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2021 | OriginalPaper | Buchkapitel

2. International Experiences of Ecotaxes: A Few Lessons

verfasst von : Rajat Verma

Erschienen in: Fiscal Control of Pollution

Verlag: Springer Singapore

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Abstract

There are countries which have implemented ecotax system; here, in order to understand the ecotaxes world over, an extensive examination of the international experiences of fifteen countries has been undertaken so as to comprehend the relative experiences in not just levying ecotaxes but also for analysing the status of other fiscal instruments such as subsidies, rebates, etc. The two primary questions explored in this chapter are: first, what is the superiority and limitations of ecotaxes over other Environmental Fiscal Instruments (EFIs) and what lessons can India deduce from the design of EFIs in other countries? To answer these questions, the experiences are analysed and categorised into two groups: OECD and emerging economies. Former group consisted of eleven OECD countries, and of these, five were Nordic, and others included Australia, Canada, Netherlands, Germany, United Kingdom and United States of America. Among the emerging economies, Brazil, India, China and South Africa were chosen so as to make the analysis comparable. The revenues from these taxes were computed and examined. The explanations for the computed revenues in the fifteen countries have been deduced from: the analyses of the data points, mathematical reasoning, policies adopted and the variances in the tax rates. The major outcome of this analysis is that energy taxes followed by transport taxes were the most prevalent forms of ecotaxes across the OECD countries. Further, pollution taxes could be difficult to implement because such instruments would require complex and costly administrative and technological structures. The revenue as a proportion of GDP and total tax revenue in OECD countries ranges from 2 to 4% and 5 to 10%, respectively, with US and Canada being an exception. On the other hand, for emerging economies ratio of revenue to GDP and total net indirect tax revenue is between 0 to 1% and 1 to 10%, respectively. All these results could be explained from the fiscal policies followed by these countries. The OECD/EEA database, which is the only major database, did not comprehensively compile the EFIs of developing countries, especially that of India.

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Fußnoten
1
Market failure can be defined simply as a condition where a sub-optimal (inefficient) level of output is produced. Therefore, it does not necessarily imply that market for a good does not exist it simply means that the provisioning of the good in market is sub-optimal; i.e., it does not maximise total surplus.
 
2
‘Environmental fiscal reform (EFR) refers to a range of taxation and pricing measures which can raise fiscal revenues while furthering environmental goals. This includes taxes on natural resource exploitation or on pollution. EFR can directly address environmental problems that threaten the livelihoods and health of the poor. EFR can also free up economic resources or generate revenues that can help to finance access of the poor to water, sanitation and electricity services’ (OECD, 2005) as cited in Schlegelmilch et al. (2009).
 
3
“Environmental tax reform (ETR) is a reform of the national tax system where there is a shift of the burden of taxation from conventional taxes, for example on labour, to environmentally damaging activities, such as resource use or pollution. The burden of taxes should fall more on ‘bads’ than ‘goods’ so that appropriate signals are given to consumers and producers and the tax burdens across the economy are better distributed from a sustainable development perspective” (European Environment Agency, 2005 as cited in Schlegelmilch et al., 2010).
 
5
The OECD-EEA database refers these taxes as ‘Environmentally Related Taxes’ and not environmental taxes. The name itself widens the scope of green taxes, but it also limits the effect of these taxes in curbing pollution. A more detailed explanation of this issue has been addressed in Sect. 3.2 of Chap. 3.
 
6
Eurostat (2001), as also cited in Steinbach et al. (2009), has the following definitions:
Energy taxes are taxes on energy products like petrol, diesel, electricity, coal, etc., which are used for transportation and stationary purposes, as well as a tax on CO2.
Transport taxes are those which are confined to the ownership and the usage of vehicles, including taxes on the aviation industry’..
Pollution taxes are those levied on activities which pollute water and air and those which create noise pollution and solid waste. These are targeted by measuring the emission levels from these activities. A tax on sulphur dioxide also comes under this category’.
Resource taxes are taxes on activities which deplete natural resources such as water and forests’. In the Netherlands, there is a tax on groundwater extraction which fits in this category, and in India, certain states levy a ‘forest development tax’ which would also come under this category. This has been detailed in Sect. 1.​1.​2.
 
7
Environmental levies imply five categories of environmentally related taxes and fee/charge.
 
8
This is one of our earlier analyses of ecotaxes in India and China.
 
9
Environmental taxes/charges are referred to as environmental levies from here on.
 
10
ETR includes revenue from environmental fees/charges.
 
11
Since, the patterns are almost similar, the graphs have not been included in the text.
 
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Metadaten
Titel
International Experiences of Ecotaxes: A Few Lessons
verfasst von
Rajat Verma
Copyright-Jahr
2021
Verlag
Springer Singapore
DOI
https://doi.org/10.1007/978-981-16-3037-8_2

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