )} = 5\) (1/day). The parameter *p* is set as 0.001 (1/day). The mortality rate *R* is set as 0.001 (1/day) considering the fact that almost 10% of aquacultured *P. altivelis* died during the growth period in 2016. There are three weight parameters \(\alpha^{ ( 1 )}\), \(\alpha^{ ( 2 )}\), and *Î²* in the model. Considering the form of the performance index \(J_{\tau}\), the following relationship is assumed without the loss of generality of analysis:

Therefore, choosing \(\alpha^{ ( 1 )}\) and \(\alpha^{ ( 2 )}\) gives *Î²* as \(\beta = 1 - ( \alpha^{ ( 1 )} + \alpha^{ ( 2 )} )\).

### 4.3 Computational results

FigureÂ 3 plots the optimal opening time \(\tau^{*}\) in the 2-D \(\alpha^{ ( 1 )}\)-\(\alpha^{ ( 2 )}\) parameter space. The grey line in the figure corresponds to \(\tau^{*}\) by HRFC in 2016. In addition, FigureÂ 4 plots the extinction time \(T_{\mathrm{ex}}\) computed with the optimal opening time \(\tau^{*}\) in the 2-D \(\alpha^{ ( 1 )}\)-\(\alpha^{ ( 2 )}\) parameter space. The grey line in the figure corresponds to \(T_{\mathrm{ex}}\) by HRFC in 2016. FigureÂ 3 shows consistency between the computational result and the mathematical analysis result since there exists an area with \(\tau^{*} = 0\) near the origin \(( \alpha^{ ( 1 )}, \alpha^{ ( 2 )} ) = ( 0, 0 )\), at which *Î·* is large and the inequality (21) is not satisfied. FigureÂ 3 also shows that the computational results are consistent with the TheoremÂ 3.2. The computational result suggests unique existence ofÂ \(\tau^{*}\).

### Conjecture 4.1

\(\tau^{*} \in [ 0, T ]\)
*exists uniquely*.

FigureÂ 5 plots \(\mathrm{E} [ N_{t} ]\), \(\mathrm{E} [ N_{t} ] \pm \sqrt{\operatorname{Var} [ N_{t} ]}\), and ten sample paths of \(N_{t}\) assuming the actual value \(\tau^{*} = 52\) (day) of HRFC in 2016 with the time increment for temporal integration 0.01 (day). The Runge-Kutta scheme [42] has been used for generating the sample paths where the transformation of variables \(f_{t} = \sqrt{c_{t}^{ ( n )}}\), so that (15) is transformed to the SDE with the additive noise term

which is easier to numerically handle [33]. The sample paths of FigureÂ 5 well characterize the behavior of \(N_{t}\) that it is monotonically decreasing due to frequent small shocks by harvesting for sale and large and rare shocks for harvesting for ecological education, which is in accordance with the actual situation of HRFC. In the actual management strategy of *P. altivelis* by HRFC, \(T_{\mathrm{ex}}\) in 2016 was 113 (day). The modelled extinction time \(T_{\mathrm{ex}}\) with \(\tau^{*} = 52\) (day) is 113.4 (day), which agrees well with the actual value by HRFC in 2016, implying that the utilized parameter values are reasonable.

Finally, to compare impacts of the two different stochastic harvestings, the following stochastic variables that quantify the profit of the harvestings

are considered. The non-dimensional indexes to evaluate relative variability of the profits are presented as

which are computed with a numerical integration technique based on the standard mid-point rules. The index \(V^{ ( n )}\) measures the fluctuation of the process \(j_{\tau}^{ ( n )}\) relative to its mean value. Therefore, larger \(V^{ ( n )}\) implies relatively larger stochastic fluctuations of \(j^{ ( n )}\). The indexes \(V^{ ( n )}\) are computed for different values of \(\sigma^{ ( n )}\) to evaluate dependence of the profits by harvestings for sale and ecological education on the stochasticity of demands.

FigureÂ 6 plots the numerically computed \(V^{ ( n )}\) for \(0 \le \sigma^{ ( 1 )}, \sigma^{ ( 2 )} \le 10\) (kg^{1/2}/day^{1/2}). FigureÂ 6 shows that the indexes \(V^{ ( n )}\) are larger in the harvesting for ecological education (\(n = 2\)) than in the harvesting for sale (\(n = 1\)). In addition, each \(V^{ ( n )}\) is monotonically increasing with respect to \(\sigma^{ ( n )}\), and variability of \(V^{ ( n )}\) for the range of \(\sigma^{ ( n )}\) examined are larger in the harvesting for selling than in that for ecological education. The computational results show that the harvesting for sale is more robust against the stochastic fluctuation of the demand, implying that it can be a major source of profit of the FC. Nevertheless, the harvesting for ecological education, although it turned out to be less robust with larger \(V^{ ( n )}\), actually should not be abandoned since it has served as an indispensable part of the work of the FC. The computational results in this paper provide useful information for decision-making on management of aquaculture systems subject to the stochasticity.

## 5 Conclusion

The present mathematical model is the first model that can evaluate the influences of the harvesting for ecological education on the aquaculture management. Mathematical and numerical analyses on the optimal opening time were carried out to comprehend its existence, uniqueness, and behavior. The analysis results focusing on *P. altivelis* in Japan demonstrated that the harvesting for ecological education is less robust than that for sale, but should not be abandoned since it has served as one of the most indispensable works of the FC. From the analysis results, we recommend FCs to create a working environment where the harvesting for ecological education can be more efficiently carried out with wider spillover effects. Financial and social supports from local governments would be helpful for FCs to achieve this attempt.

Future research will develop an optimization theory for long-term, multi-year management of aquacultured *P. altivelis*, so that FCs in Japan can find the way to achieve cost-effective management strategy of the fish. In addition, local economic dynamics around the FCs will also be mathematically described, so that the demand of the fishes is more reasonably tracked. Investigations both from theoretical and practical viewpoints are necessary for further advance of fishery science and engineering.

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## Acknowledgements

The River Fund No. 285311020 in charges of The River Foundation, JSPS Research Grant Nos. 15H06417, 17K15345, and WEC Applied Ecology Research Grant No. 2016-02 support this research. The authors thank to Hii River Fishery Cooperatives for providing valuable data.

## Author information

### Authors and Affiliations

### Corresponding author

## Additional information

### Funding

The River Fund No. 285311020 in charges of The River Foundation, JSPS Research Grant Nos. 15H06417, 17K15345, and WEC Applied Ecology Research Grant No. 2016-02 support this research.

### Competing interests

The authors declare that they have no competing interests.

### Authorsâ€™ contributions

HY wrote the paper with the support of YY. HY and YY performed mathematical and numerical analysis, and interviews to officers of Hii River Fisheries Cooperatives. All authors read and approved the final manuscript.

### Authorsâ€™ information

Yuta Yaegashi is Research Fellow of Japan Society for the Promotion of Science.

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## Appendices

### Appendix 1

This appendix presents a calculation procedure of the variance of \(M_{t}\), which is defined as \(\operatorname{Var} [ M_{t} ] = \mathrm{E} [ M_{t}^{2} ] - ( \mathrm{E} [ M_{t} ] )^{2}\). By the martingale property of the compensated Poisson process \(P_{t}^{ ( n )} - \lambda^{ ( n )}t\) (ChapterÂ 15 of [29]) and stationarity of \(c_{t}^{ ( n )}\), \(\mathrm{E} [ M_{t}^{2} ]\) satisfies

By stationarity and independency of \(c_{t}^{ ( n )}\), the second term in the right-hand side of (62) becomes

Then, (62) is rewritten as

Note that

and

Therefore, with (65) through (68), a closed-form expression of the variance \(\operatorname{Var} [ M_{t} ]\) is obtained as

The formula (69) shows that \(\operatorname{Var} [ M_{t} ]\) is increasing with respect to each \(\lambda^{ ( n )}\), \(C^{ ( n )}\), and \(\sigma^{ ( n )}\), while it is decreasing with respect to each \(a^{ ( n )}\).

### Appendix 2

This appendix shows calculation procedures of the first-order derivative of \(J_{\tau}\). A key of the calculation procedures is using the Leibnitzâ€™s rule (Appendix A of [43]). By (5), assuming \(T > T_{\mathrm{ex}}\), differentiating both-hand sides of (22) with respect to *Ï„* yields

Since

combining (70) and (71) yields

which is (23). Similarly, for \(T > T_{\mathrm{ex}}\),

The first term in the right-hand side of (73) is calculated as

By (71), the second term in the right-hand side of (73) is calculated as

since \(\mathrm{E} [ N_{T_{\mathrm{ex}}} ] = 0\). Combining (73), (74), and (75) yields (24).

### Appendix 3

The following proposition used in PropositionÂ 3.4 is proven in this appendix.

### Proposition A.1

*Assume*
\(p = 0\)
*and*
*g*
*is given by the generalized Verhulst model* (2) *with*
\(r > R\)
*and*
\(\theta \ge 1\). *In addition*, *assume*
\(\tau^{*} \in ( 0, \tau_{\mathrm{ex}} )\)
*solves*
\(\frac{\mathrm{d}J_{\tau}}{ \mathrm{d}\tau} = 0\). *Then*, \(\frac{\mathrm{d}^{2}J_{\tau}}{ \mathrm{d}\tau^{2}} < 0\)
*at*
\(\tau = \tau^{*}\).

### Proof

Under the stated assumption, \(\frac{\mathrm{d}^{2}J_{\tau}}{ \mathrm{d}\tau^{2}}\) at \(\tau = \tau^{*}\) is

which can be rewritten with (20) as

Substituting (2) into (77) yields

which with \(\tilde{A} > 0\) proves the proposition.â€ƒâ–¡

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Yoshioka, H., Yaegashi, Y. Stochastic optimization model of aquacultured fish for sale and ecological education.
*J.Math.Industry* **7**, 8 (2017). https://doi.org/10.1186/s13362-017-0038-8

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DOI: https://doi.org/10.1186/s13362-017-0038-8