Does Regulation on CO2 Emissions Influence Productivity Growth?–The Empirical Test Based on DEA Analysis

Does Regulation on CO2 Emissions Influence Productivity Growth?–The Empirical Test Based on DEA Analysis

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Energy Procedia

Energy Procedia 0016 (2011) 000–000 Energy Procedia (2012) 667 – 672 www.elsevier.com/locate/procedia

2012 International Conference on Future Energy, Environment, and Materials

Does Regulation on CO2 Emissions Influence Productivity Growth?—The Empirical Test Based on DEA Analysis Cheng-bo Zhao* Department of Economy Management Huaiyin Institute of Technology, Huaian,223001,China

Abstract In this paper we examine levels and trends in conventional and regulation on CO2 emissions sensitive productivity over the period 1995 to 2007. Firstly, we estimate and compare two type TFP index from regulations on CO2 emissions to no regulations over current levels and test the difference of TFP in two kinds of conditions. The major conclusions are as follows: Under co2 emissions restrictions, the eastern region has the highest TFP Growth rate while the western region has the lowest TFP growth rate .With accounting for convention, sensitive productivity growth for 28 regions on average is slightly higher than that of regulations on CO2, and efficiency change is the main source. Out of 28 regions, eight different regions shifted the frontier at least once. Econometric analysis indicates a number of variables that has important effects on e regulation on CO2 emissions sensitive measures of productivity, including variables relating GDP per capita, technical in efficiency, capital labor ratio, the energy intensity and openness. We find that these variables have different effects. In addition, policy implications are discussed. © 2011 Published by Elsevier B.V. Selection and/or peer-review under responsibility of International Materials Science Society.

© 2011 Published by Elsevier Ltd. Selection and/or peer-review under responsibility of [name organizer] Keywords: co2 regulations; TFP; Directional Distance Functions; Malmquist-Luenberger productivity Index

1. Introduction Although total factor productivity is not a country's economic prosperity, living standards and the only measure of competitiveness, but it is the last 20 years, widely accepted measure (Lall et al.2002). In recent years, resource-saving and environment-friendly, sustainable social development issues have become hot topics of general interest, so a lot of research has been concerned about the environmental controls for the impact of conventional total factor productivity (Jaffeetal, 1995) . traditional method of measuring TFP take into account only the desired output, without considering the undesirable outputs, such as CO2 emissions. Therefore, traditional methods of measuring total factor productivity growth makes the productivity measure has gone wrong. Malmquist productivity index was first used by Caves et al. (1982) defined, post by e et al. (1997) and other scholars continue to improve, to a distance function to

Cheng-bo Zhao.Tel:13952308602 E-mail address:[email protected] 1876-6102 © 2011 Published by Elsevier B.V. Selection and/or peer-review under responsibility of International Materials Science Society . doi:10.1016/j.egypro.2012.01.108

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describe the non-parametric method. Malmquist index defined Shephard input distance function, including two orientation and output orientation. Among them, the output-oriented distance function for input elements in the premise of not increasing production to achieve the maximum expansion ratio, input-oriented distance function seeks to reduce the output elements is not achieved under the premise of the maximum contraction ratio of input. However, if there is undesirable output, Malmquist productivity index can not calculate total factor productivity. To solve this problem, Chung et al. (1997) on the Malmquist productivity index modified and Malmquist productivity index is known as Malmquist-Luenberger productivity index, the measure of the new method considers the output of undesirable the impact of productivity . This method has been widely used in the industrial sector (Fare et al. 2001, regional (Hailu, al. 2001 ) and the State (Lindenberg, 2004 ; Domazlick and Weber, 2004 [9 ]; Yoruk and Zaim, 2005 ; Kumar, 200911]; Bing, Wu Yanrui, etc., 2008 ). At present, the existing research related to this article, only Bing, Wu Yanrui et al (2008), and Bing Wang, Wu Yanrui et al (2008), APEC is the object, this paper attempts from the following three aspects of the existing literature to develop: (1) Using Malmquist-Luenberger productivity index measure and compare the different control of CO2 emissions in the two cases in 28 districts in total factor productivity growth in 1995-2007; (2) test under the control of carbon emissions in all the different TFP differences; (3) impact of carbon controls on total factor productivity growth, an empirical study of factors. 2. Malmquist–Luenberger Productivity Index This version of the directional distance function measures observations at time based on the technology at time t t 1. Chung et al. (1997) define the ML index of productivity between period t and t t 1 as: MLtt+1=

G G (1+D0t +1(xt , yt ,bt ; yt ,−bt )) (1+D0t (xt , yt ,bt ; yt ,−bt )) Gt +1 t +1 t+1 t+1 t+1 t+1 Gt t+1 t+1 t+1 t+1 t+1 (1+D0 (x , y ,b ; y ,−b ))(1+D0( x , y ,b ; y ,−b ))

(1)

The index can be decomposed into two component measures of productivity change: G ⎡ ⎤ 1+ D0t ( x t , y t , b t ; y t , − b t ) t +1 ⎥ MLt = ⎢ ⎢ 1+ DG t +1 ( x t +1 , y t +1 , b t +1 ; y t +1 , − b t +1 ) ⎥ ⎢⎣ ⎥⎦ 0 

MLEFFCH tt +1

×

G G 1+ D0t +1 ( xt , y t ,bt ; yt , − bt ) (1+ D0t +1 ( xt +1 , yt +1 ,bt +1 ; yt +1 , − bt +1 )) G 1+ D0t ( xt , yt ,bt ; yt , − bt ) 1+ D0t ( xt +1 , yt +1 ,bt +1 ; y t +1 , − bt +1 ) 

(2)

MLTECH tt +1

The first term, MLEFFCH, represents the efficiency change component, a movement towards the best practice frontier, while the second, MLTECH, the technical change, i.e., a shift. If there have been no changes in inputs and outputs over two time periods, then MLttt1=1. If there has been an increase in productivity, then MLttt1>1, and finally, a decrease when MLttt1<1. Changes in efficiency are captured by MLEFFCHttt1, which gives a ratio of the distances the countries are to their respective frontiers, in time periods t, and t+1. If MLEFFCHttt1>1, then there has been a movement towards the frontier in period t + 1. If MLEFFCHttt1< 1, then it indicates that the country is further away from the frontier in t + 1, and hence has become less efficient. If technical change enables more production of good and less production of bad outputs, then MLTECHttt1>1. Where as if MLTECHttt1<1, there has been a shift of the frontier in the direction of fewer good outputs and more bad outputs (Fa¨re et al., 2001). 3 Empirical Results According to the research methodology and the data obtained from the analysis software are two cases

Cheng-bo Zhao // Energy – 672 Author name EnergyProcedia Procedia16 00(2012) (2011)667 000–000

of total factor productivity index and its components results. The first type is to consider the carbon emissions factor is the ML productivity index, which requires the increase in the proportion of GDP with reduced CO2 emissions. The second type is not carbon emissions constraints, productivity growth and its essence is the traditional literature Malmquist productivity index. In considering the case of carbon emission control, the entire sample period, the overall average in all regions of total factor productivity index is 1.018, indicating that the total factor productivity in all regions the average annual growth rate of 1.8%, from an average sense, the total factor productivity growth was mainly from the 12.4% growth in technical efficiency to promote, technical efficiency change is the pure technical efficiency and scale efficiency of the result of two factors, the sample period, pure technical efficiency and scale efficiency increase of 11%, and 1.3, respectively, %, while changes in the rate of technological progress has worsened in the sample period, the average rate of technical progress down 9.6%. In most parts of the sample period is the increase in total factor productivity, only economically underdeveloped areas of total factor productivity is declining, they are Henan, Hubei, Guangxi, Yunnan, Qinghai, Ningxia, Beijing is the highest growth, reaching 10.5% and the lowest in Qinghai, a decrease of 12.6%. From a regional perspective, the eastern, central, western average total factor productivity index for 1.049,1.01 and 0.992, respectively, indicating that the eastern part of the average annual total factor productivity growth of 4.9%, 1.0% and 0.8% decline in the eastern and central total factor productivity growth was mainly technical efficiency is 13.5% and 13.2% growth to drive, and the deterioration rate of technological progress, in the sample period, the eastern, central and technological progress were down 7.5% and 8.0% decline in total factor productivity in the west mainly by technological progress 10.2% rate of decline is caused in the sample period, the western technical efficiency increase of 10.1%. Without considering the case of carbon emission control, the entire sample period, the overall average in all regions of total factor productivity index for the 1.034, indicating that the total factor productivity in all regions the average annual growth rate of 3.4%, from an average sense, the whole factor productivity growth was from 14.7% to promote changes in technical efficiency, technical efficiency change is the pure technical efficiency and scale efficiency the result of two factors, the sample period, pure technical efficiency and scale efficiency were 12.6% and 1.9%, while changes in the rate of technological progress has worsened in the sample period, down 9.9% rate of technological progress. Within the sample period, only the economically less developed areas is the decline in total factor productivity, which are Henan, Hubei, Guangxi, Beijing is the highest growth, reaching 11.5%, the lowest in Henan, a decrease of 18.1%.. From a regional perspective, the eastern, central, western average total factor productivity index for the 1.052,1.013 and 1.036, respectively, indicating that the eastern part of the average annual growth of total factor productivity by 5.2%, 1.30% and 3.6%, eastern, central and western growth of total factor productivity mainly by the technical efficiency of 14.5%, 14.5% and 15.9% growth to drive, and the deterioration rate of technological progress, in the sample period, the eastern, central and western technological advances fell 8.0%, respectively, 11.5 and 10.5%. 4. The Factors That Affect The Analysis of Total Factor Productivity Previously analyzed under different conditions of total factor productivity index and its components change in circumstances and regional characteristics, but not explain the reasons to affect such changes and differences, this paper on the relevant variables for further analysis. According to endogenous growth theory shows, total factor productivity and per capita GDP, capital labor ratiois positively related. Based on economic convergence theory (Lall et al, 22002), from r the region of total factor productivity near from the production frontier is lower than in areas far the production frontier. Energy intensity of carbon dioxide emissions is one of the most direct factor, and

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(

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sometimes even the same view (Ang, 1999). Different degrees of opening up areas of emissions of carbon dioxide emissions there are also positive or negative effects. Therefore, based on existing research results, this article from the economic development of the technology behind an inefficient, capital - labor ratio, energy intensity and the opening up of five to examine the impact of carbon dioxide emissions performance, Table 5 shows the correlation variable definitions, and data sources to provide an explanation, equation (3) (4) is constructed based on the impact of panel data regression model. While economic development and environmental change for the existence of inverted U-shaped relationship, different scholars from different countries is inconsistent conclusions, but they generally believe that economic development is the impact of carbon dioxide emissions is an important factor (Mills et al., 2009). Generally believed that the openness of an area emission reduction technology may exist the effect of the overflow, the carbon dioxide emissions is the differences. Therefore, based on existing research results, this article from the economic development of the technology behind an inefficient, capital - labor ratio of the number, energy intensity and opening up to examine five aspects of the impact on total factor productivity, equation (3) (4)is constructed based on the impact of panel data regression model. JJG β1t β 2 RJGDPit + β 3 D it −1 + β 4 LNCAP + β 5 EI it + β 6 OPEN it + ε it M it =+

(3)

JJG MLit = β1t + β 2 RJGDPit + β 3 D it −1 + β 4 LNCAP + β 5 EI it + β 6 OPEN it + ε it

(4)

Which, MLit、Mitrespectively, taking into account carbon emissions and does not consider carbon emissions in the region I in year t that period of total factor productivity (dependent variable), RJGDP, Dt-1, LNCAP, EI, OPEN is the impact of total factor productivity of the factors (explanatory variables ) is the parameters to be estimated, is a random perturbation. Panel data analysis taking into account possible heteroscedasticity and serial correlation, the corresponding data for this paper based on generalized least squares regression analysis, Hausman test showed that the pair should be used fixed effects regression model, Table 1 and Table 2 shows the regression results . Table 1

Determinants of Environmentally sensitive productivity change

Variable

Fixed effect model

Random effect model

Coefficient

T-value

Coefficient

T-value

Constant RJGDP RJGDP2 Dt-1 LNCAP EI OPEN

1.170*** 0.875* -0.717* 0.174*** 0.211*** -0.005+ -5.234

9.97 1.81 -1.86 3.50 3.34 -2.26 -1.61

0.939*** 1.572*** -1.364*** 0.115** -0.00004 0.001 -10.841**

11.02 4.20 -4.18 2.38 -0.001 0.84 -2.98

R2 Hausman

0.0843

0.1356 77.5

Notes. Values in parentheses represent “t-statistics.” *,**,***,and + show the level of significance at 1%, 5%, 10%, and 15% respectively.

The results can be seen from the table, except opening up of two types, the other variables are statistically significant. GDP per capita and total factor productivity are presented "inverted U" type and

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"U-type", productivity index and the lag phase of the technical inefficiency, the capital - labor ratio is positively related to both energy intensity and total factor productivity is negatively correlated. Table 2

Determinants of Conventional productivity change

Variable Constant RJGDP RJGDP2 Dt-1 LNCAP EI OPEN R2 Hausman

Fixed effect model Coefficient

T-value

7.737*** -14.394*** 9.909*** 0.362+ 1.418*** -0.236*** -80.061+ 0.003

7.86 -4.33 3.48 1.29 4.02 -2.83 -1.55

Random effect model Coefficient 3.047 -4.663+ 3.599 0.069 0.309 -0.034 -54.735** 0.015 16.68

T-value 2.89 -1.30 1.22 0.14 1.10 -1.06 -2.45

Notes. Values in parentheses represent “t-statistics.” *,**,***,and + show the level of significance at 1%, 5%, 10%, and 15% respectively.

5. Conclusion In the traditional measure of total factor productivity, due to neglect of Africa desired output of the production process, making the measurement results to bias. In this paper, Malmquis-Luenberger productivity index measurement method and compared the carbon emission control and no control of carbon emissions under the two cases, 28 provinces and autonomous regions to the relevant data for 1995-2007 as the sample application serial DEA technology, the whole factor productivity growth and the empirical analysis of influencing factors. We found that, when control of the carbon emissions of total factor productivity is the average annual increase of 1.8%, the average technical efficiency increased by 12.4%, 9.4% average annual technological progress, but no control carbon emissions, the total factor productivity increased by an average ratio of carbon emissions per year more than 1.6 percentage points during the control, 0.2 percentage point increase technical efficiency, technological progress, less 0.5 percentage points. Therefore, in an average sense, considering the carbon control, the increased level of technological progress. We also analyzed in two different cases, affect the total factor productivity growth factors. The results showed that the per capita GDP, technical inefficiency, capital labor ratio, the energy intensity of total factor productivity factors. References [1]Lall,P.,Featherstone,A.M.,Norman,D.W.,2002,Productivity growth in the Western Hemisphere (94):the Caribbean in perspective ,Journal of Productivity Analysis,17,pp.213-231. [2]Jaffe,A.B.,S.Peterson,P.Portney,andR.Stavins.1995,Environmental

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Manufacturing:What Does the Evidence Tell Us?,Journal of Economic Literature,33,pp.132-163. [3]Caves, D.W,Christensen,L.R.,&Diewert,W.E.,1982 The Economic Theory of Index Numbers and the Measurement of Input-Output, and Productivity, Econometrica,50,pp393-1414.  R.,Grosskopf,s.,1997.Productivity and undesirable outputs: a directional distance function approach. [4]Chung,Y., Fare Journal of Environmental Management 51,pp229-240  ,R,Grosskopf,s,Noh,D.W,Weber,W,2001.Characteristics of a polluting technology: theory and practice.Journal [5] Fare of Econometrics 126,pp469-492.

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[6] Hailu,A.Veeman,T.S, 2001,Non-parametric Productivity Analysis with Undesirable Outputs: An Application to the Canadian Pulp and Paper industry, American Journal of Agricultural Economics, 83,pp.605-616  ,R,Grosskopf,s,1997.Nonparametic productivity analysis with undesirable outputs: comment .American Journal of [7] Fare Agricultural Economics85(4),pp1070-1074. [8]Domazlicky.B.Weber,W.,2004,Does Environmental Protection Lead to Slower Productivity Growth in the Chemical Industry?, Environmental and Resource Economics, 28, pp 301-324. [9] Yoruk, B.K.,Zaim,O.,2005.Productivity growth in OEDE countries: a comparison with Malmquist productivity indexes. Journal of Comparative Economics 33,pp401-420 [10]Kumar,S.,2006, Environmentally Sensitive Productivity Growth:A Global Analysis Using Malmquis-Luenberger Index, Ecological Economics,56,pp.280-293.