Robust multivariable tracking control for biological wastewater treatment process with external disturbances and uncertainties
Abstract
This paper proposes a robust multivariable tracking control (RMTC) strategy to address tracking control of the biological wastewater treatment process (BWWTP) with external disturbances and uncertainties. Primarily, the system of BWWTP, attributed to an ill-defined nonaffine nonlinear system, is directly expanded with Taylor series expansion in the neighborhood of the nominal control law (NCL). To achieve NCL, the RMTC is drawn with a direct controller and an approximate controller. The direct controller is introduced with sliding-mode theory while the structure of the system is unknown and no prior knowledge about external disturbances/uncertainties is available. The approximate controller is employed to compensate for the uncertainties of BWWTW with a suitable-sized fuzzy neural network that is tuned by a self-organizing mechanism. Then, an adaptive strategy is established to optimize the control gain and parameters of fuzzy neural network to hold the steady-state control performance under different operational conditions by suppressing the negative impacts of external disturbances and approximation errors. Finally, the stability of RMTC is established to ensure successful applications. The RMTC is evaluated in an actual BWWTP. The results including tracking performance, controlinputs, and adaptive parameters have shown that RMTC can provide effective control performance with the external disturbances and uncertainties under different operational conditions.
Keywords
1. INTRODUCTION
Biological wastewater treatment process (BWWTP), using bacteria and microorganisms to remove the pollution, has been recognized as a primary operation within wastewater treatment plants[1]. The control methods of BWWTP have attracted significant attention in industries and academia due to the increasing awareness to ensure effluent qualities[2-4]. The situation faced, however, it is difficult to control this process because of the external disturbances including the dynamics of influent flow rate and quality, as well as the noise of sensors in different treatment units[5, 6]. Besides, the uncertainties, such as the activity of microorganisms in biological reactions, implicitly change the inherent kinetics of BWWTP, which also has a significant impact on control performance[7-9].
To reject the external disturbances of process control in BWWTP, multiple robust control methods have been formulated [10-14]. Notably, Floresestrella et al. introduced a robust \(H_\infty \) control strategy to regulate the chemical oxygen demand[10]. This control strategy, based on the \(H_\infty \) control synthesis, can depress the fluctuations of organic compound concentrations in the influent. A robust control strategy, using a process-oriented approach, was proposed for removing the autotrophic nitrogen in the BWWTP[11]. The parameters of this control strategy were tuned by the internal model rules to improve the robust performance for operating the organic carbon concentration. Moreover, a multivariable robust-adaptive control (MRAC) methodology crafted for regulating dissolved oxygen and substrate concentrations[12]. For MRAC, an interval observer was crafted for calculating the minimum and maximum limits of external disturbances. The results indicated that this proposed MRAC could obtain suitable robust performance. However, the above control strategies[8-12] are sensitive to the system parameters. They are difficult to implement with steady-state performance. Recently, with the advantages of robustness, as well as easy implementation, sliding mode control (SMC) is regarded as an efficient method for controlling BWWTPs. A sliding-mode-based feeding control strategy was proposed for the fed-batch operation of BWWTP, where the desired performances (such as the fast response, the robustness and stability were attained[15]. However, a problem of this feeding control strategy is the chattering phenomenon of control action[16-18]. To mitigate the chatter in SMC, an adaptive SMC control method (ASMC) was investigated for the BWWTP operation[19]. For ASMC, an adaptation tuning approach was devised to mitigate the chattering phenomenon. The results displayed that this ASMC was able to stabilize the biomass concentration. Meanwhile, an adaptive dynamic SMC strategy (ADSMC) was designed to regulate the sludge recycle flow in BWWTP[20]. In ADSMC, an adaptive technique, which allows the controller parameters to be self-tuned towards the optimum values, was designed to suppress the chattering phenomenon and maintain robust performance. In addition, some other SMC methods have been presented[21-24]. The results demonstrated that these SMC methods can be applied to enhance the robustness of BWWTP. However, these control strategies mainly focused on the solutions to the disturbances rather than the uncertainties of the system, variation of system parameters, etc. They are difficult to shape because the structure of the system is unknown or prior knowledge about disturbances/uncertainties is unavailable[25, 26].
To deal with the uncertainties of BWWTP, Zuniga et al. developed a BWWTP wastewater treatment biofilter using an observer-based output linearizing control approach (OBLC)[27]. In this OBLC, a distributed parameter observer was designed to identify the uncertainties, such as the changes in nitrification and denitrification, to improve robust performance. A sliding mode observer control (SMOC) method was established for controlling the substrate concentrations, where the uncertainties were identified by using a sliding observer[28]. However, the achievements of OBLC and SMOC were dependent on the accurate mathematical model[29]. It is challenging to establish a precise mathematical model for BWWTP[30-33]. Recently, some intelligent control strategies, such as fuzzy neural network (FNN), have been investigated without the requirements of an accurate mathematical model[34-38]. An adaptive fuzzy control approach was developed for keeping track of the reference dissolved oxygen concentration[36]. The control law, derived from the fuzzy rules, can exhibit robustness to the uncertainties in the biochemical reactions. Lin et al. developed a neural adaptive controller to regulate the aeration unit in BWWTP[37]. This neural adaptive controller approximated unknown dynamics using a radial basis function NN. The results demonstrated that the tracking performance was improved despite the uncertain dynamics. Moreover, an integrated neural-fuzzy controller was proposed for an aerated submerged biofilm BWWTP[38]. A self-learning method in the FNN model improved uncertainty estimates. The results revealed that this integrated neural-fuzzy controller can achieve suitable robustness and accuracy. In addition, several advanced intelligent control approaches have been established to estimate uncertainty (e.g., the rough set-based hybrid fuzzy-neural controller[39], adaptive fuzzy neural controller[40], hybrid fuzzy-neural soft-sensing model-based control[41], and so on). However, there are some problems worth discussing, which are listed as follows.
Consequently, the primary goal is to provide an effective technique to address the aforementioned issues. In this article, a robust multivariable tracking control method (RMTC), consisting of the direct controller and the approximate controller, is developed to suppress the influence of external disturbances and approximation errors derived from the uncertainties of BWWTP. This method will enhance the entire system's robustness and assure effective tracking performance. The main contributions contain the following parts.
(1) A system transformation method combining Taylor series expansion and nominal control law is proposed to address the nonaffine nonlinear characteristics of the BWWTP. This method can directly convert the nonaffine nonlinear system into a standard affine nonlinear system without complex derivation or additional design. This not only avoids additional design errors caused by complex calculations but also simplifies the design process of subsequent control strategies.
(2) A novel RMTC scheme is designed, which consists of a direct controller and an approximate controller. The direct controller is constructed based on SMC, which can directly obtain the control law without prior knowledge of external disturbances or assumptions about the derivative of disturbances. The approximate controller adopts a self-organizing fuzzy neural network (SOFNN), which precisely balances empirical error and structural complexity through an optimized structural risk strategy to guide the addition and pruning of fuzzy rules. It effectively avoids the rule redundancy or insufficiency in fixed-structure networks. Unlike the common nonlinear model predictive control (NMPC), this method does not rely on an accurate predictive model for rolling optimization. Instead, it effectively estimates system uncertainties and handles disturbances through the collaboration of the two controllers, thereby improving the overall control robustness.
(3) An adaptive strategy is integrated into RMTC to dynamically adjust the control gain and parameters of the FNN. This strategy can balance the steady-state control performance of the direct controller and the approximate controller under different operating conditions of BWWTP by suppressing approximation errors and external disturbances. Meanwhile, it effectively avoids severe chattering problems while ensuring the steady-state tracking error converges to zero asymptotically.
Finally, the closed-loop stability of RMTC is thoroughly delineated according to Lyapunov stability theory. Then, the sufficient conditions and parameters of RMTC can be provided to ensure successful applications.
This work is organized into the following areas. Section 2 succinctly delineates the dynamics of BWWTP, including external disturbances and uncertainties. Then, the scheme of RMTC, adaptive strategy, and the stability discussion are given in Section 3. Several practical applications are used to assess the efficacy of the suggested strategy in Section 4. Section 5 presents the conclusion.
2. PROCESS DESCRIPTION
2.1. Dynamical model of BWWTP
The objective of BWWTP is to diminish the quantity of organic matter, nitrogen, phosphorus, and suspended solids to render the wastewater clean. Figure 1 displays the BWWTP schematic view, including three compartments and one settler.
The first compartment serves as an anaerobic zone for the denitrification of returning sludge (external recycle) from the secondary settler. The second compartment offers an anaerobic environment for the denitrification of nitrite/nitrate recirculation from the preceding aerobic chamber. This compartment regulates the peristaltic pumps to control the intake, mixed liquor flow, and return sludge flow. The third compartment serves as an aerobic zone for the decomposition of organic waste into inorganic matter, using air pumps to provide oxygen. Furthermore, a dependable control system regulates effluent quality at the appropriate stations by managing aeration and sludge recycling flow rates.
The process of BWWTP is inherently complicated, nonlinear, and characterized by significant disruptions and uncertainty. The dynamic model of BWWTP may be articulated as follows[42]
where
where
2.2. External disturbances and uncertainties
External disturbances are widespread in the BWWTP, such as the changes in influent flow rate, the unknown noise of sensors, and so on [7]. They are regarded as the combinations of unknown external disturbances. Correspondingly, the unknown
Notably, the external disturbances and uncertainties also exist not only in BWWTP simultaneously but also in other similar fields that have bioprocesses, chemical processes, biochemical processes, etc. The challenge of the control for these fields is to reject the disturbances and further ensure acceptable performance.
3. PROCESS DESCRIPTION
The scheme of RMTC, the direct controller, the approximate controller, the adaptive strategy, and the discussion of stability are presented in the subsequent sections.
3.1. Scheme of RMTC
As shown in Figure 2, the proposed RMTC, including a direct controller and an approximate controller, as well as the adaptive technique, is recommended to achieve the strong performance of BWWTP.
In this RMTC, a direct controller and an approximate controller are designed with different control targets separately. The direct controller is designed to mitigate external disturbances caused by varying environmental conditions and inflow loads. The approximate controller is developed to compensate for the uncertainties by using a SOFNN. Then, by alleviating the influence of external disturbances and approximation errors, an adaptive strategy for balancing the performance of direct and approximate controllers is introduced to optimize the control gain and adjust the parameters of RMTC to hold the steady-state control performance under different operational conditions.
For RMTC, the tracking error
where
To simplify Equation 4, there is
where
and
where
where
Remark 1: In order to avoid the complicated derivations and extra designs for its nonaffine counterpart, the system of BWWTP is transformed into a normal affine nonlinear form. As a result, there is the remainder of Taylor expansion in this step, which may bring deviation for control of BWWTP. Therefore, the control law in this work is decomposed and further obtained with a direct controller and an approximate controller. An approximate control has another role that compensates for the remainder derived from the uncertainties.
Remark 2: The two expressions of
3.2. Direct controller
The SMC serves as a proficient instrument for nonlinear systems, which is insensitive to external disturbances in the whole control period[23]. Consequently, the direct controller is designed with SMC. The control law of direct controller is given as:
where
where
where
According to the theory of SMC, a Lyapunov candidate function is selected as
Differentiating Equation 13 with respect to time
When the system maintains stability according to the Lyapunov theorem, there is
3.3. Approximate controller
It can be seen from Equation 13 that it is necessary for the controller to obtain an ideal
where
Then,
where
where
where
The structure of NN or FNN in previous studies associated with the design of the controller is always predefined with prior knowledge or trials and errors. Besides, it also maintains constant except for the parameters of the controller updated by adaptive laws. This fact may lead to inaccurate approximation for BWWTP with obvious dynamics and serious disturbances due to mismatched fuzzy rules.
As to FNN, it needs enough fuzzy rules to cover the dynamics of systems, which also brings the risk of structural redundancy. Therefore, the choice of fuzzy rules without prior knowledge is difficult. To deal with the challenge, there are two criteria, i.e., its empirical error and structural complexity associated with its performance that can be used for optimizing the FNN's structure. The empirical error is
where
where
To achieve accurate approximation and compact structure, it is critical to find the optimal
Different from the parameters shown in Equation 19, the update of the fuzzy rules number is discrete. It is challenging to conduct when the output should be smooth and stable. To remove this obstacle, a continuous function
This derivative reflects the impact of fuzzy rules number on the FNN's performance. It can be employed to direct the update of fuzzy rules. Then, the SOFNN is built as:
(1) Adding Fuzzy Rule: When the derivative satisfies
where
where
(2) Pruning Fuzzy Rule: If the derivative meets
where
where
Remark 3: The criterion[25] is introduced to evaluate the effectiveness of fuzzy rules. It is used to optimize the number of fuzzy rules by balancing the approximation error and structure complexity. With a compact structure, FNN's generality will be enhanced during approximation for BWWTP, which can strengthen the robustness of RMTC.
3.4. Adaptive strategy
To accomplish the optimization of parameters in Equation 19 an adaptive strategy is developed to obtain adaptation laws of parameters
where
The time derivative of \(V_2(t) \) is
Combining with Equation 9, Equation 10, and Equation 14, it has
Based on Equation 16 and Equation 18, the estimated error
where
and
Substituting Equation 31 into Equation 30, Equation 30 can be rewritten as
The adaptation laws of parameters are thus selected as
Taking Equation 35, Equation 36, and Equation 37 into Equation 34 yields
Applying Equation 11, if it satisfies that \(\upsilon > \|\dot{\mathbf{x}}_d(t)\|\) and \(\upsilon > \|\boldsymbol{\Delta}(t)\|\), it has
Based on Equation 39,
where
A feasible point
where \(i = 1, 2, \dots, n\). \(\varsigma^*(t) = \arg\min_{\varsigma^*(t) \in \Omega_f} \mathbf{J}(t)\) the optimal solution \(\varsigma^*(t)\) is over the compact set \(\Omega_f \in \Re\). The gradient algorithm is used to deal with this optimization problem. The derivative of \(\mathbf{J}(t)\) is given as
From Equation 8, it will be \(\frac{\partial \mathbf{u}(t)}{\partial \varsigma(t)} = [\lambda \frac{\partial \mathbf{e}(t)}{\partial \varsigma(t)} - \mathbf{u}_{ad}(t)] / v\). Equation 41 can be rewritten as
The minimization of
where
Suppose that
Figure 3 provides a summary of the primary RMTC steps.
Remark 4: For this proposed RMTC, the high control accuracy with suitable approximation performance can be obtained by felicitously adjusting the adaptive parameter
Remark 5: At the initial moment of the control system, the controller has not yet begun dynamic adjustment. At this moment, the tracking error
3.5. Stability analysis of RMTC
For the proposed RMTC, the stability of the control law is a critical topic that requires thorough examination, since it is essential for successful applications. The stability of the proposed controller is analyzed with sufficient conditions and parameters selection method.
Theorem. Consider the system given as Equation 2 with the control law as Equation 9. Suppose the number of fuzzy rules is \(h \), and the structure of SOFNN is adjusted according to Equation 25, Equation 26, Equation 27, and Equation 28, and its parameters are selected with Equation 36, Equation 37, and Equation 38. Besides, assume the following condition holds
where \(\kappa_1 = e^{\frac{1}{2} \big(\sqrt{l(n)} + 1 - \sqrt{l(n)} \big) \sqrt{o \log n}}\), and \(\kappa_2 = e^{\frac{1}{2} \big(\sqrt{l(n)} - \sqrt{l(n) - 1} \big) \sqrt{o \log n}}\). Then, the stability of RMTC under disturbances can be guaranteed.
Proof. The candidate Lyapunov function is considered as follows
where
where
Correspondingly, during the phase of fuzzy rule addition, the variation of structural complexity is
With the condition of Equation 47, Equation 51 satisfies
Besides, once a fuzzy rule is pruned, the variation of structural complexity will be
According to the agreement between
where
Therefore, the difference of Lyapunov function
By substituting Equation 36, Equation 37, Equation 38, Equation 51 and Equation 54 into Equation 55, it will be
Note that
where
From \(t = 0 \) to \(t = n \), it will be
Because of \(V_1(T) \geq 0 \) and \(\|\mathbf{d}_\mathrm{ext}(t)\| \leq \varepsilon_d \), it will be
It can be seen that the right side of Equation 60 is bounded since \(V_1(0) \), \(\|\boldsymbol{\Delta}(t)\| \), and \(\|\dot{\mathbf{x}}(t)\| \) are all finite. It will be
By using Barbalat's lemma, Equation 61 shows that the global stability of RMTC is guaranteed by the Lyapunov theorem if and only if the condition in Equation 47 holds. Consequently, the control system exhibits asymptotic stability. Furthermore, \(\mathbf{e}(t)\) will approach zero in accordance with SMC theory.
Remark 6: In RMTC, the disturbance bound
Remark 7: In distributed control architectures at large-scale WWTPs, RMTC faces challenges with computational load and inter-unit coordination. These challenges can be addressed through the following two approaches. Firstly, an adaptive event-triggering strategy can be designed based on the approximation error of SOFNN and the state error of the RMTC system[43]. This strategy dynamically adjusts thresholds to reduce the frequency of SOFNN parameter updates and communication between processing units, thereby alleviating overall computational and transmission loads. Secondly, each processing unit can be treated as an intelligent agent. A predefined time Nash equilibrium search architecture can be introduced into RMTC under an unbalanced directed graph[44]. This method dynamically solves the Nash equilibrium between subsystems using a predefined time estimator and achieves global coordination through neighborhood information exchange. Meanwhile, this method maintains the robustness of RMTC against external disturbances and the uncertainty compensation ability of SOFNN. Finally, combining the Lyapunov method ensures the stability of the distributed closed-loop system, thereby achieving efficient and robust collaborative control at the plant level.
4. ILLUSTRATED EXAMPLES
4.1. Experiment setup
To illustrate that the RMTC method is applicable, a small-scale experiment platform was built according to an actual BWWTP. The main purpose of establishing a small-scale experimental platform is to evaluate and validate the efficacy of RTMC techniques in actual wastewater treatment plants. The experimental platform is built based on the actual BWWTP. Its core control system includes an inverse sludge control system and an aeration control system, which manage the operation of the return sludge pump and air pump respectively. An industrial control computer (Pentium 4 processor with a frequency of 2.6 GHz) serves as the control core, integrating modules such as monitoring, display, list, report, operation, and printing to coordinate the entire control process and handle data. The platform is equipped with drive motors, which are responsible for closed-loop control execution, I/O data acquisition, alarm setting, and network communication. Among them, the air pump controlled by the drive motor is specifically used to regulate the dissolved oxygen concentration in the aerobic zone, ensuring it stays within the target range. All components work together to achieve precise control of the wastewater treatment process. The proposed tracking control algorithm is programmed with MATLAB version 7.01 and was run on a Pentium 4 with a clock speed of 2.6 GHz and 1 GB of RAM, under a Microsoft Windows XP environment. The control system would regulate SNO and So at desired levels. The sampling interval was fixed at 15 min, and the system executed the control actions with a time step of 2 h.
Several common indices will be used to assess the effectiveness of RMTC:
(1) \(E_{IA} = \frac{1}{T} \int_0^T |e_t(t)| dt \, (\text{mg/L}) \), the integrated absolute errors (mg/L), where \(T \) represents the sampling size of the concerned experimental segment.
(2) \(E_{ISD} = \frac{1}{T} \int_0^T |e_t(t)|^2 dt \, (\text{mg/L}) \), the integrated square differential errors over the concerned experimental segment.
(3) \(U_{rms} = \left(\frac{1}{T} \int_0^T |u_t(t)|^2 dt \right)^{1/2} \, (\text{mg/L}) \), the root mean square value.
4.2. Experimental results
Case Ⅰ: In case Ⅰ, the data of 24 h are used to perform the control of aeration and sludge recycle flow rate. The sensor noise in the third aerobic compartment is changed from 0 to 0.1 mg/L.
The set-point changes of
Figure 4. (A) Tracking the performance of SO in case Ⅰ; (B) Tracking the performance of SNO in case Ⅰ.
Figure 5. (A) (a) The dynamic of KLa5 (m3/h); (b) The dynamic of KLa5 (m3/h) using direct controller; (c) The dynamic of KLa5 (m3/h) using approximate controller. (B)(a)The dynamic of Qinter (m3/h); (b)The dynamic of Qinter (m3/h) using direct controller; (c)The dynamic of Qinter (m3/h) using approximate controller.
From the graphics in Figure 4, the behavior of the whole system using RMTC is observable (purple line), it is very close to the set points (black line). The control errors of RMTC can be achieved within a small region. In Figure 4, the outputs of RMTC can track the set points too. The curves of control errors of
To assess the efficacy of RMTC, its findings are compared with several pioneering works including, the SMC[19], the SMC based on a disturbance observer (SMOC)[28], the NMPC[45], the SMC based on a fuzzy neural network observer (SMCFNO)[34], and the observer-based sliding mode controller with self-structuring FNN (SFNN) identifier (OFNSMC)[35]. The parameters, including the control gains and initial structure of these control methods, are the same as RMTC. Other parameters are defined as in the original paper. The statistical analysis of RMTC and the other controllers is given in Table 1.
The comparison of tracking performance
Controller | |||||||||
Num. | Num. | ||||||||
RMTC | 9 | 0.018 | 0.032 | 0.31 | 8 | 0.013 | 0.028 | 44.9 | |
SMC[19] | - | 0.728 | 0.117 | 0.78 | - | 0.861 | 0.980 | 82.3 | |
SMOC[28] | - | 0.232 | 0.058 | 0.53 | - | 0.292 | 0.049 | 51.2 | |
NMPC[45] | - | 0.021 | 0.039 | 0.45 | - | 0.614 | 0.613 | 82.8 | |
SMCFNO[34] | 12 | 0.031 | 0.053 | 0.47 | 10 | 0.123 | 0.044 | 51.7 | |
OFNSMC[35] | 11 | 0.027 | 0.049 | 0.46 | 10 | 0.051 | 0.035 | 49.7 |
Compared to SMCFNO and OFNSMC, the proposed RMTC achieves the most compact structure. The smallest
Case Ⅱ: The data of the last 48 hours, including the dry and rain conditions, are used to perform the control of aeration and sludge recycle flow rate. The disturbances contain the rain events, as well as the decreasing nitrification and denitrification.
The rain event is at 9:00 on the second day. The decreasing nitrification is denoted by the specific growth rate of autotrophs which changes from 0.5 to 0.63 day
The initial structure of SOFNN is 2-6-6-2. The initial value
Figure 7. (A) Tracking the performance of SO in case Ⅱ; (B) Tracking the performance of SNO in case Ⅱ.
Figure 8. (A) (a) The dynamic of KLa5 (m3/h); (b) The dynamic of KLa5 (m3/h) using direct controller; (c) The dynamic of KLa5 (m3/h) using approximate controller. (B)(a)The dynamic of Qinter (m3/h); (b)The dynamic of Qinter (m3/h) using direct controller; (c)The dynamic of Qinter (m3/h) using approximate controller.
In addition, the comparison of RMTC with other controllers is given in Table 2. The smallest \(E_{IA}\), \(E_{ISD}\), and \(U_{rms}\) in Table 2 indicate that the tracking performance of RMTC is superior among these methods. Although the accuracy and stability are influenced by the rain event, uncertainties, sensor noise, and set-point changes, the output of RMTC remains precise and stable with the least fuzzy rules. In addition, because the set points are maintained well, the smallest \(E_{IA}\) and \(E_{ISD}\) in Table 2 demonstrate that RMTC has a preferable response. Consequently, RMTC exhibits superior control performance in dynamic aeration and sludge recycling compared to other approaches.
The comparison of tracking performance
Controller | |||||||||
Num. | Num. | ||||||||
RMTC | 10 | 0.058 | 0.047 | 0.21 | 9 | 0.014 | 0.017 | 42.9 | |
SMC[19] | - | 0.663 | 0.532 | 0.69 | - | 4.361 | 3.488 | 105.0 | |
SMOC[28] | - | 0.263 | 0.218 | 0.56 | - | 0.434 | 0.508 | 82.5 | |
NMPC[45] | - | 0.119 | 0.098 | 0.32 | - | 0.528 | 0.711 | 79.7 | |
SMCFNO[34] | 14 | 0.108 | 0.105 | 0.47 | 12 | 0.137 | 0.404 | 64.8 | |
OFNSMC[35] | 12 | 0.076 | 0.048 | 0.35 | 11 | 0.047 | 0.103 | 50.1 |
Case Ⅲ: In this case, the data of the last 72 h is used to analyze the control of aeration and sludge recycle flow rate. The influent disturbances include the rain and storm events, the decreasing nitrification and the decreasing denitrification, as well as the set-point changes and measurement noises.
The rain and storm events are launched from 9:00 to 20:30 on the second day, respectively. The decreasing nitrification and the decreasing denitrification are shaped according to case Ⅱ. The set-points are provided the same as in case Ⅰ.
The random measurement noises are set to the range of
The experiment results are presented in Figure 10, Figure 11 and Figure 12. Figure 10 shows that the curves of
Figure 10. (A) Tracking the performance of SO in case Ⅲ; (B) Tracking the performance of SNO in case Ⅲ.
Figure 11. (A) (a) The dynamic of KLa5 (m3/h); (b) The dynamic of KLa5 (m3/h) using direct controller; (c) The dynamic of KLa5 (m3/h) using approximate controller. (B)(a)The dynamic of Qinter (m3/h); (b)The dynamic of Qinter (m3/h)using direct controller; (c)The dynamic of Qinter (m3/h) using approximate controller.
The details of the comparisons in terms of
The comparison of tracking performance
Controller | |||||||||
Num. | Num. | ||||||||
RMTC | 10 | 0.038 | 0.037 | 0.191 | 9 | 0.017 | 0.052 | 31.4 | |
SMC[19] | - | 0.812 | 0.552 | 0.572 | - | 0.705 | 0.943 | 51.8 | |
SMOC[28] | - | 0.154 | 0.107 | 0.491 | - | 0.473 | 0.504 | 42.1 | |
NMPC[45] | - | 0.087 | 0.065 | 0.262 | - | 4.870 | 2.551 | 66.3 | |
SMCFNO[34] | 15 | 0.231 | 0.099 | 0.459 | 13 | 0.150 | 0.150 | 41.2 | |
OFNSMC[35] | 11 | 0.069 | 0.066 | 0.350 | 12 | 0.056 | 0.103 | 39.8 |
4.3. Analysis of experimental results
The experiments are performed to demonstrate the viability of RMTC for WWTP. The dynamic nature of WWTP is characterized by diverse physical and biological processes with significant external disturbances, complicating the regulation of
5. CONCLUSIONS
In this study, an RMTC is designed to realize an effective control performance for BWWTP. The outcomes of experiments have shown that RMTC is effective. The results show that RMTC performs better than other control methods. The accuracy and smoothness of control output can be improved for the BWWTP. The details can be summarized as follows:
(1) This proposed RMTC can provide a framework to improve the robust performance for tracking multiple variables. This control strategy can obtain good robustness for both the external disturbances and uncertainties of BWWTP.
(2) The control gain of RMTC, adjusted by an adaptive strategy with both the direct controller and the approximate controller, can maintain the steady-state control performance under different operational conditions.
(3) Sufficient conditions and parameters are provided for RMTC based on the stability analysis, which allows the proposed RMTC to be applied in the real BWWTP. Experimental experiments demonstrate that RMTC is an effective instrument for BWWTP.
Furthermore, the proposed RMTC will be applied to different kinds of BWWTP and other fields.
DECLARATIONS
Acknowledgments
The authors would like to express our great appreciation to the editors and reviewers.
Authors' contributions
Made substantial contributions to conception and design of the study and performed data analysis and interpretation: Wu, X.; Han, W.; Yang, H.; Han, H.
Performed data acquisition and provided administrative, technical, and material support: Qiao, J.; Peng, X.
Availability of data and materials
The experimental dataset supporting this study can be obtained from "Benchmark simulation model no. 1 (BSM1)". The implementation of BSM1 is available here: https://portal.research.lu.se/en/publications/benchmark-simulation-model-no-1-bsm1.
Financial support and sponsorship
This work was supported by National Science Foundation of China under Grants 62422301, 62125301, 62021003, and 62103011, Beijing Natural Science Foundation under Grants L253010, National Key Research and Development Project under Grants 2022YFB3305800-05, and Youth Beijing Scholar under Grant No. 037.
Conflicts of interest
Han, H. is Editorial Board Member of the journal Complex Engineering Systems. Han, H. was not involved in any steps of editorial processing, notably including reviewers' selection, manuscript handling and decision making, while the other authors have declared that they have no conflicts of interest.
Ethical approval and consent to participate
Not applicable.
Consent for publication
Not applicable.
Copyright
© The Author(s) 2025.
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