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j - Dipartimento di Matematica - Politecnico di Torino

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(1)<br />

(1)<br />

(a) M = 0 ; V = 0<br />

(2)<br />

(b) M = 0 ;<br />

( 2) bT<br />

− hU<br />

0<br />

V<br />

=<br />

b<br />

T<br />

(c)<br />

(d)<br />

M<br />

M<br />

M<br />

max<br />

( c k)<br />

(3)<br />

= , V = 0<br />

c<br />

( 3) −<br />

(4)<br />

=<br />

M<br />

max<br />

[ c − k( 1 −V<br />

)]<br />

c<br />

e<br />

,<br />

b<br />

=<br />

hU<br />

b<br />

( 4) T<br />

−<br />

0<br />

V<br />

T<br />

As it can be easily understood the first equilibrium is quite negative since it prevents an<br />

environment where production and <strong>di</strong>ffusion of biological energy is negligible and no areas of high<br />

ecological quality are present. The second scenario is that of a territory strongly fragmented where<br />

<strong>di</strong>ffusion of biological energy between the LU is again negligible but some area of high quality<br />

vegetation is still present. The third equilibrium corresponds to a territory characterized by some<br />

production and <strong>di</strong>ffusion of bio-energy but low vegetation quality. Finally the last scenario is that<br />

more favourable since strong production and <strong>di</strong>ffusion of biological energy between the LU allows<br />

to guarantee an ecological settlement of high level of bio-potentiality. The stability analysis (Finotto<br />

et al., 2010) has shown that the above equilibrium solutions can be obtained, respectively, when the<br />

model parameters satisfy the following inequalities:<br />

c < k and b T<br />

< hU<br />

0<br />

(I)<br />

khU<br />

0<br />

> cb T<br />

and b T<br />

> hU<br />

0<br />

(II)<br />

c > k and b T<br />

< hU<br />

0<br />

(III)<br />

khU<br />

0<br />

> cb T<br />

and b T<br />

> hU<br />

0<br />

(IV)<br />

The ecological graph representation together with the solutions of the mathematical procedure can<br />

be derived through a NetLogo model application that give us an easy tool to model the equilibrium<br />

states of landscape evolution starting from the initial, actual con<strong>di</strong>tions as described by the<br />

ecological graph itself (Gobattoni F. et al., 2010).<br />

Results and <strong>di</strong>scussion<br />

As an assessment of the ecological behaviour for an environment, the ecological graph assigns a<br />

node <strong>di</strong>mension proportional to the available energy and a link between LU with a <strong>di</strong>mension<br />

proportional to the flux of energy. The energy exchange among them will be more or less strong<br />

depen<strong>di</strong>ng on the degree of permeability of the barriers which can obstruct the energy passage from<br />

each LU to the other.

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