Home Toward rainfall prediction by machine learning in Perfume River Basin, Thua Thien Hue Province, Vietnam
Article Open Access

Toward rainfall prediction by machine learning in Perfume River Basin, Thua Thien Hue Province, Vietnam

  • Nguyen Hong Giang , YuRen Wang EMAIL logo , Tran Dinh Hieu EMAIL logo , Quan Thanh Tho , Le Anh Phuong and Hoang Ngo Tu Do
Published/Copyright: August 26, 2021
Become an author with De Gruyter Brill

Abstract

This study examines rainfall forecasting for the Perfume (Huong) River basin using the machine learning method. To be precise, statistical measurement indicators are deployed to evaluate the reliability of the actual accumulated data. At the same time, this study applied and compared two popular models of multi-layer perceptron and the k-nearest neighbors (k-NN) with different configurations. The calculated rainfall data are obtained from the Hue, Aluoi, and Namdong hydrological stations, where the rainfall demonstrated a giant impact on the downstream from 1980 to 2018. This study result shows that both models, once fine-tuned properly, enjoyed the performance with standard metrics of R_squared, mean absolute error, Nash–Sutcliffe efficiency, and root-mean-square error. In particular, once Adam stochastic is deployed, the implementation of the MLP model is significantly improving. The promising forecast results encourage us to consider applying these models with future data to help natural disaster non-stop mitigation in the Perfume River basin.

1 Introduction

Global climate change has extreme effects on the annual volume and pattern of rainfall. It is also the main cause of several droughts and floods worldwide. This situation has negatively impacted people, such as farmers, peasants, and agriculturists, whose livelihood depends on regular rainfall [1,2,3]. These points indicate that the desirability of highly accurate rainfall forecasting is now an urgent situation. Therefore, several studies have proposed several prediction methods of hydrological processes for forecasting soil temperature with neural networks and machine learning methods for rain run-off prediction, forecasting water flow, semi-arid precipitation forecast, and drought prediction [4,5,6,7,8,9]. In addition, recently several studies have applied machine learning methods to predict the quality of dykes, water quality in rivers, and the amount of sludge in wastewater treatment plants [10,11,12].

The MLP and k-nearest neighbors (k-NN) that the models conduct for supervised learning techniques in classification math are mentioned [13,14]. Classification math is divided into three processes: collecting the input training data set, using the test data set to check the classification accuracy, and deploying the classifier to categorize the new data [15]. Its abilities identify the relationships of the high complexity of input and output variables without realizing the natural physical processes [16,17,18,19,20,21,22]. Specific functions of the k-NN model’s salient features are the non-parametric approach and the most straightforward in both regression and classification functions [23,24,25]. In addition, the main advantages of k-NN can be listed as fast calculation time, a simple algorithm, easy to interpret, useful for regression and classification, high accuracy, no assumptions about data, no need to make additional assumptions and adjust some parameters or build a model [26,27,28]. Meanwhile, the MLP provides reliable regression and classification for the neural networks, which involves data entry from the input units and passes through the network to output units. Its hierarchy includes an input layer and one or more invisible layers of computational nodes and an output layer of computational nodes [29,30,31]. The MLP model integrates with the backpropagation algorithm [32].

Therefore, several studies on rainfall forecasts had been published using the models. Dash et al. [33] applied the k-NN model to predict the rainfall season of the summer monsoon (June–September) and post-monsoon (from October to December) for 4 years (from 2011 to 2016) in Kerala state of Indian Peninsula. The study concluded that k-NN has been carried out reasonably well. Wu et al. [34] used the k-NN model to forecast rain from February to April every year at 18 major hydrological stations in the Southeastern Mediterranean region. The results indicated that k-NN model well narrowed the gap between the global and the coarse forecasts models for the Southeastern Mediterranean region. Vallam and Qin [35] developed a k-NN model to test predicted long-term rainfall simulation in Singapore over 30 years. The results showed that the k-NN model is satisfactory when forecasts were conducted in the wet seasons. Moreover, the model could repeat the values closely of extreme rainfall. Zhang et al. [36] used the MLP model to predict the annual and non-monsoon rainfall prediction in Odisha, India. The results indicated that MLP was more accurate when using the model for the rest of the eight non-monsoon months in future rainfall prediction. Zahmatkesh and Goharian [37] used the MLP model to predict long lead monthly rainfall forecast from 1925 to 2016 in Vancouver, British Columbia, Canada. The research pointed out that the model with the best forecasting performance is selected to forecast rainfall 1 month ahead of time.

The perfume River basin in Thua Thien Hue Province is a vulnerable place, sensitive to natural disasters and the impact of climate change. Therefore, this area needs many types of forecasting related to natural disasters. Toward rainfall prediction for the Perfume River basin will be deployed by Machine Learning based on the Python platform. Even though the first-time study methodology is applied, this study result may contribute to making more accurate predictions and supplying a new method for rainfall forecast in this basin.

This study proposes two MLP and k-NN models with four configurations: Adam, L-BFGS methods, Euclidean, and Minkowski distance metrics predict rainfall in the Perfume River basin, respectively. These models are also deployed to compare each other to find the most optimal model. Several accurate measurement parameters such as R_squared, Nash–Sutcliffe efficiency (NSE), root-mean-square error (RMSE), and mean absolute error (MAE) are used to evaluate the accuracy levels of the proposed models. In addition, statistical measurement indicators (the percentage, the average, minimum and maximum values, standard deviation (St Dev), coefficient of variation (Cv) are applied to evaluate the reliability of the actual accumulated data.

The rest of the paper is structured as follows: Section 2 describes the methodology and study area, Section 3 evaluates the study data and analyzes the study results, Section 4 discusses the study approaches and limitations, and Section 5 presents the conclusion.

2 Methodology, study area, and data collection

2.1 Methodology

2.1.1 Multi-layer perceptron

The MLP model is considered a typical representative. It includes an input layer, an output layer, and many hidden layers in between; all the nodes in the hidden layers and the output layer are named as neurons. The strength of the signal transmitting from one node to the others depends on the connection weight of the inter-connections. Hidden layers improve the network’s ability to complex functions of the model [38,39], appurtenant to a lot of the training process. The training principle for the MLP model is using a variety of backpropagation algorithms. Training is a process of adjusting the weights and bias connections and calculating the errors caused by the network. In the training process, the differences between the desired with actual responses that the output layer of the training process fit the best-desired output [40]. During training of neurons, the activation function is applied to this training process and the rectified linear unit (ReLU) is used for the activation function. ReLU does training for machine learning networks [41,42]. Due to ReLU convergence and gradient calculation almost instantly, ReLU solves explosion and the disappearance of gradients, maintaining a steady-state convergence rate as well [43]. In addition, the ReLU function is simple and effective for rainfall prediction [44]. For popular forecasts, the Adam or Limited-memory Broyden–Fletcher–Goldfarb–Shanno (L-BFGS) method applies for a stochastic optimizer [45,46].

The specific characteristics of ReLU function, Adam, and L-BFGS methods are explained in detail.

The ReLU function is illustrated in Figure 1, and ReLU is described as follows:

(1) f ( x ) = max ( 0 , x ) .

Figure 1 
                     ReLU function graph.
Figure 1

ReLU function graph.

Equation (1) indicates that fʹ(x) = 0 when x < 0 and fʹ(x) = 1 when x ≥ 0.

L-BFGS is an algorithm of optimization of the quasi-Newton methods. It applies to the estimation of parameters in Machine Learning [47,48]. L-BFGS was performed as an estimate of the Hessian matrix of inversion; the purpose of steer is to search through variable space. Due to its requiring linear memory, the L-BFGS method is particularly suitable for optimization problems with multiple variables [49,50].

Adam is derived from the estimation of the adaptive moment. The Adam method is applied for efficient stochastic optimization. It only requires a small memory for the first-order gradience; it calculates the learning rates for different parameters from approximate for the first and second moments of the gradients. The method has several advantages of deep neutral networks as follows. The parameter amplitude updates do not change the gradient scale, do not need the stationary objective, and the step-sizes approximate bounded by the step-sizes of hyper-parameter. At the same time, it carries out with sparse gradients and naturally works in the form of step-size annealing.

In this study, Figure 2 describes the structural MLP that input layer has 12 input nodes from a 1 to a 12 (which are also 12 months of the year), one neuron of the output layer has represented the values of rainfall. There are three hidden layers: the first hidden layer contains neurons from H 11 to H 112, the second one is from H 21 to H 212, and the last one is from H 31 to H 312. Each neuron of the hidden layer and the output layer has a corresponding weight and bias, as W 11 (2), B 1 (1) and W 12 (2) , B 2 (2) are the weight and bias to correspond for neuron H 11 and neuron H 12, respectively, so on. Each neuron of the hidden layers takes the output from all neurons of the previous layers and converts these values with a weighted linear sum into the output layer, where n is the number of neurons of class and corresponds to the component of the vector weights. The output class gets the values from the last hidden layer. The ReLU function is the activation function for three hidden layers. Adam and L-BFGS methods are two stochastic optimizations to the solver of weight optimization, and using these two methods, rainfall prediction of three station areas is compared. The training method for MLP is regression.

Figure 2 
                     Structure of MLP network for rainfall prediction.
Figure 2

Structure of MLP network for rainfall prediction.

2.1.2 k-NN

The k-NN is the layer model for objects and locates on the nearest distance between the objects (query point) layer and remained objects in the training data. The k-NN algorithm is considered an easy learning algorithm and a simple implementation [49]. The response values are calculated as a weighted sum of the whole k neighbors when the k-NN model carries out the regression method. The weight is inversely proportional to the distance from the input record. This distance is called the Minkowski distance. Wilson and Martinez [51] defined the Minkowski distance of order p (p is an integer) between two vectors X, Y as follows:

(2) M  ( X , Y ) =   i n x i   y i p ,

where x i is the i th value in the vector X = i n x I and y i is the i th value in the vector Y = i n y i ; there are numeric input variables, while n is the number of input variables. In this study, the p values in equation (2) will be p = 2 and p = ∞, which are Euclidean and Minkowski distance metrics, respectively. Our purpose is to find the best model for rainfall prediction at three station areas; the results of the study compares k-NN classification error rates by using Euclidean distance versus Minkowski distance. To break the relation between different classes that we continuously decrease the neighbor size, ultimately classifying by just the k = 3 nearest neighbors.

After selecting the value of k, a prediction is an average over the outcomes for k-NN, and equation (3) is as follows [28]:

(3) θ =   1 k k i = 1 o i ,

where o i is the i th value in the vector θ and o is the number of output variables.

2.1.3 Accuracy measurements

Forecasting data will be calculated and compared with actual data to accurately evaluate the forecasted values. The metrics that calculate the forecast accuracy include the MAE, the RMSE, and the R_squared. The error metrics are as follows:

(4) MAE = 1 n t = 1 n x f , t   x a , t ,

(5) RMSE = t = 1 n ( x f , t   x a , t ) 2 n ,

(6) R_squared = 1   t = 1 n ( x a , t   x f , t ) 2 t = 1 n x a , t   1 n t = 1 n x a , t 2 ,

(7) NSE = 1   t = 1 n ( x a , t   x f , t ) 2 t = 1 n ( x a , t   x ¯ ) 2 ,

where x f,t and x a,t are the forecast value and actual value in the period time t, respectively, x ¯ is mean of the observed value, and n is the number of the observed values in the testing data. The forecasting study accuracy is conducted by the R_squared, NSE, and the error indicators (MAE, RMSE). The R_squared and NSE should be approaching up to 1 to indicate strong model performance, and the error indicators should be as close to zero as possible. Based on these error indicators, the best prediction model for each station area is chosen.

Thus, the methodology of this paper is summarized in Figure 3. The data in Figure 3 describe a flowchart illustrating the experiment steps for this study.

Figure 3 
                     Flowchart of the experimental steps conducted in this study.
Figure 3

Flowchart of the experimental steps conducted in this study.

2.2 Study area

2.2.1 Brief of geography

Thua Thien Hue Province belongs to the North Central Coast Region of Vietnam. The province containing the largest basin is the Perfume River basin (see Figure 4), which is located between the North of Bach Ma mountain and the East of Truong Son range, its area is about 2,830 km2, the altitude ranging from 200 m to 1,708 m, and the average slope ranging from 15 to 35°. Its main branches originate from the high areas of Bach Ma mountain, flow from South to North about 104 km. At the same time, the basin has three relatively sub-drainage basins: Huu Trach branch (a catchment range of 691 km2 with 70 km long), Ta Trach branch (a catchment range of 729 km2 with 51 km long), and Bo River (a drainage basin of 938 km2 with 94 km long). Perfume River basin has the highest rainfall in Vietnam. Annually, the dry season runs from March to August in this basin, and the rough often from the end of July to the end of August. Especially, hurricane season starts in September and finishes in December. The average precipitation in Hue, ALuoi, and Namdong areas is about 2,850, 3,500, and 3,200 mm, respectively (see Figure 5(a)–(b)). The basin topography has not transitional areas from the upstream of the mountain down to the plain and the lagoon system. Hence, this morphology mainly causes high runoff upstream and large floods downstream during the rainy season.

Figure 4 
                     The position of the meteorological stations.
Figure 4

The position of the meteorological stations.

Figure 5 
                     Monthly rainfall from 1980 to 2018 at the three hydrological stations.
Figure 5

Monthly rainfall from 1980 to 2018 at the three hydrological stations.

In addition, the black square dots in Figure 4 point out the Hue, Aluoi, Namdong hydrological stations. The areas signify various climatic characteristics. The precipitation of three hydrological stations is a key to flood or drought seasons in the downstream. Therefore, the obtained rainfall data are crucially important in this study.

2.3 Data collection

The annual statistical report by Thua Thien Hue Centre for Hydro-Meteorological Forecasting provided the monthly rainfall data of Hue, Aluoi, and Namdong hydrological stations. The data are also checked with the annual statistical report of Thua Thien Hue Province. This preliminary data evaluation process is crucial for the study input. Table 1 shows the features of the data deployed in this study.

Table 1

Hydrological location, record period, and years considered

Station Location Earliest record year Latest record year Numbers of month
Hue Hue city 1980 2018 468
Aluoi Aluoi district 1980 2018 468
Namdong Namdong district 1980 2018 468

Statistical features calculating from the monthly rainfall time series of each hydrological station are listed in Table 2. For comparative implementation, monthly rainfall data were measured with millimeters (mm). The range of the following characteristics was computed from the time series of the observed monthly rainfall: the percentage, average, minimum and maximum values, St Dev, and Cv.

Table 2

Statistical characteristics of monthly precipitation data

Percentage Average (mm) St Dev Cv (%) Min (mm) Max (mm)
Station Min Max Min Max Min Max Min Max Min Max Min Max
Hue 20 314 50.6 788.3 46.7 451 48 106 3.2 35 353.7 2,452.3
Aluoi 21 275 68.2 912.4 68.2 912.4 31 89 4.5 132.7 499.0 2590.0
Namdong 20 293 66.2 974.0 50 681.1 43 76 1.6 123.5 412.4 2,672.3

Dataset included 468 rainfall months from January 1980 to December 2018. In this study, the dataset from January 1980 to December 2003 of the hydrological stations is used for the training phase, and the dataset from January 2004 to December 2018 is applied for the test phase.

3 Results

3.1 The rainfall forecasting of the MLP model

After many experiments to find the optimal MLP model with two methods of Adam and L-BFGS, the study found the optimal model with the values of the core parameters that are listed in Table 3.

Table 3

MLP basic component

Item Configuration
Number of inputs 12
Number of hidden layers 3
Hidden layer sizes 12/12/12
Number of outputs 1
Learning rate init 0.001
Iter no change 10
Beta 1 0.9
Validation_fraction 0.1
Alpha 0.0001
Max iter 10000
Power_t 0.5
Beta 2 0.999
Solver Adam, L-BFGS

The results of the simulation by the MLP model with Adam and L-BFGS stochastic optimizations is shown in Figure 6. The line charts in Figure 6(a)–(c) are relatively good fitness between trained data and tested data for MLP models with Adam and L-BFGS stochastic optimizations. The difference between the two stochastic optimizations of the three hydrological stations is hardly distinguished by the figures. Hence, the accuracy parameters are provided in higher detail in the data in Table 4.

Figure 6 
                  The actual and predicted rainfall forecasting based on the MLP model with Adam and L-BFGS stochastic optimizations at (a) Hue, (b) Aluoi, and (c) Namdong stations.
Figure 6

The actual and predicted rainfall forecasting based on the MLP model with Adam and L-BFGS stochastic optimizations at (a) Hue, (b) Aluoi, and (c) Namdong stations.

Table 4

Accuracy parameters for rainfall prediction used MLP models at the three hydrological stations

Parameter Hue rainfall prediction used Adam Hue rainfall prediction used L-BFGS Average Namdong rainfall prediction used Adam Namdong rainfall prediction used L-BFGS Average Aluoi rainfall prediction used Adam Aluoi rainfall prediction used L-BFGS Average
R_squared 0.999 0.997 0.998 0.986 0.984 0.985 0.991 0.988 0.990
NSE 0.999 0.998 0.999 0.996 0.995 0.996 0.998 0.997 0.998
MAE 2.97 5.12 4.045 14.37 16.36 15.37 7.81 9.59 8.70
RMSE 4.38 6.24 5.31 17.18 20.21 18.70 9.85 13.11 11.48

The data in Table 4 compares the two methods of Adam and L-BFGS stochastic optimizations. Results from the statistics show that these three hydrological stations have more accurate values when using the Adam method. The results show that the best model is Hue with R-squared = 0.999, NSE = 0.999, MAE = 2.97, and RMSE = 5.38, the second-best model is Aluoi with R-squared = 0.991, NSE = 0.998, MAE = 7.81, and RMSE = 9.85, and the third-best model is Namdong hydrological station with R-squared = 0.986, NSE = 0.996, MAE = 14.37, and RMSE = 17.18.

3.2 The rainfall forecasting of the k-NN model

The parameters in Table 5 give optimal values for the k-NN model with distance metrics p = {2, ∞}. These values are obtained after many experiments to get the optimal model.

Table 5

k-NN basic components

Algorithm auto Leaf_size 30
Metric: Minkowski P {2, ∞}
N_neighbors: 3 Weights: uniform

The data in Figure 7 show the k-NN for rainfall forecasting to apply distance metric with p = 2 and p = ∞ in Hue, Namdong, and Aluoi hydrological stations. Figure 7(b) and (c) indicates that the rainfall prediction and actual rainfall are a very close relationship; moreover, there are no significant differences. Because the two graphs above are difficult to distinguish the best optimal distance metric, the data in Table 6 is provided to evaluate the best method. Figure 7(a) shows that the k-NN with p = ∞ is the best forecast for rainfall at Hue hydrological station; moreover, the prediction and actual data are very rigid. Meanwhile, the relationship between expected and actual rainfall of the values of p = 2 is loose-fitting.

Figure 7 
                  The actual and predicted rainfall forecasting based on the k-NN model with p = 2 and p = ∞ at (a) Hue hydrological station, (b) Aluoi hydrological station, and (c) Namdong hydrological station.
Figure 7

The actual and predicted rainfall forecasting based on the k-NN model with p = 2 and p = ∞ at (a) Hue hydrological station, (b) Aluoi hydrological station, and (c) Namdong hydrological station.

Table 6

Accuracy parameters for rainfall prediction used k-NN models at the three hydrological stations

Parameter Hue p = 2 Hue p = ∞ Average Namdong p = 2 Namdong p = ∞ Average Aluoi p = 2 Aluoi p = ∞ Average
R_squared 0.982 0.993 0.985 0.983 0.981 0.982 0.987 0.979 0.982
NSE 0.996 0.998 0.997 0.992 0.991 0.992 0.996 0.994 0.995
MAE 32.83 16.39 24.61 21.67 28.65 25.16 19.05 31.46 25.255
RMSE 43.62 27.70 35.66 61.88 76.21 69.045 29.36 44.78 37.07

The data in Table 6 show the value of prediction errors of the R_squared, NSE, MAE, and RMSE. These data were collected from the analysis of the rainfall prediction of the three hydrological stations using the k-NN model with distance metrics of p = 2 and p = ∞. At the same time, the result of the analysis indicated that the value of the forecast errors at the Hue station with p = ∞ is the lowest, and the second-lowest is the Aluoi station with p = 2. On the other hand, the value of forecast errors for the Namdong station with p = 2 is the highest. R_squared, NSE, MAE, and RMSE of the best model for the Hue, Aluoi, and Namdong hydrological station are 0.993, 0.998, 16.39, and 27.70; 0.987, 0.996, 19.05, 29.36; and 0.983, 0.992, 21.67, 61.88, respectively.

3.3 Comparison and analysis of simulation results between the MLP model and the k-NN model

The models of MLP and k-NN are carried out to assess rainfall during the 1980 to 2018 period in Thua Thien Hue Province. The line chart of Figure 8 summarizes the best rainfall projections at Hue, Aluoi, and Namdong hydrological stations after using the methods of distance metric and stochastic optimization for both the k-NN and MPL models.

Figure 8 
                  The best forecast of precipitation when using k-NN and MLP models.
Figure 8

The best forecast of precipitation when using k-NN and MLP models.

Figure 9 and Table 7 show that the average R_squared and NSE indicators of the two models are from 0.987 to 0.997, which proves that simulation results in a highly accurate forecast when compared with true data together. At the same time, the average error indicators of the MLP and k-NN models fluctuate from 8.38 to 39.65, in which the average values of MAE, RMSE parameters of the k-NN, and MPL models are 19.04, 8.38 and 39.45, 10.47, respectively, which mean that the indicators are fitness values for both the rainfall training data and the rainfall forecasting data.

Figure 9 
                  The best forecast of precipitation when using k-NN and MLP models at the (a) Hue, (b) Aluoi, and (c) Namdong hydrological stations.
Figure 9

The best forecast of precipitation when using k-NN and MLP models at the (a) Hue, (b) Aluoi, and (c) Namdong hydrological stations.

Table 7

The best accuracy parameters for rainfall prediction used k-NN and MLP models at the three hydrological stations

Parameter k-NN MLP
Hue p = ∞ Namdong p = 2 Aluoi p = 2 Average Hue Adam Namdong Adam Aluoi Adam Average
R_squared 0.993 0.983 0.987 0.988 0.999 0.986 0.991 0.992
NSE 0.998 0.992 0.996 9.995 0.999 0.995 0.998 0.997
MAE 16.39 21.67 19.05 19.04 2.97 14.37 7.81 8.38
RMSE 27.7 61.88 29.36 39.65 4.38 17.18 9.85 10.47

In addition, Figure 10 shows a comparison between the predicted values of precipitation rainfall and the actual values of precipitation in the training and testing periods and the correlation coefficient for the best k-NN model and MLP prediction model. The MLP method is more exact in the provision of the correlation coefficient.

Figure 10 
                  The best performance R_squared of MLP and k-NN terms of the correlation coefficient for Thua Thien Hue Province in (c), (d) Hue hydrological station, (b), (e) Namdong hydrological station, and (a), (f) Aluoi hydrological station.
Figure 10

The best performance R_squared of MLP and k-NN terms of the correlation coefficient for Thua Thien Hue Province in (c), (d) Hue hydrological station, (b), (e) Namdong hydrological station, and (a), (f) Aluoi hydrological station.

4 Discussion

The result of simulating rainfall by MLP and k-NN models using four different configurations showed the following findings. Two models obtained the best performance and reliability for rainfall prediction; moreover, the forecast values compared to the actual parameters achieved high accuracy, where the R_squared and NSE values were higher than 0.979. At the same time, the RMSE values were lower than 76.21. The MLP model with the Adam optimization method gave the best accuracy for rainfall prediction to compare with the rest methods.

The study is conducted to predict a time series of annual rainfall from 1980 to 2018 in three hydrological stations: Hue station is located downstream and Aluoi and Namdong are located upstream.

However, several recent rainfall studies have incorporated rainfall and some effects on precipitation. The research of Choubin et al. [52] evaluated factors that may influence fall rain forecast in Kerman Province, Iran, which consisted of large-scale oceanic and atmospheric information. Hence, the combination between these factors and accumulated rainfall data has given high accuracy for the forecast of autumn rainfall. Rainfall data have non-linear variation. Therefore, Choubin et al. [53] deployed the data normalization method for the rainfall study at the Maharlu-Bakhtegan basin, Iran. And the results indicated that the MLP model using data after normalization have resulted in a lower RMSE than the RMSE of this study. In addition, the studies by Najafzadeh et al. [54,55] have used some models such as neuro-fuzzy group method of data handling (NF-GMDH) based on self-organized models and group method of data handling gene-expression programming (GMDH-GEP) model to forecast bridge pier scour depth under debris flow effects and free span expansion rates below pipelines under waves, respectively. Research results have shown that the RMSE index of these two models is also smaller than the RMSE value of this study.

Even though the precipitation at three hydrological stations has a seasonal variation with different complexity, applying these two models with four configurations has achieved high-reliability results. Hence, it can be used for rainfall forecasting for other regions in Vietnam. In addition, the study results are also a utility reference channel for the province authority to develop short-term plans for natural disaster mitigation.

5 Conclusion

This study performs the predicted precipitation of the Perfume River basin. This study also indicated that the MLP model is more accurate than the k-NN model. The measured rainfall was collected from three hydrological stations at the Hue, Namdong, and ALuoi areas of the province from 1980 to 2018. The dataset is separated using time-based criteria: training data (1980–2003) and test data (2004–2018). The results demonstrate that the effectiveness of the models for the core parameters has been mentioned earlier. In addition, this study result may help the Thua Thien Hue government formulate short-term plans of natural disasters to mitigate for the basin.


tel: +84-90-515-3333

Acknowledgments

We would like to thank the school of Civil Engineering of National Kaohsiung University of Science and Technology of Taiwan, and the Thu Dau Mot University of Vietnam for implementing and financial study. We also thank the master class of MSE#07HCM at FSB School Of Business and Technology and Dr. Hector Tibo, Dr. June Raymon (who are currently Ph.D. students at the National Kaohsiung University of Science and Technology of Taiwan) for their help in correcting the academic writing of the paper.

  1. Funding information: This research is funded by Thu Dau Mot University, Vietnam. The APC was funded by Thu Dau Mot University.

  2. Author contributions: Conceptualization, discussion, and conclusions, material and methods: Nguyen Hong Giang; writing, original draft preparation: Tran Dinh Hieu, Hoang Ngo Tu Do; writing, review, and editing: Yu Ren Wang, Quan Thanh Tho, Le Anh Phuong; funding acquisition: Tran Dinh Hieu and Nguyen Hong Giang. All authors have read and agreed to the published version of the manuscript.

  3. Conflict of interest: The authors declare no conflict of interest.

  4. Data availability statements: The datasets analyzed during the study are available from the corresponding author on request.

References

[1] Wang B, Xiang B, Li J, Webster PJ, Rajeevan MN, Liu J, et al. Rethinking Indian monsoon rainfall prediction in the context of recent global warming. Nat Commun. 2015;6(1):1–9.10.1038/ncomms8154Search in Google Scholar PubMed PubMed Central

[2] Cramer S, Kampouridis M, Freitas AA, Alexandridis AK. An extensive evaluation of seven machine learning methods for rainfall prediction in weather derivatives. Expert Syst Appl. 2017;85:169–81.10.1016/j.eswa.2017.05.029Search in Google Scholar

[3] Kusiak A, Wei X, Verma AP, Roz E. Modeling and prediction of rainfall using radar reflectivity data: a data-mining approach. IEEE Trans Geosci Remote Sens. 2012;51(4):2337–42.10.1109/TGRS.2012.2210429Search in Google Scholar

[4] Bui DT, Pradhan B, Lofman O, Revhaug I, Dick ØB. Regional prediction of landslide hazard using probability analysis of intense rainfall in the Hoa Binh province, Vietnam. Nat Hazards. 2013;66(2):707–30.10.1007/s11069-012-0510-0Search in Google Scholar

[5] Bonakdari H, Moeeni H, Ebtehaj I, Zeynoddin M, Mahoammadian A, Gharabaghi B. New insights into soil temperature time series modeling: linear or nonlinear? Theor Appl Climatol. 2019;135(3):1157–77.10.1007/s00704-018-2436-2Search in Google Scholar

[6] Labat D, Ababou R, Mangin A. Linear and nonlinear input/output models for karstic springflow and flood prediction at different time scales. Stoch Environ Res risk Assess. 1999;13(5):337–64.10.1007/s004770050055Search in Google Scholar

[7] Adamowski J, Sun K. Development of a coupled wavelet transform and neural network method for flow forecasting of non-perennial rivers in semi-arid watersheds. J Hydrol. 2010;390(1–2):85–91.10.1016/j.jhydrol.2010.06.033Search in Google Scholar

[8] Choubin B, Khalighi-Sigaroodi S, Malekian A, Ahmad S, Attarod P. Drought forecasting in a semi-arid watershed using climate signals: a neuro-fuzzy modeling approach. J Mt Sci. 2014;11(6):1593–605.10.1007/s11629-014-3020-6Search in Google Scholar

[9] Choubin B, Malekian A, Samadi S, Khalighi‐Sigaroodi S, Sajedi‐Hosseini F. An ensemble forecast of semi‐arid rainfall using large‐scale climate predictors. Meteorol Appl. 2017;24(3):376–86.10.1002/met.1635Search in Google Scholar

[10] Zeinolabedini M, Najafzadeh M. Comparative study of different wavelet-based neural network models to predict sewage sludge quantity in wastewater treatment plant. Environ Monit Assess. 2019;191(3):1–25.10.1007/s10661-019-7196-7Search in Google Scholar PubMed

[11] Najafzadeh M, Oliveto G. Riprap incipient motion for overtopping flows with machine learning models. J Hydroinf. 2020;22(4):749–67.10.2166/hydro.2020.129Search in Google Scholar

[12] Najafzadeh M, Ghaemi A. Prediction of the five-day biochemical oxygen demand and chemical oxygen demand in natural streams using machine learning methods. Environ Monit Assess. 2019;191(6):1–21.10.1007/s10661-019-7446-8Search in Google Scholar PubMed

[13] Hosseini S, Azizi M. The hybrid technique for DDoS detection with supervised learning algorithms. Computer Netw. 2019;158:35–45.10.1016/j.comnet.2019.04.027Search in Google Scholar

[14] Govindarajan M, Chandrasekaran RM. Intrusion detection using neural based hybrid classification methods. Computer Netw. 2011;55(8):1662–71.10.1016/j.comnet.2010.12.008Search in Google Scholar

[15] Eslamloueyan R. Designing a hierarchical neural network based on fuzzy clustering for fault diagnosis of the Tennessee–Eastman process. Appl Soft Comput. 2011;11(1):1407–15.10.1016/j.asoc.2010.04.012Search in Google Scholar

[16] Mahsin MD. Modeling rainfall in Dhaka division of Bangladesh using time series analysis. J Math Model Appl. 2011;1(5):67–73.Search in Google Scholar

[17] Alizadeh Z, Yazdi J, Kim JH, Al-Shamiri AK. Assessment of machine learning techniques for monthly flow prediction. Water. 2018;10(11):1676.10.3390/w10111676Search in Google Scholar

[18] Ren J, Ren B, Zhang Q, Zheng X. A Novel hybrid extreme learning machine approach improved by k-nearest neighbor method and fireworks algorithm for flood forecasting in medium and small watershed of Loess region. Water. 2019;11(9):1848.10.3390/w11091848Search in Google Scholar

[19] Nkoana R. Artificial neural network modelling of flood prediction and early warning. Master Degree. Bloemfontein: University of the Free State; 2011. ufs.ac.za.Search in Google Scholar

[20] Di Piazza A, Conti FL, Noto LV, Viola F, La Loggia G. Comparative analysis of different techniques for spatial interpolation of rainfall data to create a serially complete monthly time series of precipitation for Sicily, Italy. Int J Appl Earth Obs Geoinf. 2011;13(3):396–408.10.1016/j.jag.2011.01.005Search in Google Scholar

[21] Chang TK, Talei A, Alaghmand S, Ooi MPL. Choice of rainfall inputs for event-based rainfall-runoff modeling in a catchment with multiple rainfall stations using data-driven techniques. J Hydrol. 2017;545:100–8.10.1016/j.jhydrol.2016.12.024Search in Google Scholar

[22] Martínez-Acosta L, Medrano-Barboza JP, López-Ramos Á, Remolina López JF, López-Lambraño ÁA. SARIMA approach to generating synthetic monthly rainfall in the Sinú River watershed in Colombia. Atmosphere. 2020;11(6):602.10.3390/atmos11060602Search in Google Scholar

[23] Loh WY. Classification and regression trees. Wiley Interdiscip Rev Data Min Knowl Discov. 2011;1(1):14–23.10.1002/widm.8Search in Google Scholar

[24] Ahmed U, Mumtaz R, Anwar H, Shah AA, Irfan R, García-Nieto J. Efficient water quality prediction using supervised machine learning. Water. 2019;11(11):2210.10.3390/w11112210Search in Google Scholar

[25] Altman NS. An introduction to kernel and nearest-neighbor nonparametric regression. Am Stat. 1992;46(3):175–85.10.1080/00031305.1992.10475879Search in Google Scholar

[26] Gayathri K, Marimuthu A. Text document pre-processing with the KNN for classification using the SVM. 2013 7th International Conference on Intelligent Systems and Control (ISCO). IEEE; 2013. p. 453–7.10.1109/ISCO.2013.6481197Search in Google Scholar

[27] Amra IAA, Maghari AY. Students performance prediction using KNN and Naïve Bayesian. 2017 8th International Conference on Information Technology (ICIT). IEEE; 2017 May. p. 909–13.10.1109/ICITECH.2017.8079967Search in Google Scholar

[28] Imandoust SB, Bolandraftar M. Application of k-nearest neighbor (knn) approach for predicting economic events: Theoretical background. Int J Eng Res Appl. 2013;3(5):605–10.Search in Google Scholar

[29] Tfwala SS, Wang YM. Estimating sediment discharge using sediment rating curves and artificial neural networks in the Shiwen River, Taiwan. Water. 2016;8(2):53.10.3390/w8020053Search in Google Scholar

[30] Jozdani SE, Johnson BA, Chen D. Comparing deep neural networks, ensemble classifiers, and support vector machine algorithms for object-based urban land use/land cover classification. Remote Sens. 2019;11(14):1713.10.3390/rs11141713Search in Google Scholar

[31] Abdullah S, Ismail M, Ahmed AN, Abdullah AM. Forecasting particulate matter concentration using linear and non-linear approaches for air quality decision support. Atmosphere. 2019;10(11):667.10.3390/atmos10110667Search in Google Scholar

[32] Naganna SR, Deka PC, Ghorbani MA, Biazar SM, Al-Ansari N, Yaseen ZM. Dew point temperature estimation: application of artificial intelligence model integrated with nature-inspired optimization algorithms. Water. 2019;11(4):742.10.3390/w11040742Search in Google Scholar

[33] Dash Y, Mishra SK, Panigrahi BK. Rainfall prediction for the Kerala state of India using artificial intelligence approaches. Comput Electr Eng. 2018;70:66–73.10.1016/j.compeleceng.2018.06.004Search in Google Scholar

[34] Wu W, Liu Y, Ge M, Rostkier-Edelstein D, Descombes G, Kunin P, et al. Statistical downscaling of climate forecast system seasonal predictions for the Southeastern Mediterranean. Atmos Res. 2012;118:346–56.10.1016/j.atmosres.2012.07.019Search in Google Scholar

[35] Vallam P, Qin XS. Multi‐site rainfall simulation at tropical regions: a comparison of three types of generators. Meteorol Appl. 2016;23(3):425–37.10.1002/met.1567Search in Google Scholar

[36] Zhang X, Mohanty SN, Parida AK, Pani SK, Dong B, Cheng X. Annual and non-monsoon rainfall prediction modelling using SVR-MLP: an empirical study from Odisha. IEEE Access. 2020;8:30223–33.10.1109/ACCESS.2020.2972435Search in Google Scholar

[37] Zahmatkesh Z, Goharian E. Comparing machine learning and decision making approaches to forecast long lead monthly rainfall: The city of Vancouver, Canada. Hydrology. 2018;5(1):10.10.3390/hydrology5010010Search in Google Scholar

[38] Cao W, Wang X, Ming Z, Gao J. A review on neural networks with random weights. Neurocomputing. 2018;275:278–87.10.1016/j.neucom.2017.08.040Search in Google Scholar

[39] Patra JC, Pal RN, Chatterji BN, Panda G. Identification of nonlinear dynamic systems using functional link artificial neural networks. IEEE Trans Syst Man Cyber Part B. 1999;29(2):254–62.10.1109/3477.752797Search in Google Scholar PubMed

[40] Simpson PK. Artificial neural systems: foundations, paradigms, applications, and implementations. 1st ed. Elmsford, NY: Pergamon Press, Inc.; 1990. worldcat.org.Search in Google Scholar

[41] Freire-Obregon D, Narducci F, Barra S, Castrillon-Santana M. Deep learning for source camera identification on mobile devices. Pattern Recognit Lett. 2019;126:86–91.10.1016/j.patrec.2018.01.005Search in Google Scholar

[42] Wang Y, Li Y, Song Y, Rong X. The influence of the activation function in a convolution neural network model of facial expression recognition. Appl Sci. 2020;10(5):1897.10.3390/app10051897Search in Google Scholar

[43] Huang X, Gao L, Crosbie RS, Zhang N, Fu G, Doble R. Groundwater recharge prediction using linear regression, multi-layer perception network, and deep learning. Water. 2019;11(9):1879.10.3390/w11091879Search in Google Scholar

[44] Xiang Z, Yan J, Demir I. A rainfall‐runoff model with LSTM‐based sequence‐to‐sequence learning. Water Resour Res. 2020;56(1):e2019WR025326.10.1029/2019WR025326Search in Google Scholar

[45] Verma C, Stoffová V, Illés Z, Tanwar S, Kumar N. Machine learning-based student’s native place identification for real-time. IEEE Access. 2020;8:130840–54.10.1109/ACCESS.2020.3008830Search in Google Scholar

[46] Basu M, Kumar S, Gupta P, Kumar Singh R. A quantitative analysis of machine learning based regressors for pressure reconstruction in particle image velocimetry applications. Fluids Engineering Division Summer Meeting. Vol. 83716, American Society of Mechanical Engineers; 2020 July. p. V001T02A01610.1115/FEDSM2020-20262Search in Google Scholar

[47] Malouf R. A comparison of algorithms for maximum entropy parameter estimation. In COLING-02. The 6th Conference on Natural Language Learning 2002 (CoNLL-2002); 2002.10.3115/1118853.1118871Search in Google Scholar

[48] Andrew G, Gao J. Scalable training of l 1-regularized log-linear models. Proceedings of the 24th International Conference on Machine Learning; 2007 June. p. 33–4010.1145/1273496.1273501Search in Google Scholar

[49] Morales JL, Nocedal J. Remark on “Algorithm 778: L-BFGS-B: Fortran subroutines for large-scale bound constrained optimization”. ACM Trans Math Softw. 2011;38(1):1–4. Researchgate.net.10.1145/2049662.2049669Search in Google Scholar

[50] Zhu C, Byrd RH, Lu P, Nocedal J. Algorithm 778: L-BFGS-B: Fortran subroutines for large-scale bound-constrained optimization. ACM Trans Math Softw. 1997;23(4):550–60.10.1145/279232.279236Search in Google Scholar

[51] Wilson DR, Martinez TR. Reduction techniques for instance-based learning algorithms. Mach Learn. 2000;38(3):257–86.10.1023/A:1007626913721Search in Google Scholar

[52] Choubin B, Zehtabian G, Azareh A, Rafiei-Sardooi E, Sajedi-Hosseini F, Kişi Ö. Precipitation forecasting using classification and regression trees (CART) model: a comparative study of different approaches. Environ Earth Sci. 2018;77(8):1–13.10.1007/s12665-018-7498-zSearch in Google Scholar

[53] Choubin B, Malekian A, Golshan M. Application of several data-driven techniques to predict a standardized precipitation index. Atmósfera. 2016;29(2):121–8.10.20937/ATM.2016.29.02.02Search in Google Scholar

[54] Najafzadeh M, Saberi-Movahed F. GMDH-GEP to predict free span expansion rates below pipelines under waves. Mar Georesour Geotechnol. 2019;37(3):375–92.10.1080/1064119X.2018.1443355Search in Google Scholar

[55] Najafzadeh M, Saberi-Movahed F, Sarkamaryan S. NF-GMDH-Based self-organized systems to predict bridge pier scour depth under debris flow effects. Mar Georesour Geotechnol. 2018;36(5):589–602.10.1080/1064119X.2017.1355944Search in Google Scholar

Received: 2021-03-09
Revised: 2021-04-23
Accepted: 2021-07-13
Published Online: 2021-08-26

© 2021 Nguyen Hong Giang et al., published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

Articles in the same Issue

  1. Regular Articles
  2. Lithopetrographic and geochemical features of the Saalian tills in the Szczerców outcrop (Poland) in various deformation settings
  3. Spatiotemporal change of land use for deceased in Beijing since the mid-twentieth century
  4. Geomorphological immaturity as a factor conditioning the dynamics of channel processes in Rządza River
  5. Modeling of dense well block point bar architecture based on geological vector information: A case study of the third member of Quantou Formation in Songliao Basin
  6. Predicting the gas resource potential in reservoir C-sand interval of Lower Goru Formation, Middle Indus Basin, Pakistan
  7. Study on the viscoelastic–viscoplastic model of layered siltstone using creep test and RBF neural network
  8. Assessment of Chlorophyll-a concentration from Sentinel-3 satellite images at the Mediterranean Sea using CMEMS open source in situ data
  9. Spatiotemporal evolution of single sandbodies controlled by allocyclicity and autocyclicity in the shallow-water braided river delta front of an open lacustrine basin
  10. Research and application of seismic porosity inversion method for carbonate reservoir based on Gassmann’s equation
  11. Impulse noise treatment in magnetotelluric inversion
  12. Application of multivariate regression on magnetic data to determine further drilling site for iron exploration
  13. Comparative application of photogrammetry, handmapping and android smartphone for geotechnical mapping and slope stability analysis
  14. Geochemistry of the black rock series of lower Cambrian Qiongzhusi Formation, SW Yangtze Block, China: Reconstruction of sedimentary and tectonic environments
  15. The timing of Barleik Formation and its implication for the Devonian tectonic evolution of Western Junggar, NW China
  16. Risk assessment of geological disasters in Nyingchi, Tibet
  17. Effect of microbial combination with organic fertilizer on Elymus dahuricus
  18. An OGC web service geospatial data semantic similarity model for improving geospatial service discovery
  19. Subsurface structure investigation of the United Arab Emirates using gravity data
  20. Shallow geophysical and hydrological investigations to identify groundwater contamination in Wadi Bani Malik dam area Jeddah, Saudi Arabia
  21. Consideration of hyperspectral data in intraspecific variation (spectrotaxonomy) in Prosopis juliflora (Sw.) DC, Saudi Arabia
  22. Characteristics and evaluation of the Upper Paleozoic source rocks in the Southern North China Basin
  23. Geospatial assessment of wetland soils for rice production in Ajibode using geospatial techniques
  24. Input/output inconsistencies of daily evapotranspiration conducted empirically using remote sensing data in arid environments
  25. Geotechnical profiling of a surface mine waste dump using 2D Wenner–Schlumberger configuration
  26. Forest cover assessment using remote-sensing techniques in Crete Island, Greece
  27. Stability of an abandoned siderite mine: A case study in northern Spain
  28. Assessment of the SWAT model in simulating watersheds in arid regions: Case study of the Yarmouk River Basin (Jordan)
  29. The spatial distribution characteristics of Nb–Ta of mafic rocks in subduction zones
  30. Comparison of hydrological model ensemble forecasting based on multiple members and ensemble methods
  31. Extraction of fractional vegetation cover in arid desert area based on Chinese GF-6 satellite
  32. Detection and modeling of soil salinity variations in arid lands using remote sensing data
  33. Monitoring and simulating the distribution of phytoplankton in constructed wetlands based on SPOT 6 images
  34. Is there an equality in the spatial distribution of urban vitality: A case study of Wuhan in China
  35. Considering the geological significance in data preprocessing and improving the prediction accuracy of hot springs by deep learning
  36. Comparing LiDAR and SfM digital surface models for three land cover types
  37. East Asian monsoon during the past 10,000 years recorded by grain size of Yangtze River delta
  38. Influence of diagenetic features on petrophysical properties of fine-grained rocks of Oligocene strata in the Lower Indus Basin, Pakistan
  39. Impact of wall movements on the location of passive Earth thrust
  40. Ecological risk assessment of toxic metal pollution in the industrial zone on the northern slope of the East Tianshan Mountains in Xinjiang, NW China
  41. Seasonal color matching method of ornamental plants in urban landscape construction
  42. Influence of interbedded rock association and fracture characteristics on gas accumulation in the lower Silurian Shiniulan formation, Northern Guizhou Province
  43. Spatiotemporal variation in groundwater level within the Manas River Basin, Northwest China: Relative impacts of natural and human factors
  44. GIS and geographical analysis of the main harbors in the world
  45. Laboratory test and numerical simulation of composite geomembrane leakage in plain reservoir
  46. Structural deformation characteristics of the Lower Yangtze area in South China and its structural physical simulation experiments
  47. Analysis on vegetation cover changes and the driving factors in the mid-lower reaches of Hanjiang River Basin between 2001 and 2015
  48. Extraction of road boundary from MLS data using laser scanner ground trajectory
  49. Research on the improvement of single tree segmentation algorithm based on airborne LiDAR point cloud
  50. Research on the conservation and sustainable development strategies of modern historical heritage in the Dabie Mountains based on GIS
  51. Cenozoic paleostress field of tectonic evolution in Qaidam Basin, northern Tibet
  52. Sedimentary facies, stratigraphy, and depositional environments of the Ecca Group, Karoo Supergroup in the Eastern Cape Province of South Africa
  53. Water deep mapping from HJ-1B satellite data by a deep network model in the sea area of Pearl River Estuary, China
  54. Identifying the density of grassland fire points with kernel density estimation based on spatial distribution characteristics
  55. A machine learning-driven stochastic simulation of underground sulfide distribution with multiple constraints
  56. Origin of the low-medium temperature hot springs around Nanjing, China
  57. LCBRG: A lane-level road cluster mining algorithm with bidirectional region growing
  58. Constructing 3D geological models based on large-scale geological maps
  59. Crops planting structure and karst rocky desertification analysis by Sentinel-1 data
  60. Physical, geochemical, and clay mineralogical properties of unstable soil slopes in the Cameron Highlands
  61. Estimation of total groundwater reserves and delineation of weathered/fault zones for aquifer potential: A case study from the Federal District of Brazil
  62. Characteristic and paleoenvironment significance of microbially induced sedimentary structures (MISS) in terrestrial facies across P-T boundary in Western Henan Province, North China
  63. Experimental study on the behavior of MSE wall having full-height rigid facing and segmental panel-type wall facing
  64. Prediction of total landslide volume in watershed scale under rainfall events using a probability model
  65. Toward rainfall prediction by machine learning in Perfume River Basin, Thua Thien Hue Province, Vietnam
  66. A PLSR model to predict soil salinity using Sentinel-2 MSI data
  67. Compressive strength and thermal properties of sand–bentonite mixture
  68. Age of the lower Cambrian Vanadium deposit, East Guizhou, South China: Evidences from age of tuff and carbon isotope analysis along the Bagong section
  69. Identification and logging evaluation of poor reservoirs in X Oilfield
  70. Geothermal resource potential assessment of Erdaobaihe, Changbaishan volcanic field: Constraints from geophysics
  71. Geochemical and petrographic characteristics of sediments along the transboundary (Kenya–Tanzania) Umba River as indicators of provenance and weathering
  72. Production of a homogeneous seismic catalog based on machine learning for northeast Egypt
  73. Analysis of transport path and source distribution of winter air pollution in Shenyang
  74. Triaxial creep tests of glacitectonically disturbed stiff clay – structural, strength, and slope stability aspects
  75. Effect of groundwater fluctuation, construction, and retaining system on slope stability of Avas Hill in Hungary
  76. Spatial modeling of ground subsidence susceptibility along Al-Shamal train pathway in Saudi Arabia
  77. Pore throat characteristics of tight reservoirs by a combined mercury method: A case study of the member 2 of Xujiahe Formation in Yingshan gasfield, North Sichuan Basin
  78. Geochemistry of the mudrocks and sandstones from the Bredasdorp Basin, offshore South Africa: Implications for tectonic provenance and paleoweathering
  79. Apriori association rule and K-means clustering algorithms for interpretation of pre-event landslide areas and landslide inventory mapping
  80. Lithology classification of volcanic rocks based on conventional logging data of machine learning: A case study of the eastern depression of Liaohe oil field
  81. Sequence stratigraphy and coal accumulation model of the Taiyuan Formation in the Tashan Mine, Datong Basin, China
  82. Influence of thick soft superficial layers of seabed on ground motion and its treatment suggestions for site response analysis
  83. Monitoring the spatiotemporal dynamics of surface water body of the Xiaolangdi Reservoir using Landsat-5/7/8 imagery and Google Earth Engine
  84. Research on the traditional zoning, evolution, and integrated conservation of village cultural landscapes based on “production-living-ecology spaces” – A case study of villages in Meicheng, Guangdong, China
  85. A prediction method for water enrichment in aquifer based on GIS and coupled AHP–entropy model
  86. Earthflow reactivation assessment by multichannel analysis of surface waves and electrical resistivity tomography: A case study
  87. Geologic structures associated with gold mineralization in the Kirk Range area in Southern Malawi
  88. Research on the impact of expressway on its peripheral land use in Hunan Province, China
  89. Concentrations of heavy metals in PM2.5 and health risk assessment around Chinese New Year in Dalian, China
  90. Origin of carbonate cements in deep sandstone reservoirs and its significance for hydrocarbon indication: A case of Shahejie Formation in Dongying Sag
  91. Coupling the K-nearest neighbors and locally weighted linear regression with ensemble Kalman filter for data-driven data assimilation
  92. Multihazard susceptibility assessment: A case study – Municipality of Štrpce (Southern Serbia)
  93. A full-view scenario model for urban waterlogging response in a big data environment
  94. Elemental geochemistry of the Middle Jurassic shales in the northern Qaidam Basin, northwestern China: Constraints for tectonics and paleoclimate
  95. Geometric similarity of the twin collapsed glaciers in the west Tibet
  96. Improved gas sand facies classification and enhanced reservoir description based on calibrated rock physics modelling: A case study
  97. Utilization of dolerite waste powder for improving geotechnical parameters of compacted clay soil
  98. Geochemical characterization of the source rock intervals, Beni-Suef Basin, West Nile Valley, Egypt
  99. Satellite-based evaluation of temporal change in cultivated land in Southern Punjab (Multan region) through dynamics of vegetation and land surface temperature
  100. Ground motion of the Ms7.0 Jiuzhaigou earthquake
  101. Shale types and sedimentary environments of the Upper Ordovician Wufeng Formation-Member 1 of the Lower Silurian Longmaxi Formation in western Hubei Province, China
  102. An era of Sentinels in flood management: Potential of Sentinel-1, -2, and -3 satellites for effective flood management
  103. Water quality assessment and spatial–temporal variation analysis in Erhai lake, southwest China
  104. Dynamic analysis of particulate pollution in haze in Harbin city, Northeast China
  105. Comparison of statistical and analytical hierarchy process methods on flood susceptibility mapping: In a case study of the Lake Tana sub-basin in northwestern Ethiopia
  106. Performance comparison of the wavenumber and spatial domain techniques for mapping basement reliefs from gravity data
  107. Spatiotemporal evolution of ecological environment quality in arid areas based on the remote sensing ecological distance index: A case study of Yuyang district in Yulin city, China
  108. Petrogenesis and tectonic significance of the Mengjiaping beschtauite in the southern Taihang mountains
  109. Review Articles
  110. The significance of scanning electron microscopy (SEM) analysis on the microstructure of improved clay: An overview
  111. A review of some nonexplosive alternative methods to conventional rock blasting
  112. Retrieval of digital elevation models from Sentinel-1 radar data – open applications, techniques, and limitations
  113. A review of genetic classification and characteristics of soil cracks
  114. Potential CO2 forcing and Asian summer monsoon precipitation trends during the last 2,000 years
  115. Erratum
  116. Erratum to “Calibration of the depth invariant algorithm to monitor the tidal action of Rabigh City at the Red Sea Coast, Saudi Arabia”
  117. Rapid Communication
  118. Individual tree detection using UAV-lidar and UAV-SfM data: A tutorial for beginners
  119. Technical Note
  120. Construction and application of the 3D geo-hazard monitoring and early warning platform
  121. Enhancing the success of new dams implantation under semi-arid climate, based on a multicriteria analysis approach: Case of Marrakech region (Central Morocco)
  122. TRANSFORMATION OF TRADITIONAL CULTURAL LANDSCAPES - Koper 2019
  123. The “changing actor” and the transformation of landscapes
Downloaded on 18.9.2025 from https://www.degruyterbrill.com/document/doi/10.1515/geo-2020-0276/html
Scroll to top button