To increase eco-efficiency, the process of the social economic development of Binh Duong
province to simultaneously satisfy three objectives: Increase the value of social and economic
development (increase SDI), Reduce exploitation and consumption of resources (reducing RCI),
and Reduce environmental pressures (reducing EPrI).
Binh Duong province tends to develop economic and social tradition, social and economic
growths high, and high demand for using of natural resources. That also means that a large
amount of natural resources will continue to be exploited, leading to a volume of waste from
production and consumption will be released into the natural environment. Meanwhile, the
province's eco-efficiency can be increased. However, this increase goes against the objectives of
sustainable development of Binh Duong Province. So based on the above objectives, in order to
enhance the ecological performance, Binh Duong province necessarily changes the approach of
social and economic development in addition to the implementation of environmental protection
measures former. To reduce pressure on the environment, Binh Duong province also need to
make reducing resource consumption in the production process
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Journal of Science and Technology 54 (2A) (2016) 251-258
APPLICATION OF PRINCIPLE COMPONENT ANALYSIS TO
BUILD PROVINCIAL ECO-EFFICIENCY INDEX FOR BINH
DUONG PROVINCE FROM 2001-2012
Doan Ngoc Nhu Tam
1, *
, Che Dinh Ly
2
1
Institute for Computational Science and Technology, Ho Chi Minh City, Vietnam
2
Faculty of Environment, University of Science, Vietnam National University Ho Chi Minh City,
227 Nguyen Van Cu, District 5, Ho Chi Minh City, Vietnam
3
Center of Water Management and Climate Change, Ho Chi Minh City, Vietnam
*
Email: tamdnn@tdmu.edu.vn
Received: 5 May 2016; Accepted for publication: 26 June 2016
ABSTRACT
Based on a proposed concept of Regional Eco-Efficiency of Zhou Zhenfeng, a set of
indicators for assessing, eco-efficiency of provincial level has been conducted. Set of indicators
included 26 indicators, and was divided into 3 groups: Socio-Economic Development Index
(SDI) (9 indicators); Resources Consumption Index (RCI) (7 indicators) and Environmental
Pressure index (EPrI) (10 indicators). Principle component analysis (PCA) was used to assess
Eco-efficiency Synthetic Index (ESI) of Binh Duong province in the 2001-2012. Results shown
that the ESI of Binh Duong province has been clearly improving from 2001-2012. RCI and EPrI
respectively had a significant correlation with SDI. Results also have been shown that the
industrialization generated waste and if the pollution control solution is not effectively so
environmental pressure is continuously increase and degrade the environment.
Keywords: Regional Eco-Efficiency, Eco-efficiency Synthetic Index, Socioeconomic
development index (SDI), Resource consumption index (RCI), Environmental Pressure index
(EprI), Principle component analysis (PCA).
1. INTRODUCTION
“Eco-efficiency” is built by the World Business Council for Sustainable Development
(WBSCD) in the early 1990s. Eco-efficiency is a useful tool for managing and evaluating the
effectiveness between economic income and resource consumption and environmental pollution.
Although the concept of eco-efficiency is quite common in business, the concept of eco-
efficiency to not be noticed Provincial research to help policy makers know: How effective
when we compared the provincial process of industrialization to the costs of resource use and
environmental remediation. Therefore, since many countries around the world have carried out
research projects to calculate and assess the eco-efficiency for different regions. Zhou Zhenfeng
[1] - studied the ecological performance for Chengyang District; Thailand, 2007 - Conference to
Doan Ngoc Nhu Tam, Che Dinh Ly
252
build eco-efficiency to assess economic growth in Bangkok, Thailand; Per Mickwitz; Matti
Melanen [2] - in Finland has done quite a program for regional research Kymenlaasko to
develop indicators and eco-efficiency calculations for the area. Francois Schneider, 2001 [3] -
aims at setting out: opportunities and limits of eco-efficiency strategies for regions. We can say
in Vietnam, eco-efficiency studies in policy evaluation are generally still limited.
Binh Duong is a newly re-established province; the southeastern zone is located in the
southern key economic. Through the development process re-established after 12 years, Binh
Duong is one of the local rapid economic growth and has high competitiveness. However, along
with the achievements in the development process, Binh Duong also suffered the environmental
consequences of economic development is not consistent with the trend of sustainable
development such as water pollution, more polluted air, increasingly impaired resources....
Therefore, Binh Duong needs to evaluate the economic performance and environmental quality
in the last stages of development. An effective approach to quantitative evaluation system is
based on Eco-efficiency indicators to calculate and evaluate the Eco-efficiency Synthetic Index
of Binh Duong. The goal of the project is to calculate and assess the ecological performance of
economic activity Binh Duong period 2001-2012 and to propose measurement to improve the
ecological performance of Binh Duong area.
2. METHODS
This article presents only limited calculation and assess the ecological performance.
Primary and secondary data, economical data, social and environmental situation of Binh Duong
period 2001-2012 were collected from Statistical Yearbooks and reports of departments and
agencies. Applied computational methodology Regional Eco-efficiency, evaluated, selected and
adjusted to fit the conditions of Binh Duong from the calculation methodology ecological
performance of Chinese authors and Finland. To integrate the directive into component
indicators of ecological efficiency, applied weights output from the main component analysis
(PCA).
3. RESULTS AND DISCUSSION
3.1. Set the indicators to calculate Regional Eco-efficiency Provincial
The indicators in the performance index calculation Regional Eco-efficiency is very diverse
and rich. The selection of indicators calculated, assessed Regional Eco-efficiency in Binh Duong
province was based on the following basic principles:
1. Simple, easy to understand and represent the trends over time.
2. Fit in linking with information systems and forecasting, the indicators should ensure
openness, facilitates regular updates over time.
3. Compatible with the national index.
4. The selected indicators to ensure the viability and quantify the database of existing
statistical systems in Binh Duong Province.
Accordingly, the directive applies to calculating Regional Eco-efficiency Binh Duong
includes 25 indicators, divided into 3 groups of indicators used to calculate the index
components:
1. Indicators of Socioeconomic Development Index (SDI) include 9 indicators.
Application of Principle Component Analysis to build Provincial Eco-Efficiency Index
253
2. Indicators of Resources Consumption Index (RCI) include 7 indicators.
3. Indicators of Environmental Pressure Index (EPrI) include 10 indicators.
Selected indicators were used to calculate Regional Eco-efficiency Provincial.
Table 1. Synthesis indicators which used in calculating Regional Eco-efficiency in Binh Duong Province.
Group
indicators
Indicator Sign Unit
Socio-
Economic
Developme
nt Index
(SDI)
1. Average population SDI1 People
2. Population density SDI2 People/km2
3. The rate of natural population growth SDI3 0/00
4. GDP SDI4 Billion dong
5. GDP per capita SDI5 Million dong/person
6. Rate workers were trained in economics SDI6 %
7. Local Income SDI7 Billion dong
8. The percentage of hospital beds per 10,000
people
SDI8 Beds / people
9. Unemployment rate SDI9 %
Resources
Consumpti
on Index
(RCI)
10. Water consumption RCI1 Million m3
11. Power Consumption RCI2 Million Kwh
12. Consumption of fertilizers RCI3 Ton
13. Mining of Minerals RCI4 thousand tons
14. Forest exploitation RCI5 thousand m3
15. The total area of agricultural land RCI6 ha
16. The total area of non-agricultural land RCI7 ha
Environme
ntal
Pressure
Index
(EPrI)
17. Waste amounts of industrial dust EPrI1 Ton
18. Waste amounts of industrial SO2 EPrI2 Ton
19. Waste amounts of industrial CO EPrI3 Ton
20. Waste amounts of BOD EprI4 Ton
21. Waste amounts of TSS EprI5 Ton
22. Total flow of domestic wastewater EprI6 m3/day
23. Total flow of industrial wastewater EprI7 m3/day
24. The volume of industrial solid waste EprI8 Ton
25. The volume of domestic solid waste EprI9 Ton
26. The area of damaged forests EPrI10 Hectares
Doan Ngoc Nhu Tam, Che Dinh Ly
254
Applying the component analysis methods for establishing the weights to the indicators.
3.2. Method of Principle Components Analysis_ PCA
Method of Principle Components Analysis_ PCA is used to build weights for the indicators
participate to calculate through the use of computational software Minitab 16 (Minitab Inc -
United States). The Method of Principle Components Analysis_ PCA uses statistical analysis of
correlation among variables and these variables are explained about the general connotation
(factors). It provides a method of condensing the information contained in the original variables
(Xi) into a smaller set of connotations (elements) (principle components)
with i = 1, 2, 3.,n.
In there Y: are the principle components; ei are eigen vectors; Xi are the original variables
(indicators). Using software was used to render principle components. The annual standardized
indicators be included in the equation principle components, and calculations. Use eigenvalues
(% variable volume) results from factor analysis, linear weights applied Yi assigned to all, and
this value will be the sum of the sustainability indicators.
3.3. The model calculates the index components of the provincial-level Regional Eco-
efficiency
To build Regional Eco-efficiency Index for Binh Duong province, authors evaluated two
basic methodologies of the calculation for an area is Regional Eco-efficiency of Finland and
China. The calculation method of Finland requires a large volume of data related to the socio-
economic activities as well as the environmental impact throughout the region. Besides the
annual statistics, this method requires the calculation details and stream flows into the region
through a combination of methods of assessment of product life cycle (Life Cycle Assessment,
LCA) and material flow analysis (material flow analysis, MFA). In Vietnam conditions, the
implementation of the above calculation is very difficult, not only requires a lot of time, funding
but also needs the cooperation of the various agencies to perform. Meanwhile, the calculation
methodology by Zhou Zhenfeng et al. [1] performed much simplified. The authors have also set
up a system to calculate basic indicators of Eco-efficiency for a region. In the data condition
existing, the authors have adopted the methodology of Zhou Zhenfeng et al. [1] to calculate
Regional Eco-efficiency in Binh Duong province. Regional Eco-efficiency in Binh Duong
province is calculated based on three indices: Socioeconomic Development Index (SDI),
Resources Consumption Index (RCI) and Environmental Pressure Index (EPrI). The calculation
steps of ESI in Binh Duong:
• Step 1: Collect, calculate and aggregate progress indicator value of the index components
from 2001 to 2012.
• Step 2: Standardize data provided by the same dimensions for the indicator values of
advantages for the development process in accordance with fuzzy logic rules:
Si = (S - Smin) / (Smax-Smin) (1)
Note: Si: The value of the indicator standardized i
th
;
S: The value of the indicator i
th
in measuring the current state of the system research;
Smax: The maximum value of the i
th
indicator in the research system;
Application of Principle Component Analysis to build Provincial Eco-Efficiency Index
255
Smin: minimum value of the i
th
indicator in the research system.
• Step 3: Using the method of analysis of the PCA to determine the weight of the indicators
through the use of software Minitab 16.
• Step 4: As the weights were determined by PCA, SDI component indexs, RCI and EPRI
were estimated by the following formula:
S=
m
i
WiCi
1
(2)
S: are the value of the index scores of SDI, RCI and EPRI; Wi: The weight of the i
th
;indicators;
Ci: The value of the i
th
indicator after data standardization; m: Number of indicators.
• Step 5: Apply the formula to calculate the composite index Regional Eco-efficiency set by
Zhou Zhenfeng et al. [2]:
2/)( EPIRCI
SDI
ESI . (3)
3.4. Application of computational steps in case of Binh Duong Province
3.4.1. Description of the study area, Binh Duong Province
Regarding the industrial development, from 2001 to 2012, this is a 12-year period after the
re-establishment, the total development investment capital increased by 3.8 times. In 2001, the
province has 3,051 businesses engaged in manufacturing industry and by 2012 had doubled to
6731 enterprises. Number of employees participating in the industrial activity increased rapidly,
within 12 years the number of industrial workers increased by 5.6 times.
3.4.2. Calculate and analyze the Regional Eco-efficiency Index of Binh Duong in 2001-2012
period
According to the principles and methodology presented above, using data gathered from
years 2001-2012, the calculation of the index components were made as follows:
1. Standardize data indicators of indexes: SDI (SDI1-SDI9) by the method mentioned
above fuzzy theory, RCI and EPRI (EPrI1-EPrI10) was calculated.
2. Using software Minitab 16 to perform analysis for the weighted PCA of SDI, RCI and
EPrI.
3. According to the calculation, SDI index will have two main components are drawn.
These two components represent 97.5 % of the difference of the directive join SDI index
calculation. For RCI index, it also has 2 main components are drawn, representing 94.8% of the
variation of the directive join RCI index calculation. Also has three main components are drawn
into the directive join as EPRI calculated, 3 components represent 99.5% of the variation of the
directive.
4. Using the formula (1) and (2) to calculate the index scores for SDI, RCI and EPRI. Using
the formula (3), to calculate the index scores for the ecological synthetic performance of Binh
Duong Province. Results are presented in Table 2 below:
Doan Ngoc Nhu Tam, Che Dinh Ly
256
Table 2. Summary of SDI, RCI, EPRI and Regional Eco-efficiency Index of Binh Duong period
2001-2012.
3.5. Assessment of regional Eco-efficiency Index of Binh Duong province in period of
2001-2012
Based on the results of calculation of the index scores components: SDI, RCI, EPRI and
ESI, we can draw graphs to show trends over time evolution of the above indexes.
Figure 1. The trend movements of each index components: SDI, RCI, EPrI, and ESI performance.
SDI has a slow downward trend from 2001 to 2010 but from 2010 to 2012 it increases
rapidly; meanwhile, resource consumption index-RCI decreases steadily over the years, but the
rate of reduction is still slow. For environmental pressure index _ EPRI, in the period 2001-2012
there have been many changes. In the early years 2001-2010, EPRI has decreased, but at a
slower pace, especially within 3 years (from 2010-2012), environmental pressures up Binh
Duong province up from the early years of establishment Binh Duong. Eco-efficiency Synthetic
Index - ESI of Binh Duong is the integration of the component index, SDI, RCI and EPRI, it
shows the general trends of the three index components. Overall, the ESI index of Binh Duong
province has improved significantly in 12 years. From 2005-2007, ESI has been trending
downwards, but from 2007 onwards, the ESI has improved and tends to increase. Tendency to
slow growth of Eco-efficiency Synthetic Index - ESI of Binh Duong fitted the changes in the use
of resources and environmental pressures of the province. Besides determining the correlation
coefficient between SDI and RCI, between SDI and EPRI, the study also identifies the
regression model between these factors in the regression equation in Figure 2 as below:
Year 2001 2000 2001 2002 2003 2004 2005 2006 2007 2008 2011 2012
SDI 0,50 0,52 0,53 0,51 0,36 0,30 0,12 0,17 0,12 0,16 0,43 0,55
RCI 0,77 0,79 0,67 0,59 0,51 0,42 0,31 0,26 0,22 0,22 0,15 0,02
EprI 0,59 0,38 0,4 0,21 0,1 0,2 0,07 0,18 0,07 0,03 0,38 0,61
ESI 0,74 0,89 0,99 1,28 1,18 0,97 0,63 0,77 0,83 1,28 1,62 1,75
Application of Principle Component Analysis to build Provincial Eco-Efficiency Index
257
Figure 2. Correlation of SDI and RCI (left), SDI and EPRI (right).
EPRI tended to decrease during the period 2005-2006, then continued to rise, but a slower
pace than in the early years. EPRI increase is unavoidable for the economic development
situation of Binh Duong now.
3.6. Propose measurements to improve the ecological performance of Binh Duong
To increase eco-efficiency, the process of the social economic development of Binh Duong
province to simultaneously satisfy three objectives: Increase the value of social and economic
development (increase SDI), Reduce exploitation and consumption of resources (reducing RCI),
and Reduce environmental pressures (reducing EPrI).
Binh Duong province tends to develop economic and social tradition, social and economic
growths high, and high demand for using of natural resources. That also means that a large
amount of natural resources will continue to be exploited, leading to a volume of waste from
production and consumption will be released into the natural environment. Meanwhile, the
province's eco-efficiency can be increased. However, this increase goes against the objectives of
sustainable development of Binh Duong Province. So based on the above objectives, in order to
enhance the ecological performance, Binh Duong province necessarily changes the approach of
social and economic development in addition to the implementation of environmental protection
measures former. To reduce pressure on the environment, Binh Duong province also need to
make reducing resource consumption in the production process.
4. CONCLUSIONS
The research results show that the ecological performance Binh Duong Province improved
markedly from 2001 to 2012. Reporting has developed a set of indicators to assess the Eco-
efficiency Synthetic Index of Binh Duong includes 26 indicators, divided into 3 groups: Social
economic development indicators (SDI) (9 indicators); Resource consumption indicators (RCI)
(7 indicators) and Environmental Pressure indicators (EPrI) (10 indicators). To integrate the
indicators into component indicators of ecological efficiency, the report has successfully used
the PCA method and calculate ESI of Binh Duong Province in period of 2001-2012: ESI = (SDI)
/ [RCI + EPRI) / 2].
Doan Ngoc Nhu Tam, Che Dinh Ly
258
Eco-efficiency Synthetic Index - ESI of Binh Duong province over the years are:
Between Socioeconomic Development Index (SDI), Resources Consumption Index (RCI)
and Environmental Pressure Index (EPrI) there is a very close relationship in models:
RCI = 0.7388 - 3.795 SDI + 4.837 SDI^2 [R
2
=81,3, F=20, p value=0]
EPrI = 0.4421 - 3.581 SDI + 7.320 SDI^2 [R
2
=75, F= 13, p value = 0]
The research results have proposed solutions that Binh Duong improve ecological
performance in the next stage. Including: the solutions of socio-economic development, continue
to promote the strengths of Binh Duong province to promote economic growth. Besides, they
also proposed measures to limit the economic dependence of Binh Duong on excessive
consumption of resources, as well as implementing measures reduce environmental pressures in
the industrial, urban and agricultural areas of the province.
REFERENCES
1. Zhou Zhenfeng, Sun Lei, Sun Yinglan - Research on Indicator System of Regional Eco-
efficiency: A Case Study of Chengyang District, Chinese Journal of Population,
Resources and Environment 4 (4) (2006) 54-58.
2. Per Mickwitz, Matti Melanen, U. R. J. S. - Measuring regional eco-efficiency - case
Kymenlaakso. Key results of the ECOREG project, The Finnish Environment 735en,
Edita Prima Oy, Helsinki, Finland, 2004, pp.1-112.
3. Francois Schneider - Eco-efficiency of regions. 7th European Roundtable on Cleaner
Production. Sustainable Europe Research Institute, Schwarzspanierstr. 4/8, A-1090
WIEN. Lund 2-4 May 2001, pp.1-22.
Year 2001 2000 2001 2002 2003 2004 2005 2006 2007 2008 2011 2012
ESI 0,74 0,89 0,99 1,28 1,18 0,97 0,63 0,77 0,83 1,28 1,62 1,75
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