Application of Luenberger Observers to Environmental Modeling of Rivers

4.8. Application of Luenberger Observers to Environmental Modeling of Rivers#

Rodriguez-Mata, Abraham Efraim, et al. “A Fractional High-Gain Nonlinear Observer Design—Application for Rivers Environmental Monitoring Model.” Mathematical and Computational Applications 25.3 (2020): 44. https://www.mdpi.com/2297-8747/25/3/44

4.8.1. Model#

The Streeter-Phelps model for oxygen in a river or stream is given by the pair of linear differential equations

(4.4)#\[\begin{align} \frac{dx_1}{dt} & = -\frac{k_1}{U} x_2 + \frac{k_2}{U}(D_s - x_1) \\ \frac{dx_2}{dt} & = -\frac{k_1}{U} x_2 \end{align}\]

where \(x_1\) is dissolved oxygen (DO) and \(x_2\) is biological oxygen demand (BOD). Rate constant \(k_1\) is the BOD removal rate, \(k_2\) is the re-areation rate, and \(D_s\) is the oxygen saturation level which, for this problem, is a disturbance variable. No manipulations to this system are possible.

For environmental monitoring, dissolved oxygen can be measured in the field with a low-cost sensor. BOD, however, cannot be measured in the field.

Our standard model for a state-space system is given by

(4.5)#\[\begin{align} \frac{dx}{dt} & = A x + B_d d + B_u u\\ y & = C x \end{align}\]

where \(x\) contains the states, \(d\) contains the disturbances, and \(u\) contains the manipulable inputs.

Parameter values are \(k_1 = 0.3\ \text{day}^{-1}\), \(k_2 = 0.06\ \text{day}^{-1}\), and \(U = 1\). A typical value of Ds = 16 mg/liter. For these values the state space model becomes

(4.6)#\[\begin{align} \frac{dx}{dt} & = A x + B_d d + B_u u\\ y & = C x \end{align}\]

where

(4.7)#\[\begin{align} A & = \begin{bmatrix} -0.06 & -0.3 \\0 & -0.3\end{bmatrix} \qquad B_d = \begin{bmatrix} 0.06 \\ 0 \end{bmatrix} \\ C & = \begin{bmatrix} 1 & 0 \end{bmatrix} \end{align}\]

For the state estimator, aat each time step \(t_k\) there are two calculations to perform:

  • Model Prediction: Use the model to update the state to the next time step, i.e., \(\hat{x}_{k-1} \rightarrow \hat{x}_{k}^{pred}\) with the equation

(4.8)#\[\begin{align} \hat{x}_k^{pred} & = \hat{x}_{k-1} + (t_k - t_{k-1}) ( A \hat{x}_{k-1} + B_u u_{k-1} + B_d \hat{d}_{k-1}) \\ \hat{y}_k^{pred} & = C \hat{x}_k^{pred} \end{align}\]

  • Measurement Correction: Use measurement \(y_k\) to update \(\hat{x}_{k}^{pred} \rightarrow \hat{x}_{k}\) with the equation

\[\hat{x}_{k} = \hat{x}_{k}^{pred} - (t_k - t_{k-1})L (\hat{y}_{k}^{pred} - y_k)\]
therefore it is desired to implement a Luenberger observer to estimate BOD. 


Our standard model for a state-space system is given by

\begin{align}
\frac{dx}{dt} & = A x + + B_u u + B_d d \\
y & = C x
\end{align}

4.8.2. State Space Model#

import numpy as np

k1 = 0.3
k2 = 0.06
U = 1
Ds = 16.0


A = np.array([[-k2/U, -k1/U], [0, -k1/U]])
Bd = np.array([[k2/U], [0]])
C = np.array([[1, 0]])


sources = [
    ("DO", lambda: x[0]),
    ("BOD", lambda: x[1]),
    ("DS", lambda: Ds )
]

array([[-0.06, -0.3 ],
       [ 0.  , -0.3 ]])

import numpy as np
import cvxpy as cp
n=2
p = 1

P = cp.Variable((n, n), PSD=True)
Y = cp.Variable((n, p))

gamma = .75
constraints = [P >> np.eye(n)]
constraints += [A.T@P + P@A - C.T@Y.T - Y@C + gamma*P << 0]

prob = cp.Problem(cp.Minimize(0), constraints)
prob.solve()
L = np.linalg.inv(P.value)@Y.value
print(L)

[[ 0.49691879]
 [-0.43544205]]

np.linalg.eig(A-L@C)

(array([-0.4284594+0.3378325j, -0.4284594-0.3378325j]),
 array([[-0.22700032+0.59698307j, -0.22700032-0.59698307j],
        [ 0.76946869+0.j        ,  0.76946869-0.j        ]]))
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