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For any question on data and metadata, please contact: Eurostat user support |
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1.1. Contact organisation | Central Statistics Office |
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1.2. Contact organisation unit | Enviroment |
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1.5. Contact mail address |
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2.1. Metadata last certified | 12/07/2022 | ||
2.2. Metadata last posted | 12/07/2022 | ||
2.3. Metadata last update | 07/07/2023 |
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3.1. Data description | |||
Data presents environmental tax revenue (by tax category - energy, transport, pollution and resource taxes) broken down by economic activity (tax payer), using the NACE classification for production activities extended to cover taxes payable by households and non-residents. |
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3.2. Classification system | |||
Environmental tax revenue is broken down by: A. Classification according to type of environmental tax For analytical purposes, the environmental taxes are divided into four categories: B. Environmental taxes by economic activity Environmental tax revenues are allocated to the different tax payers: |
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3.3. Coverage - sector | |||
Environmental taxes by economic activity data cover taxes payable by all sectors of the economy: producers (economic activities by NACE), households as consumers as well as non-residents. |
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3.4. Statistical concepts and definitions | |||
The environmental tax statistics are compiled based on Eurostat’s 2013 'Environmental taxes - a statistical guide'. Environmental tax is defined as "A tax whose tax base is a physical unit (or a proxy of a physical unit) of something that has a proven, specific negative impact on the environment, and which is identified in ESA2010 as a tax". Environmental tax statistics are part of European environmental economic accounts, which constitute satellite accounts to national accounts. Thus, environmental tax statistics follows ESA2010 definition of ‘taxes’. Consequently, only payments that are identified as taxes in the national accounts can be reported as environmental taxes whereas other types of payments to government are not excluded from the scope of the data collection. Compliance with the tax definition of the national accounts improves international comparability of the statistics, and is in line with the guidance, concepts and definitions of the System of environmental and economic accounting (SEEA). |
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3.5. Statistical unit | |||
Data refer to environmental taxes collected by the government and payable by the different economic agents. |
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3.6. Statistical population | |||
The target population are all production sectors by NACE, households as consumers and non-residents. |
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3.7. Reference area | |||
The geographical area of the Republic of Ireland. |
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3.8. Coverage - Time | |||
The data is available annually from 1995 to 2021 |
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3.9. Base period | |||
Not applicable. |
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Million National Currency (MNAC) |
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The data refer to the calendar years. |
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6.1. Institutional Mandate - legal acts and other agreements | |||
Statistics on environmental taxes are based on Regulation (EC) No. 691/2011 (Annex II) on European environmental economic accounts as amended by Regulation 538/2014, as well as legal acts in the area of national accounts. Data transmission became obligatory in September 2013. Before, Eurostat collected the data on a voluntary basis. The basis for the national accounts tax aggregates is Table 9 "Detailed tax and social contribution receipts by type of tax or social contribution and receiving sub-sector including the list of taxes and social contributions according to national classification" of the ESA2010 transmission programme - Annex B of Regulation (EU) No. 549/2013 of the European Parliament and of the Council of 21 May 2013 on the European system of national and regional accounts in the European Union. Moreover, Commission Regulation (EC) N° 995/2001 of 22 May 2001 implementing Council and European Parliament Regulation (EC) N° 2516/2000 of 10 July 2000 on the recording of taxes and social contributions sets the rules for the data sources, time of recording and comparable treatment of taxes and social contributions assessed but unlikely to be collected. |
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6.2. Institutional Mandate - data sharing | |||
Not applicable. |
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7.1. Confidentiality - policy | |||
No confidentiality policy applies to data |
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7.2. Confidentiality - data treatment | |||
No confidentiality policy applies to data |
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8.1. Release calendar | |||
The Environment Taxes release was done on 12 July 2022, 11am on the CSO website. |
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8.2. Release calendar access | |||
https://www.cso.ie/en/releasesandpublications/ep/p-eaet/environmenttaxes2021/ |
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8.3. Release policy - user access | |||
Released to the public |
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See concept 8.1 |
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10.1. Dissemination format - News release | |||
CSO Website https://www.cso.ie/en/ |
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10.2. Dissemination format - Publications | |||
CSO Website https://www.cso.ie/en/ |
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10.3. Dissemination format - online database | |||
10.3.1. Data tables - consultations | |||
Not applicable. |
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10.4. Dissemination format - microdata access | |||
Not applicable. |
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10.5. Dissemination format - other | |||
CSO Website https://www.cso.ie/en/ |
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10.5.1. Metadata - consultations | |||
Not applicable. |
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10.6. Documentation on methodology | |||
Methodology section of latest environment tax release. https://www.cso.ie/en/methods/environment/environmenttaxes/ |
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10.6.1. Metadata completeness - rate | |||
Not applicable. |
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10.7. Quality management - documentation | |||
This can be found on the methodology section of latest environment tax release. https://www.cso.ie/en/methods/environment/environmenttaxes/ |
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The estimation is based on maintaining overall environment tax amounts from the NTL as control totals throughout the estimation procedure. The procedure itself follows the guidelines set out in the Eurostat publication, “Environmental taxes A statistical Guide, 2013 edition”. The Irish specific estimation procedure has been coded in SAS, this approach ensures the data and programming are maintained separately (unlike an Excel based solution). Thus new data that might involve revisions can be readily incorporated without contaminating the procedural aspects of the estimation. Accordingly the estimates are considered reliable |
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11.1. Quality assurance | |||
Quality assurance is set out in the quality report (https://www.cso.ie/en/media/csoie/methods/environmentaltaxes/Standard_SIMS_Quality_Report_for_Environment_Taxes_2021.pdf). This follows the general standard setout by the CSO for methods and quality. |
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11.2. Quality management - assessment | |||
See above sections 11 and section 13 for the Quality management and assessment breakdown. |
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12.1. Relevance - User Needs | |||
Not applicable. |
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12.2. Relevance - User Satisfaction | |||
Not applicable. |
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12.3. Completeness | |||
The European Parliament and Council decided environmentally related taxes by economic activity shall be provided, through Regulation (EU) No 691/2011 on European environmental accounts adopted on 6 July 2011. These environmentally related taxes are an important policy instrument to influence economic behaviour by “getting the prices right”. These statistics are consistent with the System of Environmental-Economic Accounting (SEEA-CF) adopted the United Nations Statistical Commission as a world-level statistical standard in March 2012. These statistics provide key data within the overall framework of environment statistics that contributes to addressing these needs for Ireland and the EU. Environmental policy aims to reach national and international environmental and sustainable development goals. In this context the European Action Programme to 2020 calls for applying the polluter-pays principle more systematically, through phasing out environmentally harmful subsidies and shifting taxation away from labour and towards production. Here environment taxes can serve to discourage behaviour that is potentially harmful to the environment and can provide incentives to lessen the burden on the environment and preserve it by ‘getting the price right’. The economic rationale for environment taxes comes from their ability to influence markets in a cost-effective way, unlike regulatory or administrative approaches aimed at changing how we impact on the environment. Accordingly, detailed environment tax data are needed to enable policy makers assess the environmental impact of a certain tax, such as the reduction in pollution resulting from the introduction of a new tax, and more importantly assess the proportion of overall tax burden that is environmental. This release provides key data within the overall framework of environment statistics that contributes to addressing these needs for Ireland. In summary, the key driver for the compilation of environment tax estimates comes from the need of policy makers to assess the environmental impact of a certain tax, such as the reduction in pollution resulting from the introduction of a new tax, and importantly assess the proportion of overall tax burden that is environmental. |
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12.3.1. Data completeness - rate | |||
Not applicable. |
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13.1. Accuracy - overall | |||
The main data sources are the NTL, the Use Table from Supply-Use Tables (SUT) compiled by National Accounts and CO2 Emissions data available internally in Environment division. All these data sources are aggregate data. Environment Taxes are then estimated by a process that involves weighting NTL aggregates using weights derived from SUT and CO2 Emissions aggregates for the relevant year. The weights applied depend on the particular type of tax, for example Energy taxes use both SUT and CO2 Emissions weights with the latter applied to fuels. Significantly, only relevant products (rows) are selected from the UT to create weights for distributing NTL aggregate tax amounts. For example, for certain energy taxes Electricity and Gas (NACE 35) production is the row of the table chosen to compute weights to distribute the aggregate amount of tax across each industry using that product. This approach will be elaborated further below. As stated the estimation is based on maintaining overall environment tax amounts from the NTL as control totals throughout the estimation procedure. The procedure itself follows the guidelines set out in the Eurostat publication, “Environmental taxes A statistical Guide, 2013 edition”. The Irish specific estimation procedure has been coded in SAS, this approach ensures the data and programming are maintained separately (unlike an Excel based solution). Thus new data that might involve revisions can be readily incorporated without contaminating the procedural aspects of the estimation. Accordingly the estimates are considered reliable. |
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13.2. Sampling error | |||
Not applicable. |
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13.2.1. Sampling error - indicators | |||
Not applicable. |
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13.3. Non-sampling error | |||
There is no non-sampling error |
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13.3.1. Coverage error | |||
Not applicable. |
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13.3.1.1. Over-coverage - rate | |||
Not applicable. |
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13.3.1.2. Common units - proportion | |||
Not applicable. |
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13.3.2. Measurement error | |||
Not applicable. |
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13.3.3. Non response error | |||
Not applicable. |
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13.3.3.1. Unit non-response - rate | |||
Not applicable. |
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13.3.3.2. Item non-response - rate | |||
Not applicable. |
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13.3.4. Processing error | |||
There is no non-sampling error |
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13.3.5. Model assumption error | |||
Not applicable. |
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14.1. Timeliness | |||
The last day of the reference period is 31/12/21 so when the data was released on 12/7/22 it was 6 months and 12 days later |
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14.1.1. Time lag - first result | |||
The definition is looking for the last result but since that was added in the next section I assume you are looking for the first result. The first day of the reference period is 1/1/17 so when we submitted it on 21/04/23 it was 6 years 4 months and 21 days later |
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14.1.2. Time lag - final result | |||
The last day of the reference period is 31/12/17 so when we submitted it on 21/04/23 it was 5 years, 4 months and 22 days later. |
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14.2. Punctuality | |||
First sent on 21/04/23 with a deadline of 30/04/23 |
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14.2.1. Punctuality - delivery and publication | |||
Not applicable. |
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Time maintained via NTL environment tax amounts and temporarily consistent estimation methods. |
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15.1. Comparability - geographical | ||||||||||||||||||||
Not applicable - Only National level estimates compiled. Comparability with other countries is therefore not applicable. |
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15.1.1. Asymmetry for mirror flow statistics - coefficient | ||||||||||||||||||||
Not applicable. |
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15.2. Comparability - over time | ||||||||||||||||||||
Maintained via NTL |
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15.2.1. Length of comparable time series | ||||||||||||||||||||
Annually from 1995 to 2021 |
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15.2.2. Comparability - over time detailed | ||||||||||||||||||||
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15.3. Coherence - cross domain | ||||||||||||||||||||
See main choerance and comparability section |
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15.3.1. Coherence - sub annual and annual statistics | ||||||||||||||||||||
See main choerance and comparability section |
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15.3.2. Coherence - National Accounts | ||||||||||||||||||||
See main choerance and comparability section |
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15.3.2.1. Coherence - National Accounts detailed | ||||||||||||||||||||
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15.4. Coherence - internal | ||||||||||||||||||||
See main choerance and comparability section |
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N/A Data is taken provisionally from National tax authority. |
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17.1. Data revision - policy | |||
Revisions will be made annually as more up to date UTs become available. Indeed, the need for annual revisions based on more up to date UTs is highlighted in the Eurostat publication, “Environmental taxes A statistical Guide, 2013 edition”. For the 2019 return revisions are made to the years 2015, 2016 and 2017 based on the latest UT with the 2018 UT being provisional. Further revisions have been made for the years 2002 through 2015 on foot of the inclusion of Carbon Credits from 2006 and a correction relating to a double count of the Landfill Levy and Plastic bag Levy – the amounts however are relatively small and so do not substantially alter the overall taxes. Revision to years 2014 and 2015 affecting Energy taxes have also occurred due to the unavailability of up-to-date air emissions data to allocate some fuel taxes. To ameliorate this problem we have used the UT for 2018 (provisional estimates) and graduated air emissions from the 2014 to 2018 to provide a smooth transition. Recently, methodological improvements have been incorporated into the Business Energy Use Survey. These improvements have induced significant revisions to our Environment Taxes estimates across the transport and warehousing sectors over the years 2013 to 2021. |
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17.2. Data revision - practice | |||
See data revision - policy for details |
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17.2.1. Data revision - average size | |||
Minor level revision |
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17.2.2. Status of data | |||
1995-2021 is final. |
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18.1. Source data | |||||||||||||||||||||||||||||||||||||||||||||
National Accounts |
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18.1.1. Source data detailed | |||||||||||||||||||||||||||||||||||||||||||||
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18.2. Frequency of data collection | |||||||||||||||||||||||||||||||||||||||||||||
Annual |
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18.3. Data collection | |||||||||||||||||||||||||||||||||||||||||||||
N/A |
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18.4. Data validation | |||||||||||||||||||||||||||||||||||||||||||||
N/A |
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18.5. Data compilation | |||||||||||||||||||||||||||||||||||||||||||||
See attached document. Annexes: 18.5 |
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18.5.1. Imputation - rate | |||||||||||||||||||||||||||||||||||||||||||||
Not applicable. |
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18.5.2. Use of imputation methods | |||||||||||||||||||||||||||||||||||||||||||||
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18.5.3. Compilation of estimations | |||||||||||||||||||||||||||||||||||||||||||||
Please see attached word document.
Annexes: 18.5.3 |
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18.5.4. Compilation of revenue payable by non-residents | |||||||||||||||||||||||||||||||||||||||||||||
We take the Use table weighting for exports amount of tax and further allocate it according to overseas tourism numbers of tourist to (tourist+buiness) |
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18.5.5. Compilation of revenue broken down by payer for years before 2008 | |||||||||||||||||||||||||||||||||||||||||||||
To comply with the spirit of EU Regulation (EU) 691/2011 we have endeavoured to make available a continuous series of environment tax estimates from 2000 onward. To facilitate this it has been necessary to compile the UTs for 2000 to 2007 under the NACE Rev. 2 classification as UTs for those years are currently only published in Ireland under the older NACE Rev. 1.1 classification of economic activity. The methodology used to compile UTs under NACE Rev. 2 for 2000 to 2007 is not trivial. Firstly and obviously values for activity codes headings with a one-to-one match are copied directly, about 2/3rd’s of all matches were of this type. Where mismatches occur two methods are adopted. Specifically, many-to-one matches from NACE Rev. 1.1 to Rev 2. are simple aggregations. For one-to-many activity code headings matched from Rev. 1.1 to Rev 2 a split of the Rev. 1.1 amount was needed. The weights used to allocate the single NACE Rev. 1.1 amount in the UT to many NACE Rev 2 amounts was derived from the corresponding split of the United Kingdom’s UT for relevant year. Because of the two-way structure of the UT the allocation was applied both row wise and column wise to arrive at a valid two-way allocation. This highly intricate procedure was programmed in SAS to ensure the structure of the two-way transformations applied were identical across all years 2000-2007, in other words only the within year weights changed from year to year. The resulting NACE Rev. 2 UT was then used as described earlier to compile the environment taxes estimates for the years 2000 to 2007. Backcast were also required for the year 1995 to 1999. These were generated using a time series model. Specifically we applied curvilinear time trend (PROC Forecast in SAS) to each reversed NACE Rev. 2 sub-series within the energy and transport tax categories. These values were then proportionately adjusted so that the within year totals for that tax category agreed with the value in the NTL. |
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18.6. Adjustment | |||||||||||||||||||||||||||||||||||||||||||||
Not applicable |
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18.6.1. Seasonal adjustment | |||||||||||||||||||||||||||||||||||||||||||||
Not applicable. |
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