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This study parametrically and non-parametrically estimates the TFEE

scores for 47 regions in Japan and the determinants of inefficiency for

1996–2008. We extend the SFA approach employed by Zhou et al. (2012) and

Hu (2013) and incorporate the technical inefficiency effects model proposed

by Battese and Coelli (1995). Our two technical inefficiency effects models

exclusively include the manufacturing industry share and the five

energy-intensive industry shares as environmental variables that influence

inefficiency, the scores of which are referred to as TFEESFA,M and TFEESFA,E,

respectively. For comparison, a stochastic TFEE without environmental

variables, TFEESFA,O, is also computed. In addition, we use the DEA technique

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The four TFEEs are highly correlated with one another, especially

TFEESFA,O, TFEESFA,M, and TFEESFA,E. The trend of the mean TFEEs suggests

that energy efficiency improved during the sample period. However, there is

considerable potential for further savings on energy consumption in the

Japanese regions. For the bottom three regions—Chiba, Okayama, and

Oita—the TFEE scores in all four models are very low (<0.2). This suggests

the possibility of conserving more than 80% of energy in all three regions.

We compare not only the TFEEs but also the determinants of inefficiency

between SFA and DEA. In SFA, the determinants are estimated simultaneously

with inefficiency. This simultaneous estimation suitably incorporates

influences from environmental variables into inefficiency. This is SFA’s

advantage over the two-step estimation in DEA. But in the SFA estimation, we

must introduce additional assumptions regarding a functional form of the

frontier and a distribution of inefficiency and error terms compared to DEA.

On the other hand, the inefficiency of the DEA TFEEs is regressed on

environmental factors via a Tobit approach. The signs of the Tobit model are

consistent with those of the SFA estimation. For both SFA and DEA, the

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manufacturing and wholesale and retail trade shares, the lower the energy

efficiency. The results that include energy-intensive industry’s shares show

that the higher shares of chemicals; iron and steel; non-metallic mineral

products; and pulp, paper, and paper products industries, the significantly

lower the levels of efficiency.

Our study has two limitations. First, in our SFA model, all inefficiencies

are attributed to energy input. This may lead to overestimating energy

inefficiency. On this point, DEA is superior to SFA because the DEA TFEE

takes into account both radial and non-radial slack with respect to energy

inputs. The second limitation is that the estimates do not consider unobserved

heterogeneity.

Our approach can be extended in various directions. First, the

environmental variables that affect energy efficiency should be further

explored. It is important not only to measure efficiency but also to examine the

determinants of inefficiency. Second, the functional form can be easily

changed from the Cobb-Douglas function to more general functional forms

such as a translog function. Third, undesirable outputs should be added to the

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in the form of emissions and waste.

Acknowledgments

The authors thank the participants at the 2013 APEC Conference on Low

Carbon Town and Physical Energy Storage. This work was supported by the

Grant-in-Aid for Scientific Research from the Japan Society for the Promotion

of Science (#25380346) and Taiwan’s National Science Council (NSC

102-2410-H-009-045).

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