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| For any question on data and metadata, please contact: Eurostat user support |
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| 1.1. Contact organisation | Estonian Environment Agency |
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| 1.2. Contact organisation unit | Enviormental use department |
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| 1.5. Contact mail address | Mustamäe tee 33, 10616, Tallinn, Estonia |
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| 2.1. Metadata last certified | 18 June 2025 |
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| 2.2. Metadata last posted | 18 June 2025 |
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| 2.3. Metadata last update | 18 June 2025 |
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| 3.1. Data description | ||||||||||||
Reporting with the new calculations rules. The derogation to make use of average loss rates is not applicable. |
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| 3.1.1. Description of the parties involved in the data collection | ||||||||||||
Table : Institutions involved in the collection of data and distribution of tasks
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| 3.2. Classification system | ||||||||||||
Estonia use a standard classification. |
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| 3.2.1. Classification of treatment operations | ||||||||||||
Estonia use a standard classification. |
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| 3.3. Coverage - sector | ||||||||||||
All sectors |
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| 3.4. Statistical concepts and definitions | ||||||||||||
Estonia does not take into account the amount of wooden packaging that is repaired for reuse in the calculation of the targets laid down in point (f), point (g) (ii), point (h) and point (i) (ii) of Article 6(1) of Directive 94/62/EC. Estonia takes into account the amount of metals in incineration bottom ash (IBA) for the calculation of the targets. |
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| 3.4.1. Types of reuse system in place for each material type | ||||||||||||
Reuse systems are used, but we do not use this in our calculations. Amounts of reusable packaging are shown in Table 3. |
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| 3.4.2. Other recovery of waste | ||||||||||||
Bottom ash from the incineration of mixed municipal waste also contains glass packaging waste. As it goes to cover the landfill, then the glass contained in the bottom ash is taken into account as other recovery. Only the quantity from the incineration of mixed municipal waste generated in Estonia has been taken into account and the ash that remained in the warehouse has not been taken into account. |
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| 3.4.3. Information on temporary storage of packaging waste | ||||||||||||
Temporary storage of packaging waste were not largely used. Amounts of temporary storage of packaging waste are shown in waste reports. No estimates or surveys are used. |
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| 3.5. Statistical unit | ||||||||||||
waste company |
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| 3.6. Statistical population | ||||||||||||
Total packaging waste disposed of in the national territory collected by waste operators in all waste streams. |
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| 3.7. Reference area | ||||||||||||
Covers the entire territory of Estonia |
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| 3.8. Coverage - Time | ||||||||||||
year based |
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| 3.9. Base period | ||||||||||||
Not applicable |
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Tonnes |
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Calendar year |
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| 6.1. Institutional Mandate - legal acts and other agreements | |||
Packaging Act, Packaging Register Regulation, Waste Act Directive 94/62/EC, Decision 2005/270/EC |
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| 6.2. Institutional Mandate - data sharing | |||
Based on the law and cooperation agreements |
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| 7.1. Confidentiality - policy | |||
The quality report is not confidential. |
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| 7.2. Confidentiality - data treatment | |||
Not applicable |
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| 8.1. Release calendar | |||
Every year on November 15. |
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| 8.2. Release calendar access | |||
annual |
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| 8.3. Release policy - user access | |||
annual, free access |
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annually |
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| 10.1. Dissemination format - News release | |||
Environmental portal and press releases. Estonia does not keep records of the number of press releases submitted. |
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| 10.2. Dissemination format - Publications | |||
Final report: Mixed household waste, separately collected paper and packaging waste, and waste electrical and electronic equipment. A study of the composition and quantities. (file only available in Estonian): Envir. |
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| 10.3. Dissemination format - online database | |||
environmental portal: www.keskkonnaportaal.ee |
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| 10.4. Dissemination format - microdata access | |||
Microdata which is not part of enterprise secret can be downloaded as opendata. |
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| 10.5. Dissemination format - other | |||
Data are submitted to Eurostat in accordance with the guidelines of the European Commission. |
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| 10.6. Documentation on methodology | |||
Inhouse methodology is not publicly available. The survey of the composition of mixed municipal waste, separately collected waste paper and packaging waste and WEEE is public. |
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| 10.7. Quality management - documentation | |||
In-house quality validation standard |
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| 11.1. Quality assurance | |||
Quality is assured via inner procedures. We have guidelines (not for public use) and procedures descriptions explaining the roles and responsibilities. In general, the Ministry of Climate is responsible for legislative development, the Environmental Board is responsible for environmental permits and supervision of companies, and the Environmental Agency is responsible for the analysis of data submitted by companies. |
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| 11.2. Quality management - assessment | |||
See the description in point 11.1. |
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| 12.1. Relevance - User Needs | |||
free entree and no specific rules |
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| 12.2. Relevance - User Satisfaction | |||
not applicable |
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| 12.3. Completeness | |||
Packaging waste statistics cover all packaging. |
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| 13.1. Accuracy - overall | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Packaging waste report data depends on data quality from waste managers. Reusable packaging is not used in calculations. It is mandatory for companies to submit to the packaging register all the data necessary to fill in table 3, and we use this data when filling out table 3. |
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| 13.1.1. Statistical surveys used regarding packaging waste generation and treatment | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The information in this section is to provide an overarching understanding of the accuracy of any statistical surveys used relating to packaging waste. Some of the information may be available in previous questions.
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| 13.1.2. Statistical surveys used regarding reusable packaging | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
There are no statistical studies on reusable packaging. It is mandatory for companies to submit to the packaging register all the data necessary to fill in table 3. |
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| 13.2. Sampling error | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
not applicable |
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| 13.3. Non-sampling error | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Waste movements are automatically checked in WDMS reports from both the receiving and transferring companies, and any errors that occur are automatically highlighted. After entering the report, the Environmental Board conducts the initial review of the reports and approves the reports. |
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| 14.1. Timeliness | |||
Depends on the reports of submissions: deadline for waste reports is 31.01 (annually); packaging reports 31.03 (annually). |
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| 14.2. Punctuality | |||
State reportings are done on time, their are time lags from the enterprise side. Taking into the acount that reporting to the EU is based n-2 principle then it doen't effect national reporting. |
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| 15.1. Comparability - geographical | ||||||||||||||||||
Not applicable. |
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| 15.2. Comparability - over time | ||||||||||||||||||
No methodological changes were made. |
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| 15.3. Coherence - cross domain | ||||||||||||||||||
Not applicable |
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| 15.4. Coherence - internal | ||||||||||||||||||
Not applicable |
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| 15.4.1. Explanation for any component with a greater than 10 % variation | ||||||||||||||||||
Explanation detailing the causes of the tonnage difference (in relation to which waste streams, sectors or estimates have caused the difference, and what the underlying cause is) for any component of packaging waste generated and recycled which shows greater than a 10 % variation from the data submitted for the previous data year.
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Not applicable. |
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| 17.1. Data revision - policy | |||
Enterprise is responsible for its data and data quality. |
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| 17.2. Data revision - practice | |||
No revisions foreseen |
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| 18.1. Source data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Electronical system (KOTKAS-The aim of the Environmental decision information system is to maintain records on the waste generated and handled in Estonia, but also on imported and exported waste), surveys and estimates of waste managers. The aim of the sorting studies are to analyse the composition of mixed municipal waste, mixed packaging waste, separately collected waste paper and packaging waste generated in different regions of Estonia. See: A study of the composition and quantities of mixed household waste, separately collected paper and packaging waste, waste electrical and electronic equipment (Final report: Mixed household waste, separately collected paper and packaging waste, and waste electrical and electronic equipment. A study of the composition and quantities. file only available in Estonian), Envir download. |
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| 18.1.1. Waste samples from waste analysis | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The waste samples for waste analysis are taken from:
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| 18.1.2. Source of waste flow data for estimation | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.2. Frequency of data collection | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Through the electronic system (KOTKAS), we collect data every year. Once every four years, we conduct a survey of the composition of mixed municipal waste, separately collected waste paper and packaging waste and WEEE. |
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| 18.3. Data collection | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
See responses in following points. |
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| 18.3.1. Description of the methodology and verification of data on packaging waste generated in case waste analysis is used | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The generated packaging waste consists of separately collected packaging waste, mixed packaging waste, packaging contained in separately collected wastepaper and cardboard, and packaging waste contained in mixed municipal waste. The data from larger handlers of packaging waste and the data from KOTKAS have been used for the division of packaging waste containing hazardous substances by material. Waste coded 20 01 01 (separately collected paper and cardboard in municipal waste) and 20 03 01 (mixed municipal waste) have been taken into account; the results of the 2020 study on the composition of mixed municipal waste, separately collected waste paper and packaging waste and WEEE by SEI have been used to calculate the quantities of packaging waste. The results of the study are also used to divide mixed packaging waste by material. Study affect the generation of packaging. |
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| 18.3.2. Description of the methodology to report on composite packaging | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
For composite packaging we use the results of the surveys. Composite packaging is reported per material contained in the packaging. |
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| 18.3.3. Description of methods for determining packaging waste treatment | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Additional information about the methodology, including the combination of methods used: The data from KOTKAS have been used for the calculations of recycling. Export must be added to the packaging obtained on the basis of KOTKAS in order to obtain recycling, since it has not been automatically added to recovery. In addition, the packaging imported to Estonia must be deducted, since it has already been taken into account as recovered in the country of dispatch; thus, duplication of recovery is avoided within the European Union. Metal packaging from the mixed municipal waste reaches to the bottom ash during the energy production. According to the 2020 packaging study by SEI, the percentage of metal packaging in the share of metal in mixed municipal waste is 78%. Due to that the proportion of metal packaging in 19 01 02 are added to the recycling. Metal packaging are already taken into account in the packaging waste generation. The share of import of 20 03 01 is deducted from the result. Amount of landfilling is used as a one input while calculating the energy use of packaging waste. The quantity of packaging waste contained in mixed municipal waste incinerated in the power plant, the quantity of separately collected and incinerated waste and the quantities of landfilling are used to calculate the energy recovery of packaging waste (except metal and glass packaging). Moisture contents obtained as a result of measurements performed by SEI Tallinn in the course of the mixed municipal waste composition study are deducted from all quantities. The amount of total recycling, the amount of energy recovery and the amount of packaging waste deposited in the landfills need to be deducted from the generation of waste to get the amount of 19 12 10 and 19 12 12. Bottom ash from the incineration of mixed municipal waste also contains glass packaging waste. As it goes to cover the landfill, then the glass contained in the bottom ash is taken into account as other recovery. Only the quantity from the incineration of mixed municipal waste generated in Estonia has been taken into account and the ash that remained in the warehouse has not been taken into account. |
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| 18.3.4. Explanation of the scope and validity of surveys to collect data on the generation and treatment of packaging waste | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The aim of the sorting studies are to analyse the composition of mixed municipal waste, mixed packaging waste, separately collected waste paper and packaging waste generated in different regions of Estonia. See: A study of the composition and quantities of mixed household waste, separately collected paper and packaging waste, and electronic waste (Final report: Mixed household waste, separately collected paper and packaging waste, and waste electrical and electronic equipment. A study of the composition and quantities.File only available in Estonian), Envir download. |
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| 18.3.5. Explanation of the scope and validity of surveys to collect data on reusable packaging | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Estonia does not use surveys. |
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| 18.3.6. Detailed description of the method to collect data in order to calculate the amount of metals separated from incineration bottom ash | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Calculation of recycling of metals from incinerator bottom ash : Detailed description of the method to collect data in order to calculate the amount of metals separated from incineration bottom ash in accordance with the Commission Implementing Act adopted in accordance with Article 37(7) of Directive 2008/98/EC.
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| 18.4. Data validation | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
See responses in following points. |
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| 18.4.1. Detailed description of the system for quality control and traceability for packaging waste pursuant to Article 6a(3) and (8) of Directive 94/62/EC | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
We have a register where information about waste management is gathered. Waste reporting system (KOTKAS) consists ‘balance method’ - fixinging and comparing the "income" (waste generation + received from others, including imports) and "outgoing" (’finally’ handled + transferred to others, including exports) of waste quantities by type. The type of waste received at the waste management facility shall be entered in the register with the accuracy of the waste code and the quantity received shall be indicated also. When the waste is sorted then this information shall be entered to the register and the type of waste generated as a result of sorting shall be entered as a secondary generation. If the waste is recycled or recovered then waste managers enetering it to the system accoring to lists of waste recovery and disposal operations (R-codes). Register also contains information about imported and exported waste (waste type, quantity, country and R-codes). Waste movements are automatically checked in WDMS reports from both the receiving and transferring companies, and any errors that occur are automatically highlighted. After entering the report, the Environmental Board conducts the initial review of the reports and approves the reports. |
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| 18.4.2. Traceability of waste treated outside the member State and ensuring its treatment in conditions broadly equivalent to the requirements of EU environmental law | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.4.3. Description of measures to ensure broadly equivalent waste treatment | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
When inspecting waste operators, the Environmental Inspectorate checks that a contract has been concluded between the exporter and the importer and that where and how the waste is handled is described. Also that what is described in the contract corresponds to the accompanying documents. However, there is no definitive certainty asi t would require separaate control procedures in the country of destination. The European Commission is currently reviewing the requirements of the Regulation 1013/2006 and this is also one of the important topic how to make this more efficient in the future. |
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| 18.4.4. Verification of data on packaging waste generated | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The columns in the table relate to information on verification procedures used within the national statistical reporting system to validate the accuracy of the data.
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| 18.4.5. Verification of data on packaging waste recycling | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The columns in the table relate to information on verification procedures used within the national statistical reporting system to validate the accuracy of the data.
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| 18.5. Data compilation | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
See responses in following points. |
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| 18.5.1. Methods for determining packaging waste generation | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.5.1.1. Approach 1 - Put on the Market (POM) based on EPR | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Primary sources and their shares in the total.
(*) Necessity of a certain minimum amount of waste, turnover etc. to be registered |
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| 18.5.1.2. Approach 2 - Put on the market (POM) calculated from production and reign trade statistics and using coefficients of packaging for the sold goods in question | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Primary sources and their shares in the total.
(*) Necessity of a certain minimum amount of waste, turnover etc. to be registered |
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| 18.5.1.3. Approach 3 - Waste analysis | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Packaging waste generated estimated by waste analysis
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| 18.5.2. Information on estimates for packaging placed on the market | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Waste statistics cover all packaging placed on the market. |
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| 18.5.3. Presence and calculation of estimates and indication of added volume in % of the total | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.5.4. Measurement points for recycling applied | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.5.4.1. Detailed description of the methodology to calculate the amount of non-target materials removed between the measurement and the calculation points, where applicable | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Sorting is made before calculation points. The calculation point is the same as the measurement point. If there is anything else in the recyclable material that is not packaging or has excess moisture, then the waste handler must remove these other quantities with R12s operation or as another output and we will consider the clean secondary material for which the recycling operation is shown to us. |
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| 18.5.4.2. Detailed description of how compostable packaging recovered at biowaste treatment plants has been identified and recorded in the data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
If compostable packaging is recovered (recycled) at biowaste treatment plant then waste operator measures and indicates which type and how much packaging waste is going into the process. In an annual waste report waste operator shows the amount of wastes which has recycled in a year and has become a product – compost. Compost made from waste has to meet different quality requirements. Only data from waste operators which waste composte system has certified and licenced is allowed to use for annual report for packaging and use for the targets. |
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| 18.5.5. Methodology to determine recycled amounts from composite packaging or packaging composed of multiple materials | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
For composite packaging we use the results of the surveys. Composite packaging is reported per material contained in the packaging. |
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| 18.5.6. Use of Average Loss rates (ALRS) | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Description of the sorted packaging waste to which ALRs are applied, types of sorting plants to which different ALRs apply, the methodological approach to calculating ALRs at such point(s), including the statistical accuracy of any surveys used, or the nature of any technical specifications.
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| 18.6. Adjustment | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
See responses in following points. |
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| 18.6.1. Adjustment for impurities and humidity | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.6.2. Attribution of waste to packaging and non-packaging types and correction for humidity | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Description, where applicable, of the methodology to exclude non-packaging waste from the reported amount of recycled packaging waste and of the methodology to correct the amount of packaging waste at the measurement point in order to reflect the natural humidity rate of packaging (including by using relevant European standards). Aggregated data across facilities of a similar type is acceptable.
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| 18.6.3. Attribution of waste | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Description of the methodology to exclude waste originating from other countries, where applicable. Aggregated data across facilities of a similar type is acceptable.
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