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1 Introduction

Toxicity of 1,2-dichloroethane (DCA), in particular for aquatic and atmospheric biotic systems, has been recently recognized as a serious ecological problem [4]. DCA is difficult to remove from aquatic media by physico-chemical methods due to its very low concentration. Therefore, biodegradation remains the only available alternative. A microbial strain, recently recommended as a “novelty” and capable to degrade DCA to its complete mineralization is Klebsiella oxytoca VA 8391 [3, 4]. This strain was isolated from active sludge from a wastewater plant at the Luckoil Neftochim Rafinery in Burgas, Bulgaria. The identification was validated by the National Bank for Industrial Microorganisms and Cultures in Sofia, Bulgaria, and the strain was registered under the code number stated above.

We consider a continuous bioreactor model for DCA biodegradation by Klebsiella oxytoca VA 8391 immobilized on granulated activated carbon. During the microbial process the immobilized cells can detach from the solid surface and live and grow in the liquid phase. The process is irreversible, i. e. free cells can not attach again the solid particles. The model is developed and validated in [4] by authors’ own experiments.

2 Model Description

The continuous flow bioreactor model describing DCA biodegradation by Klebsiella oxytoca VA 8391 immobilized on granulated activated carbon is presented by the following differential equations [4]

$$\displaystyle\begin{array}{rcl} \dot{x}_{1}& =& (\mu _{1}(s) - D)x_{1} + k_{\mathit{im}}x_{\mathit{im}}{}\end{array}$$
(1)
$$\displaystyle\begin{array}{rcl} \dot{x}_{\mathit{im}}& =& \left (\mu _{\mathit{im}}(s) - k_{\mathit{im}}\right )x_{\mathit{im}}{}\end{array}$$
(2)
$$\displaystyle\begin{array}{rcl} \dot{s}& =& -\left (\frac{1} {\gamma } \mu _{1}(s) +\beta _{1}\right )x_{1} -\left (\frac{1} {\gamma } \mu _{\mathit{im}}(s) +\beta _{\mathit{im}}\right )x_{\mathit{im}}{}\end{array}$$
(3)
$$\displaystyle\begin{array}{rcl} & & +\:D({s}^{\mathit{in}} - s) - k_{ L}a(1 -\mu _{2}(s))s \\ \dot{p}& =& \left (\frac{1} {\gamma } \mu _{1}(s) +\beta _{1}\right )x_{1} + \left (\frac{1} {\gamma } \mu _{\mathit{im}}(s) +\beta _{\mathit{im}}\right )x_{\mathit{im}} -\mathit{Dp},{}\end{array}$$
(4)

where the dot over the phase variables means \(\frac{d} {\mathit{dt}}\). The functions μ 1(s) and μ im (s) are the specific growth rates of the free and the immobilized cells respectively, μ 2(s) is related to the adsorption capacity. The following functions are proposed in [4]:

$$\displaystyle{\mu _{1}(s) = \frac{m_{1}s} {k_{s} + s + {s}^{2}/k_{i}}, \mu _{\mathit{im}}(s) = \frac{m_{\mathit{im}}s} {k_{s} + s + {s}^{2}/k_{i}}, \mu _{2}(s) = \frac{m_{2}s} {k + s}.}$$

The growth rate functions μ 1(s) and μ im (s) exhibit inhibition, i.e. they achieve their maximum at the point \({s}^{m} = \sqrt{k_{s } k_{i}}\). The function μ 2(s) is bounded and μ 2(s) < m 2 is valid for all s ≥ 0. The definition of the phase variables x 1, x im , s and p as well as of the model parameters is given in Table 1.

In the bioreactor, the free cells are expected to consume easily the substrate necessarily for their growth, but they are more keen to be carried out by the flow. On the contrary, the immobilized cells have a more difficult access to the resources of the bulk fluid, but are more resistent to detachment induced by the hydrodynamical conditions. To predict this observation by the model, we assume that the following inequality holds true (see also the hypothesis (H5) below)

(H1):

m im  < m 1

This inequality implies that μ im (s) < μ 1(s) for all s > 0.

Table 1 Definition of the model variables and parameters

3 Equilibrium Points of the Model and Their Lyapunov Stability

Denote by

$$\displaystyle{\phi (s) = D({s}^{\mathit{in}} - s) - k_{ L}a(1 -\mu _{2}(s))s}$$

the function included in the right-hand side of (3) and assume that the following inequality is satisfied:

(H2):

max{k L a,  m 2} < 1.

It is straightforward to see, that \(\frac{d} {\mathit{ds}}\phi (s) < 0\) for all s ≥ 0; moreover, there exists a unique positive root ζ 0 of ϕ(s) = 0 such that \(\zeta _{0} < {s}^{\mathit{in}}\) and further ϕ(s) ≥ 0 if s ∈ [0, ζ 0], and ϕ(s) < 0 if s > ζ 0.

The equilibrium points of the model are solutions of the form \((x_{1},x_{\mathit{im}},s,p)\) of the nonlinear system, obtained from (1) to (4) by setting the right-hand sides equal to zero. We are looking for equilibrium points with nonnegative components due to physical evidence.

Proposition 1.

Under assumptions (H1) and (H2), the equilibrium points of the model are the following:

  1. (i)

    \(E_{0} = \left (0,\;0,\;\zeta _{0},\;0\right )\);

  2. (ii)

    \(E_{i} = \left ( \frac{\phi (\xi _{i})} {\frac{1} {\gamma } D+\beta _{1}},\:0,\xi _{i},\: \frac{\phi (\xi _{i})} {D} \right )\) , i = 1,2, (with x im = 0) where ξ i are solutions of μ 1 (s) = D; E i exist if and only if \(D \leq \max _{s>0}\:\mu _{1}(s) =\mu _{1}\left ({s}^{m}\right )\) and ϕ(ξ i ) > 0.

  3. (iii)

    \(F_{i} = \left (x_{1}^{(i)},x_{\mathit{im}}^{(i)},\zeta _{i},{p}^{(i)}\right )\) , i = 1,2, where ζ i are solutions of μ im (s) = k im , \(x_{1}^{(i)} = \frac{k_{\mathit{im}}\phi (\zeta _{i})} {\beta _{\mathit{im}}(D-\mu _{1}(\zeta _{i}))+k_{\mathit{im}}\left (\frac{1} {\gamma } D+\beta _{1}\right )}\) , \(x_{\mathit{im}}^{(i)} = \frac{D-\mu _{1}(\zeta _{i})} {k_{\mathit{im}}} x_{1}^{(i)}\) and \({p}^{(i)} = \frac{x_{1}^{(i)}} {D} \left (\left (\frac{1} {\gamma } \mu _{1}(\zeta _{i}) +\beta _{1}\right ) + \left (\frac{1} {\gamma } \mu _{\mathit{im}}(\zeta _{i}) +\beta _{\mathit{im}}\right )\frac{D-\mu _{1}(\zeta _{i})} {k_{\mathit{im}}} \right )\) ; F i exist if and only if \(k_{\mathit{im}} \leq \max _{s>0}\mu _{\mathit{im}}(s) =\mu _{\mathit{im}}\left ({s}^{m}\right )\) , D > μ 1 i ) and ϕ(ζ i ) > 0.

The point E 0 is called wash-out equilibrium. The existence of E i corresponds to the case of free microbial culture without immobilized cells on the carrier. Practically the most important equilibria are the internal points F i ; the condition k im  ≤ μ im (s m) describes the case of compensated immobilized cell leakage by growth within the particles.

Let \(E \in \left \{E_{0},E_{1},E_{2},F_{1},F_{2}\right \}\) be any one of the equilibrium points, described above. Denote by J(E) the Jacobian of (1)–(4) evaluated at E. The eigenvalues of J(E) are the roots of the following characteristic equation (I denotes the (4 × 4)-unit matrix) \(0 = \left \vert J(E) -\lambda I\right \vert = (-D-\lambda ) \cdot ({-\lambda }^{3} + {a\lambda }^{2} - b\lambda + c)\), where the coefficients a = a(E), b = b(E) and c = c(E) can be computed explicitly, using the well known invariants of the matrix J(E). Obviously, \(\lambda _{4} = -D < 0\) is an eigenvalue of every equilibrium point \(E \in \left \{E_{0},E_{1},E_{2},F_{1},F_{2}\right \}\). This means that there are no repelling steady states in the model. The other three eigenvalues are the roots of the cubic polynomial \(g(\lambda ) = {-\lambda }^{3} + {a\lambda }^{2} - b\lambda + c\). Using the Routh-Hurwitz criterion [5] for determining the signs of the real parts of the roots of g(λ), we obtain the following

Proposition 2.

Let the hypotheses (H1) and (H2) be satisfied.

  1. (i)

    If μ 1 0 ) < D and \(\mu _{\mathit{im}}(\zeta _{0}) < k_{\mathit{im}}\) are fulfilled, the equilibrium point E 0 is locally asymptotically stable; otherwise E 0 is a saddle.

  2. (ii)

    Let the assumptions of Proposition 1(ii) be satisfied. If μ im i ) < k im , i = 1,2, then E 1 is locally asymptotically stable and E 2 is a saddle equilibrium point. If μ im i ) > k im , i = 1,2, then E 1 and E 2 are saddle equilibrium points.

  3. (iii)

    Let the assumptions of Proposition 1(iii) hold. Then F 1 is locally asymptotically stable and F 2 is a saddle equilibrium point.

4 Global Properties of the Solutions

The first three equations (1)–(3) do not depend on p. If we “compute” the solutions x 1(t), x im (t), s(t) and replace them in (4), we obtain a linear nonautonomous equation for p of the form \(\dot{p} = -D\:p +\psi (t)\), which can be integrated directly. Therefore, we can omit the last equation (4) in the further considerations.

We impose additionally the following assumption on (1)–(3)

(H3):

\(\beta _{1} <\beta _{\mathit{im}} < \frac{k_{L}a} {\gamma }\), \(D > 1 - k_{L}a(1 - m_{2})\)

Proposition 3.

Let the assumptions (H1)–(H3) be fulfilled. Then the set \(\varOmega \!=\! \left \{(x_{1},x_{\mathit{im}},s): x_{1} \geq 0,x_{\mathit{im}} \geq 0,s \geq 0,D{s}^{\mathit{in}} \geq s +\beta _{1}x_{1} +\beta _{\mathit{im}}x_{\mathit{im}}\right \}\) is positively invariant for the model; all solutions are uniformly bounded for all t ≥ 0 and thus exist for t ∈ [0,+∞).

Experimental results show that the inlet substrate concentration s in must be lower than the one corresponding to the maximum specific growth rate, i.e. s in should be below the point s m where substrate inhibition starts to be significant. Assume that the following inequalities are fulfilled:

(H4):

s in < s m, k im  < μ im (ζ 0). 

It is not difficult to see that under assumptions (H1)–(H4), s(t) < ζ 0 is valid for all sufficiently large t > 0. Moreover, since \(\zeta _{0} < {s}^{\mathit{in}}\) holds, assumption (H4) implies that the functions μ 1(s) and μ im (s) are monotone increasing for s ∈ [0, ζ 0]. Our last assumption is

(H4):

\(D >\mu _{1}({s}^{\mathit{in}}) + k_{\mathit{im}}\)

The hypotheses (H1)–(H5) and Proposition 1 imply that there exist only two equilibrium points of (1)–(3) in Ω, namely E 0 and F 1; thereby F 1 is locally asymptotically stable, E 0 is a saddle equilibrium. We shall show that \(F_{1} = (x_{1}^{(1)},x_{\mathit{im}}^{(1)},\zeta _{1})\) is globally asymptotically stable for the model.

Theorem 1.

Let the assumptions (H1)–(H5) be satisfied. Then the equilibrium point F 1 is globally asymptotically stable for (1)–(3) in the set Ω.

Proof.

It is enough to show that the stable manifold of E 0 lies exterior to the set Ω (cf. [6]). The negative eigenvalues of E 0 = (0, 0, ζ 0) are \(\lambda _{1} =\mu _{1}(\zeta _{0}) - D\) and \(\lambda _{2} = \frac{d} {\mathit{ds}}\phi (\zeta _{0})\). Denote by \(u = (u_{1},u_{2},u_{3})\) and \(v = (v_{1},v_{2},v_{3})\) the corresponding eigenvectors. It is easy to see that u 2 = 0 and \(qu_{3} = -\left (\frac{1} {\gamma } \mu _{1}(\zeta _{0}) +\beta _{1}\right )u_{1}\) within \(q =\mu _{1}(\zeta _{0}) - D - \frac{d} {\mathit{ds}}\phi (\zeta _{0}) > 0\). Therefore, u cannot be directed inside the positive octant. The same is valid for the eigenvector v, since the latter has the form v = (0, 0, v 3) with \(v_{3}\neq 0\). Therefore, the stable manifold of E 0 does not intersect the interior of Ω, which implies that F 1 attracts all solutions with initial conditions in Ω, i.e. F 1 is a global attractor. This completes the proof.

5 Numerical Simulation

Consider the numerical coefficient values in Table 1 (last column). For these values, all the assumptions (H1)–(H5) are satisfied, and therefore Theorem 1 holds true.

Figure 1 visualizes results from computer experiments with an initial point (x 1(0), x im (0), s(0), p(0)) from the set Ω, i.e. satisfying \(D{s}^{\mathit{in}} \geq s(0) +\beta _{1}x_{1}(0) +\beta _{\mathit{im}}x_{\mathit{im}}(0)\). The solid circles correspond to experimental measurements, taken from [4].

Fig. 1
figure 1

Phase curves x 1(t) (left), s(t) (middle) and p(t) (right); the horizontal dashed lines pass through the components of F 1. Solid circles denote experimental data

6 Conclusion

The paper presents global stability analysis of a practically validated ecological model for wastewater treatment. Most of the results are obtained and proved in [1, 2]. The proof of the above Theorem 1 is new. Here, the computer simulations are compared with experimental measurements.

The present mathematical analysis of the model (1)–(4) could be useful to outline the parameter domain for stable operation of the microbial process in a continuously stirred bioreactor.