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Article

Predicting Coal Consumption in South Africa Based on Linear (Metabolic Grey Model), Nonlinear (Non-Linear Grey Model), and Combined (Metabolic Grey Model-Autoregressive Integrated Moving Average Model) Models

1
School of Economic and Management, China University of Petroleum (East China), Qingdao 266580, China
2
School of Management & Economics, Beijing Institute of Technology, Haidian District, Beijing 100081, China
*
Author to whom correspondence should be addressed.
Sustainability 2018, 10(7), 2552; https://doi.org/10.3390/su10072552
Submission received: 31 May 2018 / Revised: 14 July 2018 / Accepted: 16 July 2018 / Published: 20 July 2018
(This article belongs to the Section Energy Sustainability)

Abstract

:
South Africa’s coal consumption accounts for 69.6% of the total energy consumption of South Africa, and this represents more than 88% of African coal consumption, taking the first place in Africa. Thus, predicting the coal demand is necessary, in order to ensure the supply and demand balance of energy, reduce carbon emissions and promote a sustainable development of economy and society. In this study, the linear (Metabolic Grey Model), nonlinear (Non-linear Grey Model), and combined (Metabolic Grey Model-Autoregressive Integrated Moving Average Model) models have been applied to forecast South Africa’s coal consumption for the period of 2017–2030, based on the coal consumption in 2000–2016. The mean absolute percentage errors of the three models are respectively 4.9%, 3.8%, and 3.4%. The forecasting results indicate that the future coal consumption of South Africa appears a downward trend in 2017–2030, dropping by 1.9% per year. Analysis results can provide the data support for the formulation of carbon emission and energy policy.

1. Introduction

In recent years, due to the strong relationship between coal consumption and carbon emission, people have paid more attention to coal consumption. However, there are many other factors causing the changes in coal consumption, in addition to the development of modern industry [1]. As the deterioration of global ecological environment, the appeal of reducing carbon emissions is stronger than ever [2,3,4,5]. Peters et al. suggested that the leading cause for current environment problems is the large use of coal by developed countries as well as a few developing countries such as China, as their pursuit of economic growth [6,7]. Therefore, they attribute the responsibility of reducing carbon emission to developed countries and some developing countries [7,8,9]. In fact, in the era of globalization, it is a shared responsibility for all countries to reduce carbon emissions and protect the environment.
Under this special background, it is of great significance to study the coal consumption of South Africa. According to the data in BP Statistical Review of World Energy, South Africa’s main energy sources include coal, oil, etc. In addition, South Africa’s coal consumption makes up 69.6% of the country’s total energy consumption and accounts for 88.7% of African coal consumption, taking the first place in Africa [10]. It illustrates that South Africa is currently excessively dependent on fossil fuel. The government is making efforts to change this situation and planning to improve renewable energy capacity before 2030. Thus, the government intended to spend $50 billion to develop renewable energy and the Renewable Energy Independent Power Producer Procurement Program was launched in 2011, which is a public-private cooperation project, working to achieve South Africa’s transformation to low-carbon economy [11,12]. Not only that, the South African government promised to reduce carbon emission by 34% in 2020 and 42% in 2025 [13]. Therefore, understanding the trend of coal consumption for South African government is important, not only for reducing carbon emissions, but also to ensure the balance of energy supply and demand. More specifically, the long-term prediction for coal consumption will provide data support for the formulation of carbon emission policy, and offer a scientific basis to the transformation of energy in South Africa.
Considering that no studies aimed to straightforwardly forecast coal consumption for South Africa using multiple models at present, the purpose of this study is to strengthen and make up related research, and provide convincing information for policy formulation. We use the mixed models of linear and nonlinear models to forecast South Africa’s coal consumption for the period of 2017–2030. The combination of several models will greatly enhance the reliability of forecasting. The remainder of the study is organized as follows: Section 2 provides a brief literature review, Section 3 introduces the methods and principles of forecasting, Section 4 presents and discusses the forecasting results, and Section 5 provides a summary of this study.

2. Literature Reviews

2.1. Study of Energy Consumption in Other Countries

The literature on energy consumption research has witnessed the emerging studies on coal consumption over the recent years. Some scholars have studied the coal consumption of different countries. For example, Wang et al. used the LMDI (Logarithmic Mean Divisia Index Model) to study the driving factors of China’s coal consumption and provided policy suggestions [7,14]; Apergis et al. made a research on the fluctuations of coal consumption according to the data of all states in America [15]; Gurgul et al. studied the coal consumption’s influence on the economic growth of Portland [16]; besides, India, South Korea, and BRICS also became research focuses in this field [17,18,19,20,21].

2.2. Study of the Energy Consumption in South Africa

In recent years, coal consumption in South Africa has caused much attention and there are many researches centering on it. The present study mainly is focused on the relationship between coal consumption, economic growth, environment, as well as policy implementation on carbon emission reduction. Ziramba adopted the autoregressive distributed lag (ARDL) model to study the long-term relationship and causal relationship between energy consumption, industrial production, and employment in South Africa, and the analysis results showed that industrial production and employment were variables of long-term electric power consumption [22]. While exploring the relationship between South Africa’s coal consumption and carbon emission, Shahbaz et al. also employed the ARDL method and the obtained results showed that economic growth would increase energy emissions; however, financial development would reduce it [23,24]. Through studying the causal relationship among economic growth, pollutant emission, and energy consumption in South Africa, Menyah et al. reported that South Africa can achieve the goal of reducing pollutant emissions by sacrificing economic growth or reducing energy consumption [25]. Al-Mulali et al. studied the effect of energy consumption and carbon emission on economic and financial development of 19 countries (including South Africa) and concluded that carbon emissions were constantly increasing with the high-speed development of national economy and finance [26]. The author suggested that these countries should use energy protection policies to control environmental pollution. Alton et al. advised government to collect carbon taxes from energy consumers, in order to achieve the goal of carbon emission reduction in South Africa until 2025 [27]. Although a great number of researchers are studying coal consumption, the objects are mainly limited to China [7], America, and India. Scholars who study the coal consumption in South Africa mainly focus on the relationship between coal consumption, economy, employment, and pollution. As an obvious result, the economic growth of South Africa will increase energy consumption as well as carbon emissions.

2.3. Study of the Applications of Energy Prediction Models

Energy forecasting models are invented to analyze the future energy development on the basis of available energy information. Their assumption is that some knowledge of the energy development has already existed to reduce energy risk and improve its safety. A large number of energy forecasting models are applied in different situation, where significant achievements have been made. Volkans used the ARIMA (Autoregressive distributed lag Model) to study the energy demand of Turkey [28]; Org used the f-ARIMA model to forecast wind speed [29]; Farahbakhsh applied the residential energy model when studying the residential energy consumption of Canada [30]. Some scholars forecasted the different energy demand based on a single model [31,32,33,34]; Okumus et al. forecasted wind energy power by combining adaptive neural-fuzzy interference system (ANFIS) model with the artificial neural network (ANN), and the obtained error was below 4% while they all exceeded 5% in previous related study [35]. After trying several arithmetic simulations, Yu discovered that Shanghai natural gas short-term load could be forecasted more accurately with relatively less iterations by optimizing Genetic algorithm model (GA Model) and the improving BP neural network [36]. In these researches, combined models are used more often than single models in energy forecasting studies, on account of achieving a higher precision. In addition, different methods apply to forecasting of different requirement and content, and we need to select the most suitable forecasting model, according to the practical situation.
As stated above, researchers have noticed the importance of coal consumption of South Africa [27,37]. However, there are no studies related to coal consumption forecasting of South Africa To improve the accuracy of the prediction, this paper using a combined method of linear and nonlinear models to forecast the coal consumption. In this study, Metabolic Grey Model (MGM), Non-linear Grey Model (NGM), and Metabolic Grey Model-Autoregressive Integrated Moving Average Model (MGM-ARIMA) combined models are used to forecast South Africa’s coal consumption in 2017–2030.

3. Methodology

3.1. The Non-Linear Grey Model

The NGM is a model based on improvement of the gray model [38]. The core of traditional gray model is a first order differential equation. In addition, the forecasting data obtained by this method always presents a linear tendency, which greatly narrows the application scope of this model. The NGM has added a power coefficient to the core differential equation, thus enabling the forecasting value to show nonlinear characteristics. The specific operation steps are shown in the following:
First, we give the first five values of the original data and name the sequence: X ( 0 ) . Then, according to accumulative principle, the original sequence can be processed into an accumulative sequence: X ( 1 )
X ( 0 ) = ( x ( 0 ) ( i + 1 ) , x ( 0 ) ( i + 2 ) , x ( 0 ) ( i + 3 ) , x ( 0 ) ( i + 4 ) , x ( 0 ) ( i + 5 ) )   ( i = 0 , 1 , n 6 )
X ( 1 ) = { x ( 1 ) ( 1 ) , x ( 1 ) ( 2 ) , , x ( 1 ) ( n ) }
For the convenience of operation, we need to define an auxiliary sequence: Z ( 1 ) ( k ) , by adding and subtracting the accumulative sequence.
Z ( 1 ) ( k ) = 0.5 x ( 1 ) ( k ) + 0.5 x ( 1 ) ( k 1 )
Based on this, the core equation of the NGM can be obtained, as shown in Equation (4). We use the least square method to solve the coefficients ‘a’ and ‘b’. Then, the solution of Equation (5) can be obtained.
x ( 0 ) ( k ) + a ( Z ( 1 ) ( k ) ) α = b
Here, ‘a’ and ‘b’ represent the coefficients of differential equation, ‘ α ’ represents power coefficient.
d x ( 1 ) ( t ) d t + a ( x ( 1 ) ( t ) ) α = b
The principle of least square method is shown in Equations (6)–(8).
[ a , b ] T = ( B T B ) 1 B T Y N
Y N = [ x ( 0 ) ( 2 ) , , x ( 0 ) ( n ) ] T
B = [ Z ( 1 ) ( 2 ) α 1 Z ( 1 ) ( 3 ) α 1 Z ( 1 ) ( n ) α 1 ]
Then introduce the known parameter value into Equation (4) and combine solution Equations (9) and (10) of four-order Lingo. Finally, the final forecasting value will be obtained by subtraction.
d X d t = F ( t , X )
{ K 1 = F ( t n , X n ) K 2 = F ( t n + h 2 , X n + h 2 K 1 ) K 3 = F ( t n + h 2 , X n + h 2 K 2 ) K 4 = F ( t n + h , X n + h K 3 ) X n + 1 = X n + h 6 [ K 1 + 2 K 2 + 2 K 3 + K 4 ]
x ^ ( 0 ) ( k + 1 ) = x ^ ( 1 ) ( k + 1 ) x ^ ( 1 ) ( k )

3.2. The Metabolic Grey Model

The MGM is different from NGM, which has no power coefficient and the specific form is shown in Equation (12). Through differentiation processing, its solution is presented in Equation (14).
x ( 0 ) ( k ) + a Z ( 1 ) ( k ) = b
d x 1 d t + a x 1 = b
x ^ k + 1 1 = ( x 1 0 b a ) e a k + b a , k = ( 1 , 2 , , m )
Here, ‘a’ and ‘b’ represent the coefficients of differential equation, and the unknown parameter can be obtained according to the solution of the following matrix. Finally, the expression of the unknown value is in Equation (17).
[ a , b ] T = ( B T B ) 1 B T Y
B = ( ( x 1 1 + x 2 1 ) / 2 1 ( x m 1 1 + x m 1 ) / 2 1 ) , Y = ( x 2 0 x m 0 )
x ^ k + 1 0 = x ^ k + 1 1 x ^ k 1 = ( 1 e a ) ( x ^ 1 0 b a ) e a k , k = ( 1 , 2 , , m )
This is the complete calculation process. The MGM is composed of complete operation and continuous cycle. Every time finishing the calculating operation, the earliest data will be removed, and the new data reflecting system characteristics is added. Every step is operated according to this procedure.

3.3. The Metabolic Grey Model-Autoregressive Integrated Moving Average Model

Five data points are selected to forecast the sixed data point, which is called a cycle process [39]. In this study, the first 5-year data sequence is used as an example. In the next forecasting cycle, we added one new data point and removed one old data point to ensure that the forecasting data size of every step is five [40].
For each cycle process, the cut data sequence is recorded as:
X ( 0 ) = { x ( 0 ) ( 1 ) , x ( 0 ) ( 2 ) , , x ( 0 ) ( n ) }
To forecast the (n + 1)th data, a differential equation is used for the auxiliary calculation and the specific steps are as follows [41]:
An accumulative sequence is defined as X ( 1 ) = { x ( 1 ) ( 1 ) , x ( 1 ) ( 2 ) , , x ( 1 ) ( n ) } .
Where x ( 1 ) ( k ) = i = 1 k x ( 0 ) ( i ) ,   k = 1 , 2 , 3 , , n . Then establish the differential equation of sequence X ( 1 ) : d x ( 1 ) d t + a x ( 1 ) = b . As long as parameters ‘a’ and ‘b’ can be solved, the solution of sequence X ( 1 ) can be obtained.
To solve this differential equation, the following auxiliary sequence is introduced: Z ( 1 ) ( k ) = 0.5 x ( 1 ) ( k ) + 0.5 x ( 1 ) ( k 1 ) .
By using the least square method, we can obtain: [ a , b ] T = ( B T B ) 1 B T Y .
Where:
Y N = [ x ( 0 ) ( 2 ) , x ( 0 ) ( 3 ) , , x ( 0 ) ( n ) ] T
B = [ Z ( 1 ) ( 2 ) 1 Z ( 1 ) ( 3 ) 1 Z ( 1 ) ( n ) 1 ] = [ ( 0.5 x ( 1 ) ( 2 ) + 0.5 x ( 1 ) ( 1 ) ) 1 ( 0.5 x ( 1 ) ( 3 ) + 0.5 x ( 1 ) ( 2 ) ) 1 ( 0.5 x ( 1 ) ( n ) + 0.5 x ( 1 ) ( n 1 ) ) 1 ]
Then, the parameters ‘a’ and ‘b’ can be acquired and the solution of sequence X ( 1 ) is:
x ^ ( 1 ) ( k ) = [ x ( 0 ) ( 1 ) b a ] e a ( k 1 ) + b a ,   k = 1 , 2 , , n
x ^ ( 0 ) ( k ) = x ^ ( 1 ) ( k ) x ^ ( 1 ) ( k 1 ) = [ x ( 0 ) ( 1 ) b a ] ( 1 e a ) e a ( k 1 ) ,   k = 2 ,   3 , , n
The next step is correcting the residual error by the ARIMA model. The ARIMA model is composed of three parts: error stabilization, moving average process, and autoregressive process [42]. These three processes correspond to Equations (5)–(7), respectively.
Y t * = ( 1 B ) d Y t
Y t * = c + α 1 Y t 1 + α 2 Y t 2 + + α p Y t p + u t
Y t * = u t + β 1 u t 1 + β 2 u t 2 + + β q u t q
Thus, the complete formula of the ARIMA model is as follows:
Y t * = c + α 1 Y t 1 + α 2 Y t 2 + + α k Y t k + μ t + β 1 μ t 1 + β 2 μ t 2 + + β q μ t q
Here, Y t represents the original sequence; Y t * represents the stationary sequence after d-order difference; d represents the order of difference; c represents the constant variable; α i and β i represent parameters; u t represents error term.
This study selected the MGM, NGM, and the MGM-ARIMA model to predict the energy consumption of South Africa. Each model has its own advantages and disadvantages. The grey model is good at describing the laws of a fuzzy system with very little information. However, the required precision can be achieved only for the first 1–2 data points of the forecast. Based on the traditional grey model, the MGM increases the running cycles and ensures the accuracy of each predicted value. However, its forecasting result cannot reflect the nonlinearity of original data series. The NGM can exhibit nonlinear traits and guarantee the update of forecasting data [43], while its calculation process is relatively complex. The MGM-ARIMA model we have established not only inherits all the advantages of the MGM model but it also has its own special advantages. The addition of ARIMA further improves the accuracy of forecasting results.

4. Empirical Results and Discussion

4.1. Display of Data

All data sources for the study are obtained from BP Statistical Review of World Energy [44]. Based on the coal consumption of South Africa during the period of 2000–2016 (as shown in Appendix A Table A1), we establish MGM, NGM, and MGM-ARIMA models to forecast the coal consumption of South Africa for 2017–2030.
During the calculating process of the three models, the entire stage can be mainly divided into two parts: fitting and forecasting. In the fitting process, the known data is calculated following the forecasting steps. Through comparing the known data with fitting results, the accuracy of the forecasting model can be judged. The forecasting process outputs the forecasting results of unknown data. By analyzing the tendency of forecasting results, we can judge the variations of coal consumption in South Africa.

4.2. Calculation Process of the MGM Model

During calculation process of MGM, old elements are removed and new elements are added. The data reflecting the system real-time characteristic is adopted for forecasting. As shown in this study, we selected five-dimensional data as the basis of modeling. For example, in the initial cycle, five-year data in 2000–2004 is used to forecast the value in 2005. We can get a series of gray differential equation coefficients via calculation. Figure 1 below shows the parameter values obtained from these cycle processes.
With the parameters in Figure 1, the final forecasting result of this model can be calculated through the formula of solving differential equation. By applying the least square method, the forecasting result of the MGM is shown in Figure 2.
As illustrated in Figure 2, the green line represents the original data of South Africa’s coal consumption, and the yellow line represents the forecasting coal consumption in 2000–2030. It shows that although the original data of 2000–2016 is slightly different from the forecasting value during the fitting stage, their overall tendency is identical. During the forecasting stage, we can see that the coal consumption calculated by the MGM is decreasing in 2017–2030.

4.3. Calculation Process of the NGM Model

In NGM model, the element of power coefficient is added to the differential equation of the traditional gray model. With the help of Matlab software, the power coefficient can be easily calculated, which is shown in Table 1.
On this basis, the final forecasting value of NGM is shown in Figure 3. It can be seen obviously that the tendency of the results in forecasting stage is consistent with the metabolic gray model, which are both decreasing. To judge the goodness of fit, in Figure 3, the blue columns represent the original value of coal consumption, while the yellow line indicates the forecasting value obtained by the NGM. Obviously, the data’s tendency during fit stage is roughly consistent with the original data.

4.4. Calculation Process of the MGM-ARIMA Combined Model

The core of the combined model calculation is using ARIMA model to correct the forecasting residuals of the MGM. In the section above, the forecasting result of the MGM has already been presented. The residual sequence can be obtained via subtraction.
The first step for ARIMA model is the unit root test of residual sequence, the purpose of which is to determine the order of difference. The differential order to make the sequence stationary is represented by the value of parameter ‘d’ in ARIMA model. Appendix A Table A2 shows the result after zero-order difference. The value of a T test is between 1% and 5%. Therefore, we can consider that under a 95% confidence interval, the sequence is stationary and d = 0.
After determining the solution of differential equation, we can obtain the values of ‘p’ and ‘q’ by drawing the relevant coefficient figure. Figure 4 is relevant coefficient figure of the sequence after zero-order difference. Here, the auto-correction coefficient figure can reflect the value of ‘q’ and the partial auto-correction figure present the value of ‘p’.
Knowing the value of ‘d’, we can get ‘p’ and ‘q’ from the correlation coefficient diagram. Comparing the three sets of possible values in Table 2, we decide to select ARIMA (5, 0, 3), because of its maximum R value.
Figure 4 shows that the partial auto-correction figure becomes stationary after five-order difference and the auto-correction coefficient figure becomes stationary after three-order difference; thus p = 5 and q = 3. Establish the ARIMA (5, 0, 3) model in SPSS software and then the corrected residuals can be obtained, as is shown in Appendix A Table A3. Based on the corrected residual sequence and original sequence, the final forecasting value of the combined model can be acquired by calculation. Figure 5 shows that the difference between fitted value and true value is very small and the forecasting result is identical to the first two models, which all show a decreasing trend.

4.5. Goodness Test of Model

To judge the goodness of the three models, we use the mean absolute percent error (MAPE) to calculate their accuracy. The specific evaluation criteria for MAPE is as follows: the value of MAPE between 20–50% indicates a reasonable forecasting effect; 10–20% indicates a good forecasting effect; 0–10% indicates an excellent forecasting effect. Here, the calculation equation for the mean absolute percent error (MAPE) is as follows:
MAPE = | Y t * Y t | / Y t N
where: Y t represents the original value; Y t * represents the predicted value; N represents the number of sample data.
As is shown in Table 3, the MAPE of the three models all remains within 5%. Therefore, the forecasting effects are excellent. This indicates that the forecasting models used in this paper are extremely applicable and the accuracy is very high.
In addition, the relative error of each year at the fitting stage can be calculated and the method of 1-relative error can be adopted.
Figure 6 shows the accuracy of the three forecasting models. We can see that the forecasting goodness of these three models exceeds 85%, and the average accuracy is 95%, in spite of the different accuracy of each year. In a word, the reliability of these three models is very high.

4.6. Forecast Results and Discussion

Table 4 presents the forecasting results of South Africa’s coal consumption in 2017–2030, and it shows that the coal consumption of South Africa will follow a stable decrease in future. This result is in line with the judgment based on the trend of South Africa’s electricity demand by 2030. Even, there are no studies related to coal consumption forecasting of South Africa. However, Inglesi et al. applied the Engle-Granger methodology for co-integration to predict long-term centricity demand in South Africa and the results showed that the South Africa’s electricity demand would reduce by 24–27% in 2030 [45]. In other words, it can indirectly indicate coal consumption may continue to decrease by 2030 because 90% of the electricity is generated from coal [46]. Besides, the decline trend of coal consumption is also consistent with the direction of policy adjustment in South African government.
For this forecasting result, we will discuss from the following aspects:
First, the mean absolute percent error of the forecasting models (MGM, NGM, MGM-ARIMA) has averaged 4 percent. On the one hand, the existing error assessment criteria clearly states that as long as the value of MAPE is less than 5%, the prediction effect of the model is excellent. The three values of MAPE given in Table 3 are all less than 5%, which implies that the forecasting results in this study are very convincing. On the other hand, these three models still have some deficiencies in prediction. For example, these models belong to the category of time series forecasting models. The time series prediction model only shows good effect at the simulation of the sequence itself. However, the future trend of a sequence is not only influenced by its historical data, but also by other variables. In other words, this prediction model used in this study cannot reflect the effect of other factors on the system. Neglecting the changes in internal factors maybe lead to inaccurate predictions, which need to be overcome in subsequent studies.
Second, coal consumption’s downward trend is related to changes in the energy structure of the world today. With the continuous decline in the running cost of natural gas, exports of natural gas continue to increase. This has led to the fact that coal has become less competitive. Apart from this, with the emphasis on air pollution and climate warming, more and more investment has been made in renewable energy power generation equipment. In other words, alternatives to coal, such as wind, solar energy, and hydropower, are becoming commonplace.
Third, the downward trend of coal consumption in the future will have an impact on South Africa’s coal development and policy formulation. For coal development, although the future coal consumption is declining, it is still the major source of power generation in a short period of time. Thus, future investment should be placed on the improvement of existing power equipment and the development of cleaning equipment. For policy formulation, the South African government should gradually reduce the dependence on coal over the next 14 years. At the same time, policy formulation should be focused on how to reduce the production costs of natural gas. In addition, the subsidies of renewable energy power generation equipment should be strengthened continuously.

5. Conclusions

South Africa is a country that the energy sources are diversified, such as solar energy and wind energy [12,47,48]; however, its coal consumption represents 88.7% of the total consumption of the whole African continent. In addition, it covers 69.6% of the energy consumption of South Africa. The significant coal consumption leads to a large amount of carbon emission in South Africa. Furthermore, it will cause global ecological deterioration. Therefore, the longterm prediction of South Africa’s coal consumption can provide a data support for global environmental governance.
This study adopted linear (MGM and MGM-ARIMA) and nonlinear (NGM) models to forecast South Africa’s coal consumption in 2017–2030. The error in these three forecasting models is all below 5%: MGM (4.9%), NGM (3.8%), and MGM-ARIMA (3.4%). The small forecasting error indicates the high reliability of the three models in forecasting the long-term coal consumption. During the next 14 years, the development tendency of South Africa’s coal consumption will follow an annual decrease of 1.9%. This result shows that South Africa is reducing its dependence on coal. This also indicates that the strategy of increasing the use of renewable energy, formulated by the South African government, has scored remarkable achievements, which contributes to the carbon emission reduction [49,50].

Author Contributions

M.M. and S.L. performed the experiments, analyzed the data and contributed reagents/materials/analysis tools. M.S., F.J. and R.L. conceived and designed the experiments and wrote the paper. All authors read and approved the final manuscript.

Acknowledgments

This work is supported by the Shandong Provincial Natural Science Foundation, China (ZR2018MG016), the Initial Founding of Scientific Research for the Introduction of Talents of China University of Petroleum (East China) (YJ2016002), and the Fundamental Research Funds for the Central Universities (17CX05015B). We have received the grants in support of our research work. The funds we have received for covering the costs to publish in open access.

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A

Table A1. Coal consumption in South Africa 2000–2016 (Unit: Mtoe).
Table A1. Coal consumption in South Africa 2000–2016 (Unit: Mtoe).
YEAR200020012002200320042005
Coal Consumption74.63174.89871.24779.18986.76779.988
YEAR200620072008200920102011
Coal Consumption81.47383.66193.33693.82492.82390.512
YEAR20122013201420152016
Coal Consumption88.33988.61389.83983.35085.108
Table A2. The Result of unit root test.
Table A2. The Result of unit root test.
Augmented Dickey-Fuller t-StatisticProb. *
Test statistic −4.136210.0269
Test critical values:1% level−4.72836
5% level−3.75974
10% level−3.32498
* Denotes rejection of the hypothesis at the 0.05 level.
Table A3. Initial error and corrected error of residual sequence.
Table A3. Initial error and corrected error of residual sequence.
YearError of MGMError Forecast by ARIMA (5, 0, 3)
20000.0000−1.21
20013.4894−1.17
2002−4.3812−1.38
2003−0.9070−3.24
20041.9398−2.64
2005−9.8511−1.97
2006−6.3175−1.62
20071.78315.12
200812.369210.5
2009−2.0981−0.69
2010−7.4760−6.96
2011−7.4566−7.17
2012−1.9373−0.24
20131.83351.93
20143.41640.58
2015−5.5212−4.18
20160.9243−0.11
2017 −1.93
2018 −2.39
2019 −5.61
2020 −1.79
2021 0.91
2022 1.41
2023 −1.8
2024 −3.55
2025 −3.6
2026 −2.48
2027 −1.71
2028 −0.84
2029 −0.4
2030 −1

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Figure 1. Value of MGM model parameters. Note: The values of ‘a’ and ‘b’ in Figure 1 correspond to Equation (13). Figure 1 shows the solution of ‘a’ and ‘b’ in Equation (13).
Figure 1. Value of MGM model parameters. Note: The values of ‘a’ and ‘b’ in Figure 1 correspond to Equation (13). Figure 1 shows the solution of ‘a’ and ‘b’ in Equation (13).
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Figure 2. The forecasting of the MGM model.
Figure 2. The forecasting of the MGM model.
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Figure 3. Forecasting of the NGM model.
Figure 3. Forecasting of the NGM model.
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Figure 4. Correlation plot of the stationary sequence.
Figure 4. Correlation plot of the stationary sequence.
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Figure 5. Forecasting of the MGM-ARIMA model.
Figure 5. Forecasting of the MGM-ARIMA model.
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Figure 6. Accuracy of forecasting of all three models.
Figure 6. Accuracy of forecasting of all three models.
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Table 1. Power coefficient of the NGM model.
Table 1. Power coefficient of the NGM model.
YEAR2004200520062007200820092010
The Power Coefficient10.8420.0010.001110.001
YEAR201120122013201420152016
The Power Coefficient110.9130.00111
Note: The Power coefficient ‘ α ’ corresponds to Equation (5).
Table 2. Results of R value test.
Table 2. Results of R value test.
ARIMA (p, 0, q)R Value
(5, 0, 3)0.634
(4, 0, 3)0.549
(5, 0, 2)0.614
Table 3. Goodness of fit.
Table 3. Goodness of fit.
MGMNGMMGM-ARIMA
MAPE4.938%3.821%3.439%
Table 4. Final forecasting period 2017–2030 (Unit: Mtoe (Million Tons of Oil Equivalent)).
Table 4. Final forecasting period 2017–2030 (Unit: Mtoe (Million Tons of Oil Equivalent)).
YearMGMNGMMGM-ARIMA
201782.564782.129580.6347
201880.252681.557977.8626
201979.907680.165374.2976
202077.538878.668275.7488
202176.26577.143377.175
202274.985475.632376.3954
202373.250374.156671.4503
202472.045272.723868.4952
202570.611971.334667.0119
202669.212369.988266.7323
202767.954768.682466.2447
202866.58367.415465.743
202965.300766.18664.9007
203064.041764.992863.0417

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Ma, M.; Su, M.; Li, S.; Jiang, F.; Li, R. Predicting Coal Consumption in South Africa Based on Linear (Metabolic Grey Model), Nonlinear (Non-Linear Grey Model), and Combined (Metabolic Grey Model-Autoregressive Integrated Moving Average Model) Models. Sustainability 2018, 10, 2552. https://doi.org/10.3390/su10072552

AMA Style

Ma M, Su M, Li S, Jiang F, Li R. Predicting Coal Consumption in South Africa Based on Linear (Metabolic Grey Model), Nonlinear (Non-Linear Grey Model), and Combined (Metabolic Grey Model-Autoregressive Integrated Moving Average Model) Models. Sustainability. 2018; 10(7):2552. https://doi.org/10.3390/su10072552

Chicago/Turabian Style

Ma, Minglu, Min Su, Shuyu Li, Feng Jiang, and Rongrong Li. 2018. "Predicting Coal Consumption in South Africa Based on Linear (Metabolic Grey Model), Nonlinear (Non-Linear Grey Model), and Combined (Metabolic Grey Model-Autoregressive Integrated Moving Average Model) Models" Sustainability 10, no. 7: 2552. https://doi.org/10.3390/su10072552

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