# Design of a fuzzy differential evolution algorithm to predict non-deposition sediment transport

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## Abstract

Since the flow entering a sewer contains solid matter, deposition at the bottom of the channel is inevitable. It is difficult to understand the complex, three-dimensional mechanism of sediment transport in sewer pipelines. Therefore, a method to estimate the limiting velocity is necessary for optimal designs. Due to the inability of gradient-based algorithms to train Adaptive Neuro-Fuzzy Inference Systems (ANFIS) for non-deposition sediment transport prediction, a new hybrid ANFIS method based on a differential evolutionary algorithm (ANFIS-DE) is developed. The training and testing performance of ANFIS-DE is evaluated using a wide range of dimensionless parameters gathered from the literature. The input combination used to estimate the densimetric Froude number (*Fr*) parameters includes the volumetric sediment concentration (*C* _{ V }), ratio of median particle diameter to hydraulic radius (*d/R*), ratio of median particle diameter to pipe diameter (*d/D*) and overall friction factor of sediment (*λ* _{ s }). The testing results are compared with the ANFIS model and regression-based equation results. The ANFIS-DE technique predicted sediment transport at limit of deposition with lower root mean square error (RMSE = 0.323) and mean absolute percentage of error (MAPE = 0.065) and higher accuracy (*R* ^{2} = 0.965) than the ANFIS model and regression-based equations.

## Keywords

ANFIS Bed load Differential Evolution (DE) Non-deposition Pipe Sediment transport## Introduction

A significant concern regarding sediment transport with inflow is solid matter deposition in the pipe channel. It is essential to determine the limiting velocity (at a constant slope) in dry weather flow (DWF) for sediment transport without deposition. Moreover, the pipe diameter should be sufficiently capable of transporting maximum flow in wet weather flow (WWF). Sedimentation can increase the bed roughness and decrease the cross-sectional area of the channel. The long-term accumulation of sediment on the bed can increase the risk of stabilization and cementation, thus causing transport capacity reduction. Therefore, a criterion for predicting the limiting velocity to prevent sediment deposition is essential.

The simplest traditional method is to use a constant limiting velocity value provided in many references for different hydraulic and geographical situations (see more details in Ebtehaj et al. 2014). This method is inaccurate in some circumstances because the values do not consider hydraulic and sediment characteristics, such as pipe diameter, flow depth, hydraulic radius, median particle diameter and volumetric sediment concentration.

*C*

_{ V }is the volumetric sediment concentration,

*D*is the pipe diameter,

*d*is the median particle diameter,

*V*is the flow velocity,

*V*

_{ t }is the incipient motion velocity of sediment (Eq. 2),

*A*is the cross-sectional area of the flow,

*g*is the gravitational acceleration,

*s*(=

*ρ*

_{ s }

*/ρ*) is the specific gravity of sediment and

*y*is the flow depth.

*Fr*) by dimensional analysis with a wide range of data as follows:

Because artificial intelligence (AI) performs adequately (Gholami et al. 2011; Al-Abadi 2014; Gorai et al. 2014; Mondal et al. 2015), techniques such as neural networks (Ebtehaj and Bonakdari 2013), decision trees (Ivanovich and Hamid 2014), fuzzy logic (Demirci and Baltaci 2013), evolutionary computing (Ebtehaj and Bonakdari 2016), and gene expression programming (Ab Ghani and Azamathulla 2014) have been successfully applied in sediment transport modeling. Shoorehdeli et al. (2007) developed a new hybrid particle swarm optimization (PSO) algorithm for ANFIS network training. The authors modified the PSO for the training scheme in the antecedent part of the fuzzy rules, inspired by the genetic algorithm and using adaptive weighted by PSO. They demonstrated that the new ANFIS is less complex and more accurate than the gradient-based method in ANFIS training.

Moosavi et al. (2013) applied hybrid models based on Wavelet, Wavelet-ANFIS and Wavelet-ANN for groundwater level forecasting during different prediction periods. The results of ANFIS, Wavelet-ANFIS, ANN and Wavelet-ANN indicated that the hybrid methods exhibit superior precision to both ANFIS and ANN, while Wavelet-ANFIS performs the best of all models. Ebtehaj and Bonakdari (2014b) optimized the MLP-ANN weights in sediment transport prediction using two evolutionary algorithms (EA): the imperialist competitive algorithm (ICA) and genetic algorithm (GA). A comparison of the hybrid methods (ANN-ICA and ANN-GA) with the general ANN indicated that EA performs significantly better than ANN.

Ebtehaj and Bonakdari (2014a) evaluated the ANFIS performance in predicting sediment transport. The authors recommended applying evolutionary algorithms for the optimum selection of ANFIS membership functions. Therefore, in this study, ANFIS is coupled with the DE algorithm for the first time to develop a hybrid model and assess sediment transport in sewers. The main goal is to increase prediction accuracy and reliability by benefiting from the specific nature of each approach. The DE algorithm is applied to optimize the membership function of the ANFIS network using three datasets with a wide range of data. The parameters affecting limiting velocity (i.e. *Fr*) prediction are identified initially by examining the influential factors on sediment transport. Thereafter, six models are proposed to assess the effect of different parameters on *Fr* prediction. The developed ANFIS-DE model predictions are compared with the ANFIS model as well as existing sediment transport equations.

## Theoretical background of the method used

### Overview of ANFIS

*x*and

*y*) and

*f*as an output is an example of this process. For sediment transport in pipe channels, the

*x*and

*y*parameters are considered the volumetric sediment concentration (

*C*

_{ V }) and a dimensionless parameter (the ratio of hydraulic radius to median particle diameter

*d/R*). Moreover,

*F*as an output parameter represents the

*Fr*function. This example is examined for two input parameters. For a first-order Takagi–Sugeno fuzzy model, it is possible to set a sample rule with two IF–THEN rules as follows:

*C*

_{ V }and

*d/R*are considered

*Fr*model input variables, Eqs. 1 and 2 can be rearranged as follows:

*p*

_{ i },

*q*

_{ i }and

*r*

_{ i }(

*i*= 1, 2, 3,…,

*n*) are the set of parameters. Figure 1 presents the overall structure of ANFIS with two inputs and ANFIS with four inputs used in this study. The performance of the different layers shown in this figure is as follows:

*First layer*Each node in this layer produces the membership degree from an input variable.

*C*

_{ V }is the input of the

*i*th node and

*A*

_{ i }is the linguistic label related to this node’s function. For

*d/R*(the second input parameter), another function can be derived as in Eq. 9:

*O*

_{ i }

^{1}is regarded as the membership function

*A*

_{ i }(MF) and it determines the degree that satisfies a given input (

*C*

_{ V }or

*d/R*) to the

*A*

_{ i }quantity. These functions are smooth and have concise notation; for this reason, the most accepted membership functions in ANFIS are deemed to be the Gaussian and bell shape functions (Bui et al. 2012). Both have the advantages of smoothness and being non-zero at all points. The bell shape MF (Eq. 10) has a greater parameter than the Gaussian MF (Eq. 11); as a result, it can approach the non-fuzzy set if the free parameter is tuned (MATLAB and Statistics Toolbox Release 2009). Therefore, the Gaussian MF is employed in this study.

*a*

_{ i }

*, b*

_{ i }

*, c*

_{ i }

*and σ*

_{ i }} is the parameter set of Gaussian MFs and

*μ*is the MF of

*A*

_{ i }. Changing any of the parameters leads to different MF results. Hence, representing different forms of MFs is dependent on the linguistic label

*A*

_{ i }. In fact, many of the piecewise and continuous functions in this node may be used. The parameters of this layer are introduced as premise parameters. Three membership functions are derived for each input model presented in Fig. 2.

*Second layer*This layer consists of circular nodes marked with П. The following equation is multiplied by the input signal and these nodes are sent to the output produced:

*Third layer*Here, circular nodes (Ns) calculate the ratio of the firing strength rule (

*i*th rule) to the sum of all firing strength rules, as follows:

*Fourth layer*The parameter values of

*p*,

*q*and

*r*are optimized in this layer. All nodes in this layer adapt to a node function as follows:

*p*

_{ i }

*, q*

_{ i }

*, r*

_{ i }} is the parameter set and \(\bar{w}\) is the normalized weight. The parameters in this layer are known as consequent parameters.

*Fifth layer*The circular single node in this layer, Σ, and all outputs are calculated as the sum of all input signals as:

Ebtehaj and Bonakdari (2014a) showed that the hybrid algorithm presents better results than backpropagation. Hence, this algorithm is employed in the present study to estimate *Fr* with the ANFIS network. In addition to these algorithms, the more recent use of hybrid ANFIS has led to improved ANFIS prediction results (Cus et al. 2009; Shoorehdeli et al. 2009; Chang et al. 2011; Chen 2013; Bui et al. 2016a, 2017b). Therefore, Differential Evolution (DE) is employed in this study and the results are compared with the hybrid algorithm results.

### Differential evolution

Differential evolution (DE) is a powerful evolutionary global optimization method that was proposed by Storn and Price (1997). The advantages of DE are its simple structure, quality of solutions found, and ease of implementation (Liu and Lampinen 2002; Bui et al. 2016b). Thus, it has been applied in many different practical cases. EA is grouped as an optimization stochastic algorithm and is inspired by biological processes, whereby survival of the fittest is required for compliance with environmental and inherent genetic features (Bäck et al. 1997).

*f*, we have:

*R*is related to real data and

*D*represents the objective function parameters

*f*(

*V*). The DE algorithm aims to minimize the objective function using the optimized parameter values:

*V*is a vector including the parameters of the objective function of

*D*. The objective function is the mean squared error between the actual and estimated

*Fr*. The objective function parameters are defined as follows:

*v*

_{ i }

^{(L)}and

*v*

_{ i }

^{(U)}are related to the lower and upper boundaries, respectively.

*P*

_{ G }) of candidate solutions and not only on a single solution. If

*G*is considered the generation of a population, the population evaluated by DE can be stated as follows:

*G*

_{max}is the maximum generation that usually serves as the stopping criterion of DE (Bui et al. 2016b). Each vector contains the exact parameter of

*D*considered an individual chromosome.

*P*

_{ G }= 0, is the random selection of restrictions given as follows:

_{ j }[0, 1] is a random value distributed consistently in the [0, 1] range, which is selected for every new

*j*. The DE procedure differs from other evolutionary algorithms. From the primary production to the regular population of vectors,

*P*

_{ G }is combined and sampled randomly to produce candidate vectors for the next generation,

*P*

_{ G + 1}.

*U*

^{ iG+1}=

*u*

_{ j },

_{ I, G + 1}, is calculated as follows:

*r*

_{ 1 },

*r*

_{ 2 }and

*r*

_{ 3 }are values that differ in each run and

*i*is a parameter whose value should be specified. The correct values of parameters

*r*

_{ 1 },

*r*

_{ 2 }and

*r*

_{ 3 }are randomly selected for each

*i*value.

*P*

_{ G + 1}, is selected from the current population (

*P*

_{ G }) and the population of children follows this equation:

Thus, the temporary population of individuals is compared with their peers’ population. Assuming the objective function is minimized, the vector with the lowest objective function value gains a new position in the next generation. As a result, every individual from the next population is good or better than peers from the general population.

### Statistical measure

*R*

^{2}), Root Mean Squared Error (RMSE), Mean Absolute Error (MAE), Mean Absolute Relative Error (MARE) and average absolute deviation (δ).

## Methodology

*R*is the hydraulic radius,

*y*is the flow depth,

*d*is the median particle diameter,

*C*

_{ V }is the volumetric sediment concentration,

*A*is the cross-sectional area of the flow,

*g*is the gravitational acceleration,

*ρ*is the water density,

*ρ*

_{ s }is the sediment density,

*λ*

_{ s }is the overall friction factor of sediment,

*Fr*is the densimetric Froude number,

*s*is the specific gravity of sediment (=

*ρ*/

*ρ*

_{ s }),

*D*

_{gr}(=

*d*(

*g*(

*s*

*−*1)

*/ν*

^{ 2 })

^{ 1/3 }) is the dimensionless particle number and

*D*is the pipe diameter.

In some recent studies, Ebtehaj and Bonakdari (2013; 2014a; 2014b; 2016) classified the dimensionless parameters presented in the above equation with respect to the nature of each parameter in the dimensionless groups of transport (*C* _{ V }), transport mode (*d/R*, *D* ^{ 2 } */A* and *R/D*), flow resistance (*λ* _{ s }), movement (*Fr*) and sediment (*D* _{gr} and *d/D*).

*Fr*parameter is the target selected to estimate the limiting velocity parameter. By considering the effect of each of the following categories, four inputs are derived for the models. The inputs obtained from “transport “and “flow resistance” are constant, while “sediment” and “transport mode” have more than one parameter. Hence, different models are presented to investigate the effect of each parameter, as follows:

## The study site and data used

In this study, three datasets are used to predict sediment transport in the non-deposition condition in pipe channels (Ab Ghani 1993; Ota and Nalluri 1999 and Vongvisessomjai et al. 2010). The data employed in this study are all associated with non-deposition in different hydraulic conditions, such as pipe diameter, channel slope, particle size and channel length. Details of the datasets are provided in studies carried out by Ebtehaj et al. (2014) and Ebtehaj and Bonakdari (2014a, b(. The samples are in the following ranges: 1 <*C* _{ V } (ppm) <1280; 0.005 < *R* (m) < 0.136; 0.013 < *λ* _{ s } < 0.053; 0.1 < *D*<0.45; 0.237 < *V* (m/s) < 1.216; 0.072 < *d* (mm) < 8.3; 0.153 < *y/D* < 0.84 and 5.06 < *D* _{gr} < 142.

## Proposed hybrid method for non-deposition sediment transport prediction

This section describes the hybrid comprising ANFIS and a global optimization method, i.e. Differential Evolution (ANFIS-DE). ANFIS-DE is used for modeling sediment transport at limit of deposition in sewer networks. The proposed ANFIS-DE is encoded in MATLAB Environmental. First, an initial ANFIS model is produced for the sediment transport data using the training dataset. Subsequently, DE is utilized to optimize the premise and consequent parameters of the model. Once the optimum parameter values are determined, the ANFIS-DE regression model is acquired and it can be used to predict the limiting velocity for non-deposition sediment transport in sewer systems.

### Data preparation

The data utilized in this study are arranged as four inputs and one output parameter (*Fr*). To present a useful predictive model with scientific significance, model validation is essential in the analysis. Therefore, all datasets collected from the literature are divided in two subsets at a ratio of 70–30 for training and testing. The training dataset comprised 150 samples that were selected randomly, whereas the rest of the samples (68) were utilized for testing to confirm the prediction accuracy of the proposed model.

### Model configuration

DE control parameters

Number of dimensions | | 4 |
---|---|---|

Population size | NP | 20 |

Mutation constant | F | 0.5 |

Crossover constant | CR | 0.9 |

parameters; boundaries | | 12 |

( | | −12 |

### ANFIS model training using PSO

First, to avoid expansion process duplication, the values of the objective function and constraint functions for parameter *V* _{ i,G } are stored in the variables. *U* _{ i, G + 1} refuses constraint function values greater than the *V* _{ i,G } value and rejects these constraint functions without reassessment. If *V* _{ i,G } is not convinced of all constraints, *U* _{ i,G + 1} probing is done because the constraint is still much less than *V* _{ i,G }. As the *U* _{ i,G + 1} and *V* _{ i,G } values are searched, the membership function to probe the new *U* _{ G + 1} should be evaluated. This practice continues until the value of *U* _{ i,G + 1} becomes greater than *V* _{ i,G }. In this case, the membership function value is not evaluated once more.

### Stopping criteria

The maximum number of iterations and minimum defined error are utilized as stopping criteria, such that if one of the conditions is satisfied the optimization process in terminated. In this case, the objective function defined as RMSE (Eq. 25) is the smallest and the antecedent and consequent parameters are assigned to the ANFIS-DE model. The validation dataset is employed to validate the final model for accuracy and to predict the limiting velocity required to prevent sedimentation in sewer systems.

## Results and discussion

*Fr*estimation using the ANFIS and ANFIS-DE methods. Model 1 that employs

*C*

_{ V }

*, D*

_{gr}

*, d/R*and

*λ*

_{ s }as inputs produced good results with both methods.

*Fr*estimated by ANFIS-DE mostly had less than 10% relative error. According to Table 2, the average relative error of Model 1 for all samples in testing mode was about 8% (MARE = 0.076), but with ANFIS it was often more than 10%. The estimates were both under and overestimates (MARE = 0.099). Other indicators presented in the table also indicate the superiority of ANFIS-DE over ANFIS. Therefore, the DE evolutionary algorithm in Model 1 outperformed the hybrid algorithm (backpropagation with least squares).

Performance evaluation of ANFIS and ANFIS-DE in predicting *Fr* for all models (training and testing)

Model No. | Method | | RMSE | MAE | MARE | δ | |
---|---|---|---|---|---|---|---|

Train | Model 1 | ANFIS | 0.933 | 0.579 | 0.456 | 0.120 | 0.117 |

ANFIS-DE | 0.972 | 0.370 | 0.285 | 0.074 | 0.073 | ||

Model 2 | ANFIS | 0.707 | 1.136 | 0.876 | 0.260 | 0.224 | |

ANFIS-DE | 0.840 | 0.831 | 0.594 | 0.167 | 0.152 | ||

Model 3 | ANFIS | 0.670 | 1.199 | 0.904 | 0.258 | 0.232 | |

ANFIS-DE | 0.906 | 0.637 | 0.461 | 0.121 | 0.118 | ||

Model 4 | ANFIS | 0.963 | 0.406 | 0.336 | 0.094 | 0.086 | |

ANFIS-DE | 0.973 | 0.341 | 0.272 | 0.072 | 0.070 | ||

Model 5 | ANFIS | 0.798 | 0.960 | 0.716 | 0.188 | 0.183 | |

ANFIS-DE | 0.913 | 0.632 | 0.478 | 0.125 | 0.123 | ||

Model 6 | ANFIS | 0.819 | 0.902 | 0.646 | 0.171 | 0.165 | |

ANFIS-DE | 0.916 | 0.613 | 0.417 | 0.105 | 0.107 | ||

Test | Model 1 | ANFIS | 0.882 | 0.590 | 0.448 | 0.099 | 0.102 |

ANFIS-DE | 0.963 | 0.392 | 0.331 | 0.076 | 0.075 | ||

Model 2 | ANFIS | 0.611 | 1.375 | 1.103 | 0.240 | 0.252 | |

ANFIS-DE | 0.720 | 1.248 | 1.005 | 0.232 | 0.229 | ||

Model 3 | ANFIS | 0.635 | 1.232 | 0.955 | 0.209 | 0.218 | |

ANFIS-DE | 0.869 | 0.663 | 0.546 | 0.128 | 0.125 | ||

Model 4 | ANFIS | 0.929 | 0.452 | 0.385 | 0.091 | 0.088 | |

ANFIS-DE | 0.965 | 0.323 | 0.281 | 0.065 | 0.064 | ||

Model 5 | ANFIS | 0.735 | 0.866 | 0.749 | 0.185 | 0.171 | |

ANFIS-DE | 0.868 | 0.801 | 0.675 | 0.154 | 0.154 | ||

Model 6 | ANFIS | 0.752 | 0.867 | 0.636 | 0.142 | 0.145 | |

ANFIS-DE | 0.869 | 0.606 | 0.481 | 0.112 | 0.110 |

In Models 1, 2 and 3, the influence of parameters related to the transport mode (*d/R*, *D* ^{ 2 } */A* & *R/D*) is examined. By applying the constant parameters of sediment (*D* _{gr}), transport (*C* _{ V }) and flow resistance (*λ* _{ s }), besides using parameter *D* ^{ 2 } */A* instead of *d/R* (Model 2), the performance of both methods significantly decreased compared with Model 1. The statistical indices show that the relative error in estimating *Fr* reached over 20% (MARE for ANFIS = 0.24; MARE for ANFIS-DE = 0.232) and the RMSE of both methods was double that for Model 1. In this model, most estimations were considered underestimations, and using its results would lead to excessive solid deposition on the channel bed and reduced transmission capacity. Therefore, using *D* ^{ 2 } */A* as a transport mode parameter in addition to *C* _{ V }, *D* _{gr}, and *λ* _{ s } has a negative impact on ANFIS and ANFIS-DE performance in predicting the limiting velocity (*Fr*). This resulted in high error values, low accuracy (*R* ^{2} for ANFIS = 061 and *R* ^{2} for ANFIS-DE = 0.72) and high sediment deposition.

Based on the statistical indices presented in Table 2 and the scatter plot in Fig. 4, Model 3 outperformed Model 2 but was inferior to Model 1. ANFIS-DE estimated Model 3 with fairly good accuracy, whereby the relative error decreased from 24% in Model 2 to about 13% in Model 3. However, Model 3 still made underestimations. The *Fr* predicted by ANFIS and the input combination of Model 3 that employed *R/D* as a transport mode parameter led to a decrease in relative error by 3% compared with Model 2. Hence, the *Fr* value had high relative error and was underestimated. Models 2 and 3 were relatively similar in accuracy. Model 3 had only 4% relative error, which was lower than Model 2, but it had a mean relative error of over 20%. Consequently, using Model 3 is not reliable, as the results would decrease sediment transport capacity and increase sedimentation on the bed channel. The results obtained for Models 1, 2 and 3 signify that considering *λ* _{ s }, *D* _{gr} and *C* _{ V } as part of the “flow resistance,” “sediment” and “transport” groups (respectively) led to the best performance of ANFIS and ANFIS-DE when employing *d/R* as a “transport mode” parameter.

Regarding Models 4-6, the influence of the transport mode group parameters was investigated when *d/D* was used as a dimensionless parameter from the “sediment” group in this study. Model 4 produced good results with both methods: ANFIS (*R* ^{2} = 0.929; RMSE = 0.452; MAE = 0.385; MARE = 0.091 and δ = 0.088) and ANFIS-DE (*R* ^{2} = 0.965; RMSE = 0.323; MAE = 0.281; MARE = 0.065 and δ = 0.064), whereby most *Fr* predictions had less than 10% relative error. The difference between Models 1 and 4 is in their input combinations, as their parameters from the “sediment” group are *D* _{gr} and *d*/*D* and the other parameters are the same. A general comparison of these models demonstrate their high accuracy. Both ANFIS and ANFIS-DE methods in Model 4 estimate with less than 10% relative error, but ANFIS showed an insignificantly greater relative error. A quantitative comparison of these models indicates that using *d/D* in Model 4 rather than *D* _{gr} in Model 1 decreased the relative error about 1.1 and 0.8% for ANFIS-DE and ANFIS, respectively. Models 5 and 2 were compared to survey the effect of the “sediment” parameters (*D* _{gr} and *d/D*) and *D* ^{ 2 } */A* as a “transport mode” parameter. It was found that Model 5 had nearly the same conditions as Model 2 and often underestimated but had a lower relative error. Consequently, the mean error of ANFIS-DE and ANFIS decreased from 24 to 18% and 23 to 16%, respectively. Evidently, the simultaneously use of *d/D* and *D* ^{ 2 } */A* may decrease the lack of effect of *d/R* as an input on limiting velocity estimation.

By ANFIS-DE, for input combination presented in the form of Model 6 reasonable results were obtained. However, this model had significant error of over 10% as overestimation and underestimation, which would reduce its reliability and lead to uneconomical plans or sedimentation, respectively. Using ANFIS to estimate *Fr* with the input combination of Model 6 presented weaker results than ANFIS-DE, with about 15% error. A comparison of Models 6 and 3 shows that the simultaneously use of of *d/D* and *R/D* has insignificant impact in comparison with *D* _{gr} and *R/D* because the *D* _{gr} is a function of *d* as well *d/D*. In addition, the *D* is absent in *D* _{gr} but is considered in *R/D* in both models. In general, using the *d/D* parameter as a representative of the sediment group improves *Fr* estimation.

According to the explanations given, in addition to the parameters related to transport (*C* _{ V }) and flow resistance (*λ* _{ s }) that are constant, using parameter *d/D* from the sediment group and parameter *d/R* from transport mode offers the best performance (Model 4). A comparison of ANFIS and ANFIS-DE for all models signifies the superior performance of the hybrid method presented in this study.

*R*

^{2}; therefore, it is quite different from the estimate achieved by May et al. (1996), which increases its unreliability.

*DR*), which is equal to the ratio of the predicted value to the actual value. These results are presented in Fig. 5. The

*DR*values for ANFIS-DE, and Ebtehaj et al. (2014) and May et al. (1996) equations are 0.99, 1.03 and 0.97, respectively. Although the difference is not vast, model accuracy and the average precision should be confirmed by considering the maximum relative error values as well. In Fig. 5 the

*DR*value for ANFIS-DE is 1 ± 0.15, while the estimation results of the two regression equations indicate that some of the estimated values have large error. Thus, overestimation beyond a certain allowance results in non-economical project assessment, while underestimation below a certain value leads to sediment deposition and related problems. Using the equations would also result in less confidence.

## Conclusion

Sediment transport in pipe channels is a critical subject, because using incorrect designs leads to sediment deposition and non-economical assessments. Therefore, a method that accurately estimates the limiting velocity to prevent sediment deposition is essential. In this study, a hybrid ANFIS was designed based on differential evolution called ANFIS-DE. It was used to predict the densimetric Froude number (*Fr*) parameter, which takes into account the limiting velocity effect. Accordingly, the factors affecting non-deposition sediment transport were determined and the dimensionless parameters were defined to propose six different models (Models 1–6). According to the results obtained for the effect of each dimensionless parameter on the estimated *Fr* parameter, using *D* ^{ 2 } */A* as a parameter in “transport mode” leads to significantly inferior performance of both methods. The average relative error attained was over 20% for both methods. The best result of each input combination was achieved by selecting *d/R* as representative of the “transport mode” group. Besides, by taking into account parameters related to “flow resistance,” “transport” and “transport mode,” using *D* _{gr} instead of *d/D* led to a minor accuracy reduction of less than 2%. The best performance in estimating the *Fr* parameter was attained by the model that used the following dimensionless parameters: volumetric sediment concentration (*C* _{ V }), ratio of median particle diameter to hydraulic radius (*d/R*), ratio of median particle diameter to pipe diameter (*d/D*) and overall friction factor of sediment (*λ* _{ s }) (*Fr* = *f* (*CV, d/R, d/D, λ* _{ s })). Moreover, a comparison of ANFIS-DE with ANFIS represented the superior performance of ANFIS-DE. Two regression-based methods presented based on semi-experimental and dimensional analysis were also compared with the results of ANFIS-DE. The comparison results indicated the superior performance of ANFIS.

## References

- Ab Ghani A (1993) Sediment transport in sewers. Dissertation, University of Newcastle Upon Tyne, UKGoogle Scholar
- Ab Ghani A, Azamathulla HM (2014) Development of GEP-based functional relationship for sediment transport in tropical rivers. Neural Comput Appl 24(2):271–276. doi: 10.1007/s00521-012-1222-9 CrossRefGoogle Scholar
- Ackers JC, Butler D, May RWP (1996) Design of sewers to control sediment problems. Rep. No. CIRIA 141. Construction Industry Research and Information Association, LondonGoogle Scholar
- Al-Abadi AM (2014) Modeling of stage–discharge relationship for Gharraf River, southern Iraq using backpropagation artificial neural networks, M5 decision trees, and Takagi-Sugeno inference system technique: a comparative study. Appl Water Sci 6(4):407–420. doi: 10.1007/s13201-014-0258-7 CrossRefGoogle Scholar
- Almedeij J (2012) Rectangular storm sewer design under equal sediment mobility. Am J Environ Sci 8(4):376–384. doi: 10.3844/ajessp.2012.376.384 CrossRefGoogle Scholar
- Azamathulla HMd, Ab Ghani A, Fei SY (2012) ANFIS—based approach for predicting sediment transport in clean sewer. Appl Soft Comput 12(3):1227–1230. doi: 10.1016/j.asoc.2011.12.003 CrossRefGoogle Scholar
- Bäck T, Fogel DB, Michalewicz Z (eds) (1997) Handbook of Evolutionary Computation. Inst. Phys. and Oxford University Press, New YorkGoogle Scholar
- Banasiak R (2008) Hydraulic performance of sewer pipes with deposited sediments. Water Sci Technol 57:1743–1748. doi: 10.2166/wst.2008.287 CrossRefGoogle Scholar
- Bonakdari H, Ebtehaj I (2014a) Verification of equation for non-deposition sediment transport in flood water canals. In: 7th International Conference on Fluvial Hydraulic RIVER FLOW 2014; Lausanne; Switzerland, 3–5 September, p 1527–1533. doi: 10.1201/b17133-203
- Bonakdari H, Ebtehaj I (2014b) Study of sediment transport using soft computing technique. In: 7th International conference on fluvial hydraulic, RIVER FLOW 2014; Lausanne; Switzerland, 3–5 September, p 933–940. doi: 10.1201/b17133-126
- Bui DT, Pradhan B, Lofman O, Revhaug I, Dick OB (2012) Landslide susceptibility mapping at Hoa Binh province (Vietnam) using an adaptive neuro-fuzzy inference system and GIS. Comput Geosci 45:199–211. doi: 10.1016/j.cageo.2011.10.031 CrossRefGoogle Scholar
- Bui DT, Pradhan B, Nampak H, Bui QT, Tran QA, Nguyen QP (2016a) Hybrid artificial intelligence approach based on neural fuzzy inference model and metaheuristic optimization for flood susceptibilitgy modeling in a high-frequency tropical cyclone area using GIS. J Hydrol 540:317–330. doi: 10.1016/j.jhydrol.2016.06.027 CrossRefGoogle Scholar
- Bui DT, Pham BT, Nguyen QP, Hoang ND (2016b) Spatial prediction of rainfall-induced shallow landslides using hybrid integration approach of Least-Squares Support Vector Machines and differential evolution optimization: a case study in Central Vietnam. Int J Digit Earth 9(11):1077–1097. doi: 10.1080/17538947.2016.1169561 CrossRefGoogle Scholar
- Bui KTT, Bui DT, Zou J, Van Doan C, Revhaug I (2017a) A novel hybrid artificial intelligent approach based on neural fuzzy inference model and particle swarm optimization for horizontal displacement modeling of hydropower dam. Neural Comput Appl p 1–12. doi: 10.1007/s00521-016-2666-0
- Bui DT, Bui QT, Nguyen QP, Pradhan B, Nampak H, Trinh PT (2017b) A hybrid artificial intelligence approach using GIS-based neural-fuzzy inference system and particle swarm optimization for forest fire susceptibility modeling at a tropical area. Agric For Meteorol 233:32–44. doi: 10.1016/j.agrformet.2016.11.002 CrossRefGoogle Scholar
- Chang JR, Wei LY, Cheng CH (2011) A hybrid ANFIS model based on AR and volatility for TAIEX forecasting. Appl Soft Comput 11(1):1388–1395. doi: 10.1016/j.asoc.2010.04.010 CrossRefGoogle Scholar
- Chen MY (2013) A hybrid ANFIS model for business failure prediction utilizing particle swarm optimization and subtractive clustering. Inf Sci 220:180–195. doi: 10.1016/j.ins.2011.09.013 CrossRefGoogle Scholar
- Cus F, Balic J, Zuperl U (2009) Hybrid ANFIS-ants system based optimization of turning parameters. J Achiev Mater Manuf Eng 36(1):79–86Google Scholar
- Demirci M, Baltaci A (2013) Prediction of suspended sediment in river using fuzzy logic and multilinear regression approaches. Neural Comput Appl 23(1):145–151. doi: 10.1007/s00521-012-1280-z CrossRefGoogle Scholar
- Ebtehaj I, Bonakdari H (2013) Evaluation of sediment transport in sewer using artificial neural network. Eng Appl Comput Fluid Mech 7(3):382–392. doi: 10.1080/19942060.2013.11015479 Google Scholar
- Ebtehaj I, Bonakdari H (2014a) Performance evaluation of adaptive neural fuzzy inference system for sediment transport in sewers. Water Resour Manag 28(13):4765–4779. doi: 10.1007/s11269-014-0774-0 CrossRefGoogle Scholar
- Ebtehaj I, Bonakdari H (2014b) Comparison of genetic algorithm and imperialist competitive algorithms in predicting bed load transport in clean pipe. Water Sci Technol 70(10):1695–1701. doi: 10.2166/wst.2014.434 CrossRefGoogle Scholar
- Ebtehaj I, Bonakdari H (2016) Assessment of evolutionary algorithms in predicting non-deposition sediment transport. Urban Water J 5:499–510. doi: 10.1080/1573062X.2014.994003 CrossRefGoogle Scholar
- Ebtehaj I, Bonakdari H, Sharifi A (2014) Design criteria for sediment transport in sewers based on self-cleansing concept. J Zhejiang Univ Sci A 15(11):914–924. doi: 10.1631/jzus.A1300135 CrossRefGoogle Scholar
- Gholami R, Kamkar-Rouhani A, Ardejani FD, Maleki S (2011) Prediction of toxic metals concentration using artificial intelligence techniques. Appl Water Sci 1(3–4):125–134. doi: 10.1007/s13201-011-0016-z CrossRefGoogle Scholar
- Gorai AK, Hasni SA, Iqbal J (2014) Prediction of ground water quality index to assess suitability for drinking purposes using fuzzy rule-based approach. Appl Water Sci. doi: 10.1007/s13201-014-0241-3 Google Scholar
- Ivanovich EV, Hamid K (2014) An alternative approach for assessing sediment impact on aquatic ecosystems using single decision tree (SDT). J Water Sustain 4(3):181–204. doi: 10.11912/jws.2014.4.3.181-204 Google Scholar
- Jang JSR, Sun CT, Mizutani E (1997) Neurofuzzy and soft computing: a computational approach to learning and machine intelligence. Prentice-Hall, New JerseyGoogle Scholar
- Liu J, Lampinen J (2002) On setting the control parameter of the differential evolution method. In: Proc. 8th Int. Conf. Soft Computing (MENDEL 2002), p 11–18Google Scholar
- MATLAB and Statistics Toolbox Release (2009) Fuzzy logic toolboxTM user’s guide. The MathWorks Inc., Natick, MassachusettsGoogle Scholar
- May RWP (2003) Preventing sediment deposition in inverted sewer siphons. J Hydraul Eng 129(4):283–290. doi: 10.1061/(ASCE)0733-9429(2003)129:4(283) CrossRefGoogle Scholar
- May RWP, Ackers JC, Butler D, John S (1996) Development of design methodology for self-cleansing sewers. Water Sci Technol 33(9):195–205. doi: 10.1016/0273-1223(96)00387-3 Google Scholar
- Mayerle R, Nalluri C, Novak P (1991) Sediment transport in rigid bed conveyance. J Hydraul Eng 29(4):475–495. doi: 10.1061/(ASCE)1084-0699(2007)12:5(532) CrossRefGoogle Scholar
- Mondal NK, Bhaumik R, Das B, Roy P, Datta JK, Bhattacharyya S, Bhattacharjee S (2015) Neural network model and isotherm study for removal of phenol from aqueous solution by orange peel ash. Appl Water Sci 5(3):271–282. doi: 10.1007/s13201-014-0188-4 CrossRefGoogle Scholar
- Moosavi V, Vafakhah M, Shirmohammadi B, Behnia N (2013) A wavelet-ANFIS hybrid model for groundwater level forecasting for different prediction periods. Water Resour Manag 27(5):1301–1321. doi: 10.1007/s11269-012-0239-2 CrossRefGoogle Scholar
- Nalluri C, Ab Ghani A (1996) Design option for self-cleansing storm sewers. Water Sci Technol 33(9):215–220. doi: 10.1016/0273-1223(96)00389-7 Google Scholar
- Ota JJ, Nalluri C (1999) Graded sediment transport at limit deposition in clean pipe channel. In: 28th international association for hydro-environment engineering and research, Graz, AustriaGoogle Scholar
- Shoorehdeli MA, Teshnehlab M, Sedigh AK (2007) Novel hybrid learning algorithms for tuning ANFIS parameters using adaptive weighted PSO. In: Fuzzy Systems Conference, 2007. FUZZ-IEEE 2007. IEEE International (pp. 1-6). IEEE. doi: 10.1109/FUZZY.2007.4295571
- Shoorehdeli MA, Teshnehlab M, Sedigh AK, Khanesar MA (2009) Identification using ANFIS with intelligent hybrid stable learning algorithm approaches and stability analysis of training methods. Appl Soft Comput 9(2):833–850. doi: 10.1016/j.asoc.2008.11.001 CrossRefGoogle Scholar
- Storn R, Price K (1997) Differential evolution—A simple and efficient heuristic for global optimization over continuous spaces. J Global Optim 11:341–359. doi: 10.1023/A:1008202821328 CrossRefGoogle Scholar
- Vongvisessomjai N, Tingsanchali T, Babel MS (2010) Non-deposition design criteria for sewers with part-full flow. Urban Water J 7(1):61–77. doi: 10.1080/15730620903242824 CrossRefGoogle Scholar

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