Abstract
The paper presents the results of an ex-ante evaluation of the economy-wide benefits that may be achieved through the implementation of the 20-year Energy Efficiency Action Plan (EEAP) in Thailand. The objective of the EEAP is to reduce energy intensity by 25 % in 2030 compared to 2010. This is to be reached by reducing the projected energy consumption by 20 % or 38 Mtoe until 2030. We have specified an analytical framework, which allows for a calculation of the overall energy cost savings, energy import cost reductions and reduced CO2 emissions. Moreover, we calculated the induced energy efficiency investments, employment effects and impacts on governmental budget. The evaluation shows that an effective implementation of the plan may lead to a reduction in energy expenditure of 37.7 billion EUR by 2030. Moreover, the EEAP-induced energy savings will significantly reduce the greenhouse gas emissions as well as Thailand’s energy import costs and generate private investment in energy efficiency of about 5 billion EUR annually in 2030, which in turn may lead to about 300,000 new jobs. The size of the net impact of the plan on Thailand’s governmental budget is uncertain due to positive and negative effects on corporate and income tax revenues, expenses for unemployment benefits, governmental energy consumption, expenses for energy subsidies and energy tax income.
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Notes
Kilotonne of oil equivalent. 1ktoe = 41.9 TJ = 11.6 GWh (IEA 2015).
Tonne of oil equivalent.
While energy security was enhanced by expanding domestic hydropower between the 1960s and 1990s, such infrastructure projects have been facing tremendous public opposition since the mid-1990s (Greacen and Palettu 2007).
The EEAP includes values on expected energy savings, cost savings, CO2 reductions, but no information on the calculation approach and the assumptions.
The quantification of rebound effects is outside the scope of this study.
Emission estimations are based on CO2eq emission factors from the EEAP and therefore include not only carbon dioxide but also other greenhouse gases as CO2 equivalents.
For savings from ‘traditional’ and ‘modern renewable energies’ listed in the EEAP impact assessment, the emission factor for biomass/charcoal listed was applied.
For the conversion of end-use electricity to primary energy, a conversion factor of 2.5 has been applied. This factor results from average Thai electricity generation efficiency of about 40 % (Enerdata 2014).
In practice, reductions in energy demand may impact the relative share of energy products (and the power plant loading order), as well as line losses (operating at capacity vs. below capacity). These effects can have significant impacts on greenhouse gas emissions but cannot be treated here.
Energy efficiency subsidy programme in Thai industrial sector. Data on 428 energy efficiency measures are available to the authors (Nexant 2003).
The external validity of non-Thai CSE values (i.e. their transferability) is questionable but the best approach at hand.
Note: This approach calculates additional investments in energy efficiency, irrespective of the financing source. The investments may either come from other sectors, crowding-out alternative investments or be additional if funded, e.g. by additional credit programmes.
Direct policy implementation costs have not been considered in this evaluation.
In a previous version of this paper (Suerkemper et al. 2014), we used data from World Energy Outlook 2013. Note that IEA has revised Thai subsidy figures for the years 2011–2012 substantially and published new data for 2013 in the 2014 World Energy Outlook (IEA 2014b). For this study, this led to a downward revision of subsidy figures by about 2/3.
Greacen and Greacen (2012) discuss how Thai utilities can be incentivised to promote energy efficiency.
For details on deductions and allowances, see The Revenue Department (2013b).
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Acknowledgments
The research was partly funded by the International Climate Initiative (ICI) of the German Federal Ministry for the Environment, Nature Conservation, Building and Nuclear Safety (BMUB). We are grateful for the very helpful and detailed comments of several anonymous referees which greatly improved the paper. We also thank Thomas Adisorn for his support in revising the paper and Gregory Scutt for proofreading. Helpful comments to an earlier conference version were also provided by panellists of the IEPPEC 2014 conference.
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Appendix
Appendix
Input data: energy savings as expected by the EEAP
2011 | 2012 | 2013 | 2014 | 2015 | 2016 | 2017 | 2018 | 2019 | 2020 | 2021 | 2022 | 2023 | 2024 | 2025 | 2026 | 2027 | 2028 | 2029 | 2030 | |||
Transport | Total | ktoe | 57 | 158 | 531 | 1146 | 805 | 1350 | 2130 | 2750 | 4153 | 4275 | 5085 | 5924 | 6789 | 7685 | 8619 | 9585 | 10,579 | 11,603 | 12,658 | 15,323 |
Thermal | ktoe | 57 | 158 | 531 | 1146 | 805 | 1350 | 2130 | 2750 | 4153 | 4275 | 5085 | 5924 | 6789 | 7685 | 8619 | 9585 | 10,579 | 11,603 | 12,658 | 15,323 | |
Electricity | ktoe | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | |
GWh | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Industry | Total | ktoe | 18 | 50 | 429 | 1521 | 2634 | 3774 | 4916 | 6057 | 7200 | 8360 | 9629 | 10,886 | 12,092 | 12,611 | 13,131 | 13,757 | 14,373 | 14,992 | 15,625 | 16,256 |
Thermal | ktoe | 2 | 5 | 255 | 1039 | 1822 | 2655 | 3488 | 4322 | 5155 | 5988 | 6918 | 7847 | 8758 | 9135 | 9512 | 9939 | 10,366 | 10,793 | 11,219 | 11,646 | |
Electricity | ktoe | 16 | 45 | 174 | 482 | 812 | 1119 | 1428 | 1735 | 2045 | 2372 | 2711 | 3039 | 3334 | 3476 | 3619 | 3818 | 4007 | 4199 | 4406 | 4610 | |
GWh | 184 | 525 | 2038 | 5658 | 9531 | 13,129 | 16,748 | 20,371 | 24,000 | 27,838 | 31,807 | 35,659 | 39,126 | 40,792 | 42,465 | 44,804 | 47,031 | 49,284 | 51,703 | 54,107 | ||
Large commercial buildings | Total | ktoe | 12 | 26 | 182 | 342 | 509 | 679 | 851 | 1089 | 1319 | 1558 | 1810 | 2055 | 2246 | 2416 | 2595 | 2798 | 3001 | 3211 | 3418 | 3631 |
Thermal | ktoe | 2 | 4 | 31 | 78 | 125 | 178 | 230 | 283 | 336 | 389 | 455 | 514 | 548 | 563 | 578 | 606 | 634 | 661 | 676 | 692 | |
Electricity | ktoe | 10 | 22 | 151 | 264 | 384 | 501 | 621 | 806 | 983 | 1169 | 1355 | 1541 | 1698 | 1853 | 2017 | 2192 | 2367 | 2550 | 2742 | 2939 | |
GWh | 118 | 260 | 1770 | 3103 | 4503 | 5883 | 7280 | 9451 | 11,534 | 13,715 | 15,902 | 18,092 | 19,918 | 21,747 | 23,664 | 25,725 | 27,788 | 29,922 | 32,170 | 34,493 | ||
SME and residence | Total | ktoe | 74 | 158 | 296 | 490 | 690 | 854 | 1010 | 1196 | 1354 | 1526 | 1671 | 1836 | 2070 | 2278 | 2499 | 2712 | 2929 | 3157 | 3395 | 3635 |
Thermal | ktoe | 33 | 67 | 104 | 171 | 240 | 300 | 361 | 424 | 489 | 556 | 615 | 676 | 768 | 832 | 898 | 961 | 1026 | 1092 | 1161 | 1231 | |
Electricity | ktoe | 41 | 91 | 192 | 319 | 450 | 554 | 649 | 772 | 865 | 970 | 1056 | 1160 | 1302 | 1446 | 1601 | 1751 | 1903 | 2065 | 2234 | 2404 | |
GWh | 478 | 1058 | 2261 | 3747 | 5282 | 6498 | 7606 | 9052 | 10,148 | 11,389 | 12,396 | 13,618 | 15,290 | 16,967 | 18,792 | 20,553 | 22,338 | 24,232 | 26,219 | 28,213 | ||
Total | Total | ktoe | 160 | 392 | 1438 | 3500 | 4639 | 6656 | 8906 | 11,092 | 14,026 | 15,719 | 18,195 | 20,702 | 23,197 | 24,990 | 26,844 | 28,852 | 30,883 | 32,963 | 35,095 | 38,845 |
Thermal | ktoe | 94 | 235 | 921 | 2434 | 2993 | 4483 | 6210 | 7779 | 10,133 | 11,208 | 13,073 | 14,961 | 16,863 | 18,215 | 19,607 | 21,091 | 22,604 | 24,149 | 25,714 | 28,891 | |
Electricity | ktoe | 66 | 157 | 517 | 1066 | 1646 | 2173 | 2696 | 3313 | 3893 | 4511 | 5122 | 5741 | 6334 | 6775 | 7237 | 7761 | 8279 | 8814 | 9381 | 9954 | |
GWh | 780 | 1842 | 6069 | 12,507 | 19,316 | 25,510 | 31,634 | 38,875 | 45,683 | 52,943 | 60,105 | 67,368 | 74,334 | 79,506 | 84,921 | 91,081 | 97,157 | 103,439 | 110,092 | 116,813 |
Corporate tax
Income tax rates
Thai personal income taxes follow a progressive scheme (see Table 7). These rates are to be paid on the Footnote 19
Energy taxes
Petroleum products are charged with excise tax, municipality tax, VAT on wholesale price as well as on retail price. Conservation and oil fund levy are not affecting the governmental budget; these levies are for cross subsidisations of petroleum products and the promotion of energy efficiency measures. In cases of unknown price structures, only VAT was considered for tax revenue calculation.
Natural gas is primarily consumed in the industrial sector. As industry can reclaim VAT, respective revenues are not counted as ‘foregone’.
Electricity is consumed in all sectors. Foregone VAT revenues are calculated for the residential sector. As industry can reclaim VAT, respective revenues are not counted as ‘foregone’.
For coal and renewables, no information on taxes was available and thus not accounted for in the calculations.
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Suerkemper, F., Thema, J., Thomas, S. et al. Benefits of energy efficiency policies in Thailand: an ex-ante evaluation of the energy efficiency action plan. Energy Efficiency 9, 187–210 (2016). https://doi.org/10.1007/s12053-015-9357-z
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DOI: https://doi.org/10.1007/s12053-015-9357-z