Abstract
This paper introduces an alternative environmentally sensitive productivity growth index, which is circular and free from the infeasibility problem. In doing so, we integrated the concept of the global production possibility set and the directional distance function. Like the conventional Malmquist-Luenberger productivity index, it can also be decomposed into sources of productivity growth. The suggested index is employed in analyzing 26 OECD countries for the period 1990–2003. We also employed the conventional Malmquist-Luenberger productivity index, the global Malmquist productivity index and the conventional Malmquist productivity index for comparative purposes in this empirical investigation.
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Notes
The M index does not take into account the effect of environmentally harmful by-products in general. When using the M index in empirical investigation of this paper, we did not include environmentally harmful by-products.
The GM index also does not consider the effect of environmentally harmful by-products in general. Hence, we did not include environmentally harmful by-products when using the GM index in the empirical investigation.
Using a slightly different perspective, the infeasibility problem could be solved by augmenting the infeasibility problem inherent in the super-efficiency measure. The infeasibility in the super-efficiency measure is well discussed in Xue and Harker (2002) and Chen (2005). Authors are grateful to anonymous referees for their constructive comments.
Jeon and Sickles (2004) show that the average M and ML indexes of OECD countries are 1.0113 and 1.0116, respectively. Those of Asian countries are 0.9996 and 0.9963, respectively.
Berg et al. (1992) address a fixed-type benchmark technology frontier. Although the benchmark technology frontier is constructed at time period t = 1 or t = T, their work is notable in that it opens up the possibility of choosing a fixed benchmark technology frontier. We are grateful to Associate Editor for this invaluable comment.
When variable returns to scale is assumed, it is needed to check if the non-convexity problem occurs (Kuosmanen 2005; Kuosmanen and Podinovski 2009). An empirical investigation shows that the CRS (VRS) assumption yields a convex (non-convex) PPS. We are grateful to Associate Editor for this comment.
In calculating the ML index, a linear programming infeasibility occurred. When this problem occurred, we employed the window analysis.
Authors are grateful to anonymous referees for their constructive comments on this nonparametric test.
Note that previous literature employ the ML and M indices.
Cumulative efficiency change in Zhou et al. (2010) is minus 4.5%. See footnote 10 for reasons of the difference.
Zhou et al. (2010) report that cumulative technical change is 30.4%, which is significantly larger than our result. For the reasons of the difference, see footnote 10
As discussed in footnote 4, Jeon and Sickles (2004) show that for OECD countries the ML index is slightly larger than the M index. The difference between Jeon and Sickles (2004) and this study seems to come from (a) the different time span, and (b) the different sample countries including the rapid carbon-emitting countries such as Korea and Turkey.
The results of Jeon and Sickles (2004) reveal that six countries (China, France, Italy, Japan, Spain and Sweden) are green countries. Their results also reveal that 10 countries (Austria, Belgium, Canada, Finland, Germany, Ireland, Japan, Norway, Korea and Taiwan) are yellow countries. Seven out of remaining 11 countries cannot be compared because their indexes are not available.
Kumar (2006) reports that six countries (Hong Kong, Iceland, Japan, Luxembourg, the Netherlands and Switzerland) are innovators during the period between 1971–1992, which is smaller than ours. It appears that increase in the number of innovators during our study period (1990–2003) reflects the fact that the advancement of environment-related technologies has been made.
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Acknowledgments
The author would like to thank Almas Heshmati for very helpful comments and suggestions on an earlier version of this paper. He is also grateful to three anonymous referees and the Editors of Journal of Productivity Analysis for constructive comments. He would also thank Phillip Greene and Julia Chang for carefully reading this paper.
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Appendix
Appendix
Proposition 1
The GML index and its decomposed components are circular.
Proof
In order to save space, we substitute input and output vector in a parenthesis of a distance function with a time index. For example, D t(x t, y t, b t) is equivalent to D t(t). Then,
\(\square\)
Proposition 2
If undesirable outputs are excluded from directional distance functions andg = g y = y, then GML ≡ GM and ML ≡ M.
Proof
PPS is redefined as follows.
Then
Then D(x, y | y) = 1/D(x, y) − 1, where \(D({\bf x}, {\bf y}) =\min\{\delta \vert{\bf y}/{\delta} \in \Uppsi({\bf x}) \}\) is an output-oriented distance function. This relationship can be shown as follows:
Then GML ≡ GM since
The relationship between the ML and the M indices is trivial. \(\square\)
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Oh, Dh. A global Malmquist-Luenberger productivity index. J Prod Anal 34, 183–197 (2010). https://doi.org/10.1007/s11123-010-0178-y
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DOI: https://doi.org/10.1007/s11123-010-0178-y
Keywords
- Global Malmquist-Luenberger productivity index
- Circularity environmentally sensitive productivity growth
- Directional distance function