From Consumer-Resource to single-species dynamics
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From consumer-resource models to single-species dynamics
We are interested in building simple consumer-resource models and exploring how single-species models emerge as we simplify the dynamics of the resource. We assume a simple Lotka-Volterra type equation, with a carrying capacity for the resource:
\[ \begin{aligned} \frac{dR}{dt} &= rR \left(1-\frac{R}{K}\right) - cRN \\ \frac{dN}{dt} &= N(ecR - d) \end{aligned}\] The fixed points are: the trivial one \((0, 0)\), only resource \((K, 0)\), and the coexistence one, given by \(R^* = \frac{d}{ec}\), \(N^* = \frac{r}{c}\left(1-\frac{R^*}{K}\right)\). The trivial fixed point is unstable (the resource is always able to grow), and the fixed point without consumers is unstable if \(ecK-d > 0\), that is, if the consumer is able to grow when the resource is at its carrying capacity. The stability of the coexistence fixed point can be found calculating the Jacobian at that point:
\[ J = \begin{bmatrix} -\frac{r}{K} & -cR^* \\ ecN^* & 0 \end{bmatrix} = \begin{bmatrix} -\frac{r}{K} & -\frac{d}{e} \\ er\left(1-\frac{R^*}{K}\right) & 0 \end{bmatrix} \]
We can see directly that the trace \(T\) of the Jacobian is negative while its determinant \(\Delta\) is positive. The eigenvalues \(\lambda\) are determined by \(\lambda^2 - T \lambda + \Delta = 0\), so \(\lambda = \frac{1}{2}\left[T \pm \sqrt{T^2 - 4\Delta} \right]\). It is clear that the real part of the eigenvalues are always negative, and the eigenvalues will be complex when the term inside the square root becomes negative. Thus, we conclude that the coexistence fixed point is always stable.
Now we rescale the variables and time by letting \(t' = dt\), \(R'=\frac{R}{R^*}\) and \(N'=\frac{N}{N^*}\). Rewriting the equations (and dropping the primes), we have:
\[ \begin{aligned} \frac{dR}{dt} &= \frac{r}{d} \left[ R (1-\beta R) - (1-\beta) RN \right]\\ \frac{dN}{dt} &= N (R - 1) \end{aligned} \]
where \(\beta = \frac{R^*}{K} = \frac{d}{ecK}\).
Let's assume that the resource growth rate is much faster than the consumer's death rate, that is, \(r \gg d\). Another way of writing this is \(\frac{d}{r} = \epsilon \ll 1\). Plugging it in the resource equation, it becomes \(\epsilon \frac{dR}{dt} = \left[ R (1-\beta R) - (1-\beta) RN \right]\). Since \(\epsilon\) is very small, it can be a good approximation to set it to zero, so that the resource equation becomes just an algebraic equation:
\[ R (1-\beta R) - (1-\beta) RN = 0 \therefore R = \frac{1 - (1-\beta)N}{\beta} \]
Substituting it back into the differential equation for the consumer, we find
\[ \frac{dN}{dt} = N \left[\frac{1 - (1-\beta)N}{\beta} - 1\right] = \frac{1-\beta}{\beta} N (1-N) \]
We just recovered the logistic equation! Let's write the equation above in dimensional form again:
\[ \frac{dN}{dt} = (ecK-d) N \left[ 1-\frac{N}{\frac{r}{c}\left( 1-\frac{d}{ecK}\right)} \right] = r_C N \left(1-\frac{N}{K_C}\right)\]
So we find that the consumer-resource model we proposed, in the limit where the resource growth rate is much faster than consumer mortality, leads to a logistic growth for the consumer with maximum growth rate \(r_C = (ecK-d)\) and carrying capacity \(K_C = \frac{r}{c}\left( 1-\frac{d}{ecK}\right)\). By approximating \(\epsilon=0\), we were able to derive a phenomenological model of population regulation from a mechanistic model of consumption and limitation of resources, and thus relate the phenomenological parameters of the logistic equation to measurable quantities such as consumption and mortality rates, and efficiency of conversion.
Still, the original consumer-resource model is not completely mechanistic, since it assumes that the resource growth also saturates at a carrying capacity. This is appropriate, as "mechanistic" and "phenomenological" are not two separate categories, but are actually part of a continuum, with more mechanistic models incorporating more explicit details of the processes involved.
We explore below how well this approximation behaves for different values of parameters and initial conditions. We have several factors to take into account. The first thing we should be careful is to look at it in the time-scale of the consumer, that is much longer than that of the resource, and look at how different the time-scales of consumer and resource are (that is, the value of \(\epsilon=\frac{d}{r}\)).
In second place, regarding the stability analysis of the original system, we could have damped oscillations that may influence how the solutions approach the fixed point. This is determined by the sign of the discriminant: if it is positive, perturbations around the fixed point do not overshoot the fixed point, otherwise they oscillate towards it. The condition for the absence of oscillation is:
\[ T^2 - 4\Delta = \left(\frac{r}{K}\right)^2 - 4 dr\left(1 - \frac{d}{ecK}\right) > 0 \]
Finally, initial conditions may be important: if we use both models with the same initial values for the consumer, the first model will behave differently depending on the initial population of the resource. If the initial consumer population is small (compared to \(N^*\)), we expect that the resource population starts near (or at) the carrying capacity, which should yield dynamics closer to that of the logistic model.
First, we look at the simplest case: \(r\) is \(1000\) times larger than \(d\) (\(\epsilon = 0.001\)), the dynamics of the consumer-resource model are asymptotic (no oscillatory behavior: \(T^2-4\Delta > 0\)).
%pylab inline
# larger plots and fonts, please
pylab.rcParams['figure.figsize'] = (10.0, 6.0)
pylab.rcParams['font.size'] = 12
from scipy.integrate import odeint
ion()
def LVK(y, t, r, K, c, e, d):
"""Lotka-Volterra equations with a resource carrying capacity."""
return array([ r * y[0] * (1-y[0]/K) - c*y[0]*y[1],
y[1] * (e*c*y[0] -d) ])
def logist(y, t, rC, KC):
"""The logistic equation."""
return rC*y*(1-y/KC)
# parameters of C-R model
r = 10.
K = 10.
c = 0.1
e = 0.1
d = 0.01
# corresponding parameters of single-species model
rC = e*c*K-d
KC = r/c * (1-d/(e*c*K))
t = arange(0, 200, 0.1)
y0 = [K, .1]
# we integrate the C-R model
y = odeint(LVK, y0, t, (r, K, c, e, d))
# and the logistic model
yC = odeint(logist, y0[1], t, (rC, KC))
# the time-scales ratio epsilon
print('epsilon: ', d/r)
# check the stability, if the discriminant T^2-4 Delta is positive,
# the solutions do not approach the fixed point oscillating
print('discriminant: ', (r/K)**2 - 4*d*r*(1-d/(e*c*K)))
print('initial condition: ', y0)
plot(t, y[:,0], label='resource')
plot(t, y[:,1], label='R-C model')
plot(t, yC, label='1-species model')
xlabel('time')
ylabel('population')
ylim((0, KC*1.1))
legend(loc='best');
The agreement is quite good! Now we make \(r\) smaller and \(d\) larger, reducing \(\epsilon\) from \(1/1000\) to just \(1/10\). Notice that, as we do that, we also make \(T^2-4\Delta\) negative.
# parameters of C-R model
r = .5
K = 10.
c = 0.1
e = 0.1
d = 0.05
# corresponding parameters of single-species model
rC = e*c*K-d
KC = r/c * (1-d/(e*c*K))
t = arange(0, 400, 0.1)
y0 = [K, .1]
# we integrate the C-R model
y = odeint(LVK, y0, t, (r, K, c, e, d))
# and the logistic model
yC = odeint(logist, y0[1], t, (rC, KC))
# the time-scales ratio epsilon
print('epsilon: ', d/r)
# check the stability, if the discriminant T^2-4 Delta is positive,
# the solutions do not approach the fixed point oscillating
print('discriminant: ', (r/K)**2 - 4*d*r*(1-d/(e*c*K)))
plot(t, y[:,0], label='resource')
plot(t, y[:,1], label='R-C model')
plot(t, yC, label='1-species model')
xlabel('time')
ylabel('population')
ylim((0, KC*1.2))
legend(loc='best');
We see that, although the final solution is the same (as it should always be!), the relative difference in the dynamics in the transient increased. Now it is your time to explore: try changing the initial conditions and parameter values and see when the approximation breaks badly!
References
The Consumer-Resource model was proposed by MacArthur a long time ago, and he then already pointed out that by substituting the value of the resource population at equilibrium back into the consumer equation, we recover the logistic equation. Schaffer later generalized this approach to more general forms. The recent paper by Reynolds and Brassil (which begins with the approach we followed here) treats the same question from the point of view of separating time scales, a topic that has been receiving some attention in the recent theoretical literature.
- Robert H. MacArthur (1972) Geographical Ecology: patterns in the distribution of species
- Schaffer 1981
- Reynolds and Brassil 2013