REGULAR A RTI CLE
Viability Analysis of Multi-fishery
C. Sanogo • S. Ben Miled • N. Raissi
Received: 16 February 2012 / Accepted: 20 February 2012 / Published online: 4 March 2012
� Springer Science+Business Media B.V. 2012
Abstract This work is about the viability domain corresponding to a model of
fisheries management. The dynamic is subject of two constraints. The biological
constraint ensures the stock perennity where as the economic one ensures a mini-
mum income for the fleets. Using the mathematical concept of viability kernel, we
find out a viability domain which simultaneously enables the fleets to exploit the
resource, to ensure a minimum income and stock perennity.
Keywords Fishing management � Viability kernel � Sustainable exploitation
strategy
1 Introduction
According to recent studies (Assessment 2005) exploited renewable resources are
under extreme worldwide pressure. In particular for halieutic resources, three
C. Sanogo
LIRNE, Mathmatics Engineering Team, Ibn Tofail University, Kenitra, Morocco
e-mail: [email protected]
S. Ben Miled
ENIT-LAMSIN, Tunis el Manar University, Tunis, Tunisia
S. Ben Miled (&)
Pasteur Institute of Tunis, 13, place Pasteur, Belvedere, B.P. 74, 1002 Tunis, Tunisia
e-mail: [email protected]
N. Raissi
LAA, Mohamed V University, Rabat, Morocco
e-mail: [email protected]
123
Acta Biotheor (2012) 60:189–207
DOI 10.1007/s10441-012-9153-5
quarters of the worldwide fish stocks are sub-exploited or over-exploited (FAO
2004). Hence, fishing management policies should include some interaction
problems between that involves different stakeholders interest. Stakeholders are
multiple and resource conservation objective seems a priori in opposition with their
objectives profitability.
The question that arises is for which conditions is it possible to keep functioning
several fleets? Clark (1990) considered a model of games dynamic where actors
were two fleets. The model analysis shows that the less efficient fleet is compelled to
leave the fishery. Raissi (2001) mentions a regulator that aimed to protect the
interests of one of the two fleets in activity. Using multilevel optimization the author
has obtained the same conclusion as Clark (1990).
For a sustainable management, it would be relevant to underline the existence of
stakeholders’ common interests: cohabitation and a sustainable activity are incon-
testably the main goal of every actor. We will use in this work the viability theory
approaching this problematic.
Bene et al. (2001) considered a model with one fleet, using the mathematical
concept of viability kernel. Authors reveal situations and management options
which guarantee a perennial system.
Doyen and Pereau (2009) give insights on the complex equilibrium between
coalitions structure and resource stock to avoid bio-economic collapses. Authors
show that the stability of coalition occurs for a high levels of stock, using the game
theory and viability approach. By contrast, for lower levels of resource, the most
efficient user plays the role of a dictator.
Mullon and Freon (2006) have considered a model with several fleets and several
landing markets. The analysis of the model showed that the cohabitation between
the different fleets is possible.
In this work, we consider a model which describes the dynamics of a fish
population exploited by two fleets. Our aim is to find out a viability domain that
ensures the stock sustainability, a minimum income for the fleets and the
cohabitation. From a mathematical point of view, we should determine a set of
initial conditions (stock, fishing efforts) from which admissible and viable strategies
of exploitation are elaborated for different fleets.
The work is organized as follows: In Sect. 2, we describe the dynamics of the
system. Section 3 deal with the identification of viability constraints and the
determination of viability kernel associated to each fleet. The intersection of
viability kernel corresponding to each fleet is determined in Sect. 4. Finally Sect. 5
provides with a general conclusion of our work.
2 Model Description
We consider a model which describes the dynamic of fish population exploited by
two fleets of different characteristics. The dynamic of the population is controlled
by the variation rates of the fishing efforts E1 and E2. Following (Clark 1990), the
dynamic of the resource can be written as follows:
190 C. Sanogo et al.
123
_XðtÞ ¼ FðXðtÞÞ � q1E1ðtÞXðtÞ � q2E2XðtÞ;_E1ðtÞ ¼ u1ðtÞ;_E2ðtÞ ¼ u2ðtÞ;
Xð0Þ ¼ X0; E1ð0Þ ¼ E01; E2ð0Þ ¼ E02:
8>><
>>:
ð1Þ
where X(t) is the exploited stock biomass at time t C 0 and X0 correspond to the
initial biomass, Ei(t) is the fishing effort for fleet i at time t, ui(t) is the variation rate
of the fishing effort Ei(t) at time t. The variation rate of the fishing effort can be
interpreted as an investment rate of fleet i in activity, qi is the catchability coefficient
of fleet i for i [ {1,2}. We suppose, that the natural growth rate of the resource is
represented by a logistic law:
FðXÞ ¼ rX 1� X
K
� �
where K is carrying capacity of the environment.
For the fleet i, i [ {1, 2}, the discount rate di, the fish unit price pi and the unit
cost of fishing effort ci are supposed to be constant and non-negative. The net
benefit generated by the exploitation has the following expression (Jerry and Raissi,
2001), for i [ {1,2}
PðuiÞ ¼Zþ1
0
exp�di t ðpiqiXðtÞ � ciÞEiðtÞ � uið Þdt; ð2Þ
u�i � uiðtÞ� uþi ; u�i \0; uþi [ 0
The maximization problem of profit must be inevitably hierarchically organized
to define the order of the priorities of every fleet.
In their work, Clark (1990) and Raissi (2001) showed that the less efficient fleet
ended up by leaving the fishing activity.
The maximization of the net benefit generated by the exploitation (2) leads
systematically to the exclusion of the less efficient fleet.
To maintain the two fleets in activity, it is necessary to replace the maximization
objective by a set of constraints ensuring a minimal income for each fleet and
maintaining the stock sustainable. In the next paragraph we will analyze the
compatibility of the dynamical system (1) with these new constraints.
3 Viability Analysis
In this section we identify the viability constraints and determine the viability kernel
associated to each fleet. In other words, we determine for every fleet, the set of
initial conditions (stock, efforts) in which viable and sustainable strategies of
exploitation are elaborated.
3.1 Viability Constraints
We study the viability property of (1) in relation to three constraints:
Viability Analysis of Multi-fishery 191
123
1. The first constraint is an ecological one ensuring a minimum stock level,
r1 : Xmin�X�K:
2. The second one is an economic matter ensuring a minimum income Li for
fishermen at each time,
r2 : ðpiqiX � ciÞEi � uþi � Li� 0; with i 2 f1; 2g
this constraint is verified for all ui(t) B ui?.
3. For the third it stems from the technical constraint, the fishing efforts are non-
negatives and constrained by a limited capacity,
r3 : 0�Ei�Emaxi with i 2 f1; 2g:
After that, we should define a set of constraints imposed to fleets and we shall
determine the viability kernel associated to each fleet compared to the following set:
Ki ¼ðX;E1;E2Þ=ðpiqiX � ciÞEi � uþi � Li;
Xmin\X�K; 0�E1�Emax1 ; 0�E2�Emax
2
� �
Where for all i 2 f1; 2g;Ki represents the set of constraints associated to fleet i.First, we will work in dimension two, as if only one fleet is in activity. Then we will
use these results in the dynamical analysis in dimension three by including the second
fleet. Let’s define the projection of Ki; in the phase plane (X, Ei), (i [ {1, 2}),
projðKiÞ ¼ðX;EiÞ=ðpiqiX � ciÞEi � uþi � Li;
Xmin\X�K; 0�Ei�Emaxi
� �
:
Some elementary geometric considerations bring insight to understand the role of
the parameters in the consistency between constraints and controlled dynamics.
Indeed, let us note by Di the curve defined by:
Di ¼ X;ðuþi þ LiÞðpiqiX � ciÞ
� �
=Xmin\X�K
� �
:
This curve describes levels of stock-effort for which the fleet i has a minimal
income Li, with i [ {1,2}. Below, Di the minimal income Li is not guaranteed for
the fleet i.The identification of the viable equilibrium points is an essential stage in the
determination of viability kernel. These viable equilibrium points verify constraints
imposed by the dynamical system. In the following, we denote the set of equilibrium
points in the phase plane (X, Ei), i [ {1, 2} by,
I i ¼ X;r
qi1� X
K
� �� �
=Xmin\X�K
� �
;
If
pi þci
qiK
� �2
[ 4pi
rK
cir
qiþ uþi þ Li
� �
; i 2 f1; 2g; ð3Þ
192 C. Sanogo et al.
123
then the following polynomial admits two positive roots Xi,min* and Xi,max
* ,
� pir
KX�2 þ r pi þ
ci
qiK
� �
X� � cir
qiþ uþi þ Li
� �
ð4Þ
We denote by Ei,min* (resp. Ei,max
* )the corresponding fishing effort of Xi,min* (resp.
Xi,max* ).
If, for all i [ {1, 2},
pi þci
qiK
� �2
�4pi
rK
cir
qiþ uþi þ Li
� �
¼ 0;
then the polynomial (4) admits a positive root X*; we denote also Ei* the fishing
effort corresponding to X* (Fig. 1).
Remark 1 We suppose Xmin sufficiently small and K sufficiently high to ensure
X*, Xi,min* and Xi,max
* i [ {1, 2} viability.
3.2 Viability Kernel of Fleets
The goal of this part is to find out for E2 = 0, the compatibility of controlled
dynamics (1) and the set of constraints projðK1Þ: Also, we will determine in this
case the viability kernel associated to projðK1Þ:Bene et al. (2001) treated the problem in dimension two. We shall reformulate
their result by using the notations introduced before and generalizing it in dimension
three.
To determine the viability kernel of projðK1Þ we should identify first the viable
equilibrium points.
Fig. 1 Projection of Kiði 2 f1; 2gÞ in phase plane (X, Ei) economics and biological parameters valuesused in numerical simulations are from Jerry and Raissi (2001)
Viability Analysis of Multi-fishery 193
123
3.2.1 Viable Equilibrium Points in the Phase Plane (X, E1)
The projection of (1) in phase plane (X, E1) is given by:
_X ¼ FðXÞ � q1E1X_E1 ¼ u1ðtÞ
Xð0Þ ¼ X0; E1ð0Þ ¼ E01:
8<
:ð5Þ
Existence of viable equilibrium points corresponding to (5) are obtained by the
following proposition. Proof of this proposition is left in the ‘‘Appendix 1’’
Proposition 1 Under following conditions:
K [ maxc1
p1q1
;c2
p2q2
� �
ð6Þ
Emaxi � 2ðuþi þ LiÞ
piqiK � ci; i 2 f1; 2g ð7Þ
r� r� ¼ 4p1q21Kðuþ1 þ L1Þ
ðc1 � p1q1KÞ2ð8Þ
Emax1 �E�1;max ð9Þ
and if (3) is fulfilled, then the set of viable equilibrium points correspondingto (5) is given by the segment AB, where
AB ¼ X�;r
q1
1� X�
K
� �� �
maxðXmax1 ;X�1;minÞ�X� �X�1;max
���
� �
and Xmax1 ¼ K 1� q1Emax
1
r
� �is the biomass level when E1 = E1
max.
Remark 2 The condition (6) is equivalent to K piqi [ ci, with i [ {1,2} this is a
condition of fishing activity viability, it indicates that the fleet participates in fishing
activity only if the minimum income is ensured.
The condition (7) indicates that at equilibrium the fishing effort must not exceed
the limit capacity imposed. Otherwise, the fleet is forced to leave fishery.
The conditions (8) and (9) play important roles in the determination of viability
kernel. The first one gives us a minimal intrinsic growth rate r* below which the activity
of fishing is not viable the second reveals to us a minimum threshold of effort E1,max* .
3.2.2 Calculation of Kernel Viability of projðK1Þ
In this paragraph we have to characterize the viability kernel of projðK1Þ noted by
ViabðprojðK1ÞÞ and defined by,
ViabðprojðK1ÞÞ ¼ ðX;E1Þ9u1ð:Þwith u�1 � u1ðtÞ� uþ1 such that the solution
ðXð:Þ;E1ð:ÞÞ of ð5Þ starting at ðX;E1Þ stays in projðK1Þ
����
� �
194 C. Sanogo et al.
123
Proposition 2 Under the same hypotheses in (1) one of the two following casesoccurs:
1. Case 1: if E1max [ E1,min
* , then
ViabðprojðK1ÞÞ ¼ ðX;E1ÞX�1;min�X�K; and ðX;E1Þ
is between the curvesD1 and Y1
����
� �
where Y1 ¼ ðXð:Þ;E1ð:ÞÞis solution of the following Cauchy problem,
_X ¼ �FðXÞ þ q1E1X_E1 ¼ �u�1
X0 ¼ X�1;min; E0 ¼ E�1;min:
8<
:
2. Case 2: if E1max B E1,min
* , then,
ViabðprojðK1ÞÞ ¼ ðX;E1ÞXmax
1 �X�K; if E1�Emax1 and
ðX;E1Þ is above curveD1
����
� �
Proof See ‘‘Appendix 2’’. h
Remark 3 The curve Y1 defines the upper boundary of the viability kernel,
Y1represents the states of the system where it is necessary to change the control and
thus fishing effort in order to prevent the system from leaving the set of the
constraints.
We have made the same work with the fleet 2 by considering that E1 = 0, in the
same way we obtain the following results:
Proposition 3 Under hypotheses (3), (6) and (7) and under the followingconditions:
r� r0� ¼ 4p2q22Kðuþ2 þ L2Þ
ðc2 � p2q2KÞ2
Emax2 �E�2;max
the set of viable equilibrium points is given by:
A0B0 ¼ X�;r
q2
1� X�
K
� �� �
maxðX0max;X�2;minÞ�X�X�2;max
���
� �
and the viability kernel ViabðprojðK2ÞÞ is given by:
1. Case 1: if E2max [ E2,min
* then,
ViabðprojðK2ÞÞ ¼ ðX;E2ÞX�2;min�X�K; and ðX;E2Þ
is between the curvesY2 andD2
����
� �
where Y2 ¼ ðXð:Þ;E2ð:ÞÞ is solution following Cauchy problem,
Viability Analysis of Multi-fishery 195
123
_X ¼ �FðXÞ þ q2E2X_E2 ¼ �u�2
E0 ¼ E�2;min; X0 ¼ X�2;min
8<
:
2. Case 2: if E2max B E2,min
* then
ViabðprojðK2ÞÞ ¼ ðX;E2ÞX�2;min�X�K; if 0\E2�Emax
2 andðX;E2Þ is above curve D2:
����
� �
3.2.3 Viable Equilibrium Points in Space (X, E1, E2)
After having determined the viability kernel of constraint sets K1 and K2 in the
phase planes (X, E1) and (X, E2), it remains to find out the viability kernel
corresponding to each set of constraints in space (X, E1, E2).
In the space (X, E1, E2) the goal is to determine the compatibility of controlled
dynamics (1) and the set of constraints K1: Also, we will determine the viability
kernel of K1: First, we should identify the viable equilibrium points.
To avoid the exclusion of one of the two fleets, it is necessary to compel the
fishing efforts to remain upper a positive quantity and lower than a limited capacity.
For fleet 2 this limit is given by:
E��2 ¼r
q2
1� c1
p1q1K
� �
�
ffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffi
ðuþ1 þ L1Þrp1K
s !
:
As in Sect. 3.1, the identification of viable equilibrium points is a fundamental
stage in the determination of the viability kernel. It involves the determination of the
set of equilibrium points in the space (X, E1, E2):
P ¼ X;1
q1
r 1� X
K
� �
� q2E2
� �
;E2
� �
=Xmin\X�K; 0�E2�Emax2
� �
:
In Sect. 3.1, for E2 = 0 we had the curve D1: In this section for E2 varying from a
minimal value to a maximal one we have a surface defined by:
D1;s ¼ X;ðuþ1 þ L1Þðp1q1X � c1Þ
;E2
� �
=X��1;min�X�K; 0�E2�E��2
� �
:
Below surface D1;s the minimal income Li, i [ {1, 2}, is not guaranteed for
fleets.
Still in the setting of geometric considerations let us define the surfaces Ks and
E1,smax which delimit the set of constraints K1:
Ks ¼ ðK;E1;E2Þ= 0�E1�Emax1 ; 0�E2�Emax
2
�;
Emax1;s :¼ ðX;Emax
1 ;E2Þ=X��1;min�X�K; 0�E2�E��2
n o:
If
196 C. Sanogo et al.
123
p1ðr � q2E�2Þ þc1r
q1K
� �2
[ 4p1r
K
c1
q1
ðr � q2E�2Þ þ ðuþ1 þ L1Þ� �
; ð10Þ
then the following polynomial
� p1r
KX�2 þ p1ðr � q2E�2Þ þ
c1r
q1K
� �
X� � c1
q1
ðr � q2E�2Þ þ ðuþ1 þ L1Þ� �
ð11Þ
two positive roots:
X��1;min ¼K
2rp1
p1ðr � q2E�2Þ þc1r
q1K
� �
�ffiffiffiffiDp� �
and
X��1;max ¼K
2rp1
p1ðr � q2E�2Þ þc1r
q1K
� �
þffiffiffiffiDp� �
with,
D ¼ p1ðr � q2E�2Þ þc1r
q1K
� �2
�4p1r
K
c1
q1
ðr � q2E�2Þ þ ðuþ1 þ L1Þ� �
:
We denote by,
E��1;min ¼1
q1
ð1� q2E�2Þ �1
2p1q1
p1ðr � q2E�2Þ þc1r
q1K
� �
�ffiffiffiffiDp� �
resp:E��1;max ¼ 1q1ð1� q2E�2Þ � 1
2p1q1p1ðr� q2E�2Þ þ c1r
q1K
� �þ
ffiffiffiffiDp� �� �
the corre-
sponding fishing effort of X1,min** (resp. X1,max
** ).
If,
p1ðr � q2E�2Þ þc1r
q1K
� �2
¼ 4p1r
K
c1
q1
ðr � q2E�2Þ þ ðuþ1 þ L1Þ� �
then the polynomial 11 admits a positive root:
X�� ¼ K
2
c1
p1q1Kþ
ffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffi
uþ1 þ L1
rp1K
s !
þ c1
2p1q1
:
We also denote by E��1 ¼ r2q1
ffiffiffiffiffiffiffiffiffiffiffiffiffiðuþ
1þL1Þ
rp1K
q
the corresponding fishing effort of X**.
Remark 4 As in dimension two, we suppose that Xmin sufficiently small and
K sufficiently high such that,
Xmin�X��1;min�K and Xmin�X��1;max�K:
The set of viable equilibrium points for fleet 1 is given by the following
proposition, the proof is left in the ‘‘Appendix 3’’:
Viability Analysis of Multi-fishery 197
123
Proposition 4 Under hypothesis (10) and if
1 [1
2
ffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffi
ðuþi þ LiÞrpiK
s
; ði 2 f1; 2gÞ ð12Þ
E2�E��2 ; ð13ÞEmax
1 �E��1;max: ð14Þ
then the set of viable equilibrium points is given by:
ABC ¼ X�;1
q1
rð1� X�
KÞ � q2E�2
� �
;E�2
� �maxðXmax
1 ;X��1;min�X� �X��1;max;0�E�2 �E��2
����
� �
where Xmax1 ¼ K 1� 1
r ðq1Emax1 þ q2E��2 Þ
� :
Remark 5 As in dimension 2, the condition (12) indicates that no fleet exploits the
fishery if the minimum income is not ensured and (14) reveal that E1,max** is the
minimal threshold of effort for the fleet 1 (Fig. 4).
3.2.4 The Viability Kernel of K1
Let us define the viability kernel of K1:
ViabðK1Þ ¼ ðX;E1;E2Þ9uið:Þwith u�i � uiðtÞ� uþi i 2 f1; 2g so that
the solution ðXð:Þ;E1ð:Þ;E2ð:ÞÞ of :ð1Þstarting at ðX;E1;E2Þ stay inK1
������
8<
:
9=
;
ViabðK1Þ is given by the following proposition which proof is left in the ‘‘Appendix
4’’
Proposition 5 Under hypothesis (10) and conditions (12), (13) and (14), one ofthe following cases occurs:
1. Case 1: if E1max [ E1,min
** then,
ViabðK1Þ ¼ ðX;E1;E2ÞX��1;min�X�K; and ðX;E1;E2Þ isbetween the surfacesD1;s andY1;s
����
� �
where Y1;s ¼ ðXð:Þ;E1ð:Þ;E2ð:ÞÞ is solution of the following Cauchy problem :
_X ¼ �FðXÞ þ q1E1X þ q2E2X;_E1 ¼ �u�1 ;_E2 ¼ �u�2 ;
X0 ¼ X��1;min; E0;1 ¼ E��1;min for all 0�E0;2�E��2 :
8>><
>>:
ð15Þ
2. Case 2: if E1max B E1,min
** then,
ViabðK1Þ ¼ ðX;E1;E2ÞXmax
1 �X�K; and ðX;E1;E2Þ isbetween the surfacesD1;s andEmax
1;s :
����
� �
198 C. Sanogo et al.
123
In the same way as previously, we determine the viability kernel associated to
fleet 2 given by the following proposition (Fig. 5),
Proposition 6 Under hypotheses (10), (12) and following conditions:
E1�E��1Emax
2 �E��2;max:
�
ð16Þ
The set of viable equilibrium points is given by:
A0B0C0 ¼ X�;E�1;1
q2
r 1� X�
K
� �
� q2E�1
� �� �maxðXmax
2 ;X��2;min�X�X��2;max;0�E1�E��1
����
� �
where Xmax2 ¼ K 1� 1
r ðq1E��1 þ q2Emax2 Þ
� :
For fixed E1, the set ViabðK2Þ is given by one of two following cases:
1. Case 1: if E2max [ E2,min
** then,
ViabðK2Þ ¼ ðX;E1;E2ÞX��2;min�X�K; and ðX;E1;E2Þ is
between surfacesD2;s and Y2;s
����
� �
where Y2;s ¼ ðXð:Þ;E1ð:Þ;E2ð:ÞÞ is solution of the following Cauchy problem,
_X ¼ �FðXÞ þ q1E1X þ q2E2X;_E1 ¼ �u�1 ;_E2 ¼ �u�2 ;
Xð0Þ ¼ X0;E1ð0Þ ¼ E0;1;E2ð0Þ ¼ E0;2;
8>><
>>:
with, X0 ¼ X��2;min;E0;2 ¼ E��2;min; 0�E01�E��1 :
2. Case 2: if E2max B E2,min
** then,
ViabðK2Þ ¼ ðX;E1;E2ÞXmax
2 �X�K; and ðX;E1;E2Þ isbetween surfacesD2;s and Emax
2;s
����
� �
with,
D2;s ¼ X;E1;ðuþ2 þ L2Þðp2q2X � c2Þ
� �
=X��2;min�X�K; 0�E1�E��1
� �
;
Emax2;s ¼ ðX;E1;E
max2 Þ=X��2;min�X�K; 0�E1�E��1
n o:
4 Intersection of the Two Viability Kernels K1 and K2
In this section, we determine the intersection of the viability kernels K1 and K2; in
which the two fleets can exploit the resource simultaneously without violating the
constraints. It is convenient to give the following definitions:
– E1,s** = {(X, E1
**, E2)/ X2,min** B X B K, 0 B E2 B E2
max}
Viability Analysis of Multi-fishery 199
123
– E2,s** = {(X, E1, E2
**)/ X1,min** B X B K, 0 B E1 B E1
max}.
The intersection of ViabðK1Þ with ViabðK2Þ is given by the following
proposition, the proof is left in the ‘‘Appendix 5’’:
Proposition 7 Under hypotheses (10), (12) and under conditions (13),(14)
and (16) the viability kernel is given according to the following cases:
1. Case 1: if E2** [ E2,min
** and E1** [ E1,min
**
ViabðK1Þ \ ViabðK2Þ ¼ ðX;E1;E2ÞmaxðX��1;min;X
��2;minÞ�X�K; ðX;E1;E2Þ
is above surfaces D1;s; D2;s
and bellow surfacesY1;s; Y2;s
������
8<
:
9=
;
2. Case 2: if E1** [ E1,min
** and E2** B E2,min
** ,
ViabðK1Þ \ ViabðK2Þ ¼ ðX;E1;E2ÞmaxðX��1;min;X
��2;minÞ�X�K; ðX;E1;E2Þ
is above surfacesD1;s;D2;s
and below surfacesY1;s; E��2;s
������
8<
:
9=
;
3. Case 3: if E��1 �E��1;min andE��2 [ E��2;min;
ViabðK1Þ \ ViabðK2Þ ¼ ðX;E1;E2ÞmaxðX��1;min;X
��2;minÞ�X�K; ðX;E1;E2Þ
is above surfacesD1;sD2;s
and below surfaces E��1;s; Y2;s
������
8<
:
9=
;
4. Case 4: if E1** B E1,min
** and E2** B E2,min
** ,
ViabðK1Þ \ ViabðK2Þ ¼ ðX;E1;E2ÞmaxðX��1;min;X
��2;minÞ�X�K; ðX;E1;E2Þ
is above surfacesD1;sD2;s
and below surfaces E��1;s; E��2;s
������
8<
:
9=
;
5 Conclusion and Discussion
In this work, we were looking for the management of sustainable exploitation of
renewable resources. Usually, one is inclined towards looking for the optimization
of the net income generated by the exploitation and/or stabilizing the production.
Such objectives allow to elaborate optimal strategies of exploitation. Nevertheless,
directives inspired by such studies are rarely directly applied in practice, especially
in the fishermen community. Asking fishermen to follow a precise strategy for
reaching desired objectives without taking into account external environment is of
course unrealistic.
In this work, we revisited in a new structure based on the concept of viability the
classical bioeconomic models elaborated by Clark (1990). The dynamics is
controlled by the variation of the fishing effort rather than the fishing effort and is
submitted to the constraints that ensure the system viability.
200 C. Sanogo et al.
123
The main goal of this study is not to maximize the income generated by the
exploitation, but to analyze the compatibility between the constraints and the
controlled dynamics. We used the viability analysis to build domain of viability
which is the set of initial conditions (efforts, stock) from which the system evolves
without violating the constraints. The viability kernel allows both of the fleets to
exploit the resource simultaneously and guarantees a minimum profit while
maintaining the stock above a minimal level of biomass. In particular for fishery
model, it goes through the introduction of effort and biomass minimal thresholds
and thus aims at reconciling ecological and economical objectives.
Indeed, the use of viability theory permitted us to find out a viability domain in
which the conservation of the resource and the exploitation activity are ensured. In
other terms it allowed us to characterize satisfactory management policies. Several
fleets with different characteristics can exploit the resources simultaneously and of
them will generate at least a minimal income.
These results are obtained in the setting where the natural growth rate of the
resource is represented by a logistic law. It is clear that in this study the model is built
on simplistic hypotheses. However, we showed that Li;E��i ; ði 2 f1; 2gÞ;and r* play
together a crucial role in the vacuity of viability kernel. In further we aim to include the
fact that the fishing efforts vary according to the investment. We hope to incorporate
the dynamics of price and the demand in order to make the model more realistic.
Generally, we believe that the viability approach may provide an interesting
analytical framework to address some of the issues experienced in natural resource
management and sustainable development.
Acknowledgements We would like to thank the two anonymous referees for their helpful comments.
Appendix 1
Proof of Proposition 1 The equilibrium points of (5) are X = 0 and
X� ¼ K 1� q1E�1r
� �
:
It is easy to see that X = 0 is not viable. The equilibrium points (X*, E1*) Must verify
the constraints r1, r2 and r3.
The expression of constraint r2 compared to X* is
ðp1q1X� � c1ÞE�1 � uþ1 � L1
which can be written according to X* as follows
� p1r
KX�2 þ r p1 þ
c1
q1K
� �
X� � c1r
q1
þ uþ1 þ L1
� �
� 0: ð17Þ
The resolution of this inequality depends on the position of r with respect to r*:
1. First case (see Fig. 2a): if r = r*, then (3) is satisfied and the inequality (17) is
reduced in a quadratic equation admitting a double root X� ¼ K2þ c1
2p1q1which is
Viability Analysis of Multi-fishery 201
123
viable considering the Remark 1. Hypotheses (6) and (7) ensure respectively
positivity and viability of the corresponding fishing effort of X* noted by,
E�1 ¼2ðuþ
1þL1Þ
p1q1K�c1.
2. Second case (see Fig. 2b): if r [ r* then, (3) is satisfied. Thus, the existence of
X1,min* and X1,max
* is ensured. The solutions X* of inequality (17) are given by:
X�1;min�X� �X�1;max
According to Remark 1, they are viable and the corresponding fishing efforts verify
the following double inequality :
E�1;max�E�1 �minðEmax1 ;E�1;minÞ:
Therefore, the set of viable equilibrium points is:
AB ¼ X�;r
q1
ð1� X�
KÞ
� �
maxðXmax1 ;X�1;minÞ�X� �X�1;max
���
� �
3. Third case (see Fig. 2c): if r \ r* then, the equilibrium points I1 is outside of
the set of constraints. In this case the set of viable equilibrium points is empty.
Fig. 2 Viable equilibrium points p1 = 1.3, q1 = 1, r = 1, c1 = 0.24, E1min = 0, E1
max = 1, K = 1.a One viable equilibrium point A = (X*,E1
*). b Two viable equilibrium points A = (X1,min* , E1,min
* ), B =(X1,max
* , E1,max* ). c No viable equilibrium points
202 C. Sanogo et al.
123
Appendix 2
Proof of Proposition 2 Consider the same hypotheses like in the Proposition 1, we
have two cases:
1. Case 1: if E1max [ E1,min
* then,
(a) Let us consider an initial condition (X, E1) above the curve Y1 (see Fig. 3)
such that X1,min* B X B K, 0 \ E1 B E1
max. For all control u1- B u1 B u1
?
the corresponding trajectory is decreasing until traversing the curve D1
before intersecting the nullcline I1: From this intersection point, the
trajectory leaves the set of constraints projðK1Þ: This means that the
trajectory will not stay in the set of constraints. Therefore, (X, E1) does not
belong to the viability kernel.
(b) Let us consider an initial condition (X, E1) underneath the curve Y1 (see
Fig. 3) such that X1,min* B X B K.
Knowing that the point (X ,E1) is above (resp. below) the segment AB, the
best choice of control consists of taking u1 = u1- (resp. u1 = u1
?) then,
the trajectory decreases (resp. increases). It is always possible to choose
the control so that the trajectory fulfils the sustainability constraints.
2. Case 2: if E1max B E1,min
* then, viability kernel is limited at the top by the straight
line E1 = E1max instead of the curve Y1 like in the Case 1. Therefore, we use the
same approach for the proof.
Appendix 3
Proof of Proposition 4 At equilibrium we have:
Fig. 3 Case 1: Viability kernel of projðK1Þ in phase plane (X,E1). with p1 = 1.3, q1 = 1, r = 1, c1 =0.24, u1
? = 1/15, u1- = - 1/15, E1
min = 0, E1max = 1, K = 1
Viability Analysis of Multi-fishery 203
123
rX 1� XK
� � q1E1ðtÞXðtÞ � q2E2XðtÞ ¼ 0;
u1 ¼ 0;u2 ¼ 0:
8<
:
It is easy to see that X = 0 is not viable. The other equilibrium points of (1) belong
to the plane whose equation is:
X� ¼ �K
rq1E�1 þ K 1� q2E�2
r
� �
ð18Þ
These equilibrium points (X*, E1*, E2
*) are viable if they verify constraints
r1, r2, r3.
The expression of the constraint r2 is :
� p1rK X�2 þ p1ðr � q2E�2Þ þ c1r
q1K
� �X� � c1
q1ðr � q2E�2Þ þ ðuþ1 þ L1Þ
� �� 0: ð19Þ
For all E2* fixed, the resolution of this inequality depends on the position of E2
*
relatively to E2**.
1. First case : if E2* = E2
** then, hypothesis (10) is satisfied. It implies that the
associated equation (19) admits only one positive root,
X�� ¼ K
2
c1
p1q1Kþ
ffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffi
uþ1 þ L1
rp1K
s !
þ c1
2p1q1
;
and E��1 ¼ r2q1
ffiffiffiffiffiffiffiffiffiffiffiffiffiðuþ
1þL1Þ
rp1K
q
is the corresponding effort of fleet 1. Therefore, there is only
one stationary point (X**, E1** , E2
**) its viability is ensured by hypothesis (12).
2. second case : if E2* \ E2
** the hypothesis (12) ensures the existence of
X1,min** , X1,max
** as the smallest and the biggest solution of equation (19)
respectively. The other solutions verify the following double inequality :
X��1;min�X� �X��1;max
Fig. 4 Set of viable equilibrium points in space (X, E1, E2) p1 = 1.3, q1 = 1, r = 1, c1 = 0.24,E1
min = 0, E1max = 1, E2
min = 0, E2max = 1, 2, K = 1
204 C. Sanogo et al.
123
and are viable according to Remark 3. By using (18) the expression of the fishing
effort of fleet 1 corresponding to X* is:
E�1 ¼1
q1
r 1� X�
K
� �
� q2E�2
� �
:
Therefore, the set of viable stationary points is given by ABC.
3. Third case : if E2* [ E2
** then, the plane Pis underneath surface D1s: Therefore,
no stationary point belongs to the set of constraint. Finally, the set of viable
stationary points is empty.
Appendix 4
Proof of Proposition 5 For all 0 B E2 B E2** we have,
1. Case 1: if E1max [ E1,min
** ,
(a) Let us consider an initial condition (X, E1, E2) above surface Y1;s such that
X1,min* B X B K. For all control u1
- B u1 B u1? the solution of the
dynamical system (1) decreases until traversing surface D1;s before
intersecting the surface P: From this intersection point with the surface
D1;s the trajectory leaves the set of constraints K1: Therefore (X, E1, E2)
does not belong to the viability kernel.
(b) Let us consider an initial condition (X, E1, E2) between surfaces D1;s and
Y1;s such that X1,min** B X B K.
Above the surface ABC one takes u1 = u1- then, for all admissible control
u2 the trajectory solution of dynamical system (1) decreases until
traversing surface ABC. Underneath surface ABC one take u1 = u1? then
the corresponding trajectory increases with respect to X and to E1 until
crossing the surface ABC. Therefore, there always exists a control choice
Fig. 5 Viability kernel of K1 in space (X, E1, E2). p1 = 1.3, q1 = 1, r = 1, c1 = 0.24, u1? =
1/15, u1- = - 1/15, E1
min = 0, E1max = 1, E2
min = 0, E2max = 1, 2, K = 1
Viability Analysis of Multi-fishery 205
123
to ensure that the trajectory fulfils the sustainability constraints. Finally,
(X, E1, E2) belongs to viability kernel.
2. Case 2: if E1max B E1,min
** then viability kernel is different from the previous case
by the surface E1,smax which delimits it at the top instead of the surface Y1;s:
Therefore, the same argument for the proof of Case 1 is valid in this case.
Appendix 5
Proof of Proposition 7
1. Case 1: if E��2 [ E��2;min and E��1 [ E��1;min
(a) Let us consider an initial condition (X, E1, E2) above surfaces Y1;s and
Y2;s such that max(X1,min** , X2,min
** ) B X B K. For all control u�i � ui� uþi ;ði 2 f1; 2gÞ the solution of dynamical system (1) decreases until traversing
one of the surfaces D1;s or D2;s and leaves one of the sets of constraints K1
or K2 before intersecting surface P: Therefore, (X, E1, E2) does not
belong to viability kernel.
(b) Let us consider an initial condition (X, E1, E2) above surfaces D1;s; D2;s
and underneath surfaces Y1;s; Y2;s; such that max(X1,min** , X2,min
** ) B
X B K. Above surface ABC \ A0B0C0; we take ui ¼ u�i ; ði 2 f1; 2gÞthe solution of dynamical system (1) decreases until crossing surface
ABC \ A0B0C0: Underneath this intersection we take ui ¼ uþi ; ði 2f1; 2gÞ the corresponding trajectory increases until traversing surface
ABC \ A0B0C0: Therefore, there always exists a choice of control that
maintains the trajectory in the constraints domain.
2. Case 2: if E��1 [ E��1;min and E��2 �E��2;min
We notice that the viability kernel is different from the one in Case 1. by
surface E2,s** which delimits it in top instead of Y2;s:
3. Case 3: if E��1 �E��1;min and E��2 [ E��2;min
In this case we find that the viability kernel is different from the one in Case 1.
by surface E1,s** which replaces the limit surface Y1;s:
4. Case 4: if E1** B E1,min
** and E2** B E2,min
**
The viability kernel is different from the viability kernel of Case 1. this time by
two surfaces E2,s** and E1,s
** . The first (resp. the second) appears instead of Y2;s
(resp. Y1;s). Therefore, we use the same argument in Case 1 for the proofs of
these three last cases.
References
Assessment ME (2005) Ecosystems and human well-being: biodiversity synthesis. http://www.millen
niumassessment.org/proxy/document.354.aspx
206 C. Sanogo et al.
123
Bene C, Doyen L, Gabay D (2001) A viability analysis for a bio-economic model. Ecol Econ
36(3):385–396. ISSN 0921-8009
Clark C (1990) Mathematical bioeconomics: the optimal management of renewable resources. 2nd edn.
Wiley, New York
Doyen L, Pereau J (2009) Sustainable coalitions in the commons. Cahiers du GREThA
FAO (2004) The state of world fisheries and aquaculture. Technical guidelines for Responsible Fisheries
4, Suppl 2, FAO
Jerry M, Raissi N (2001) A policy of fisheries management based on continous fishing effort. J Biol Syst
9(4):247–254. ISSN 0218-3390
Mullon C, Freon P (2006) Prototype of an integrated model of the worldwide system of small pelagic
fisheries. In: Climate change and the economics of the world’s fisheries: examples of small pelagic
stocks. Edward Elgar Publishing, pp 262–295. ISBN 1845424476
Raissi N. (2001) Features of bioeconomics models for the optimal management of a fishery exploited by
two different fleets. Nat Resour Model 14(2): 287–310. ISSN 1939-7445
Viability Analysis of Multi-fishery 207
123