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| For any question on data and metadata, please contact: Eurostat user support |
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| 1.1. Contact organisation | Interregional Packaging Commission / Interregionale Verpakkingscommissie / Commission interrégionale de l'Emballage |
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| 1.2. Contact organisation unit | general direction |
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| 1.5. Contact mail address | Gaucheretstraat 92-94, 1030 Schaarbeek Rue Gaucheret 92-94, 1030 Schaerbeek |
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| 2.1. Metadata last certified | 30 June 2025 |
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| 2.2. Metadata last posted | 30 June 2025 |
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| 2.3. Metadata last update | 30 June 2025 |
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| 3.1. Data description | ||||||||
Reporting for the reference year 2023 is done in accordance with the new calculation rules. As off 2020, Belgium no longer uses the old calculation method. The derogation to make use of the delegated act on average loss rates has not been applied. |
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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 | ||||||||
See 3.2.1. |
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| 3.2.1. Classification of treatment operations | ||||||||
The R and D-classificationcodes as described in the annex I (Disposal operations) and in the annex II (Recovery operations) of the Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives, is used. |
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| 3.3. Coverage - sector | ||||||||
Waste. |
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| 3.4. Statistical concepts and definitions | ||||||||
Recycling rate for wood = (recycling (184 198) + repair (33 943)) / (waste generated (281 071) + repair (33 943)) = 69.25%. Belgium wishes to take 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 | ||||||||
For household packaging it concerns mostly glass bottles with deposit. |
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| 3.4.2. Other recovery of waste | ||||||||
Incineration in cement kilns, blast furnaces, drying kilns, biomassinstallations. The IRPC confirms that the results in the column for "Recovery" are the sum of both and include as well "Energy recovery (R1)" as "Incineration at waste incinerators with energy recovery". |
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| 3.4.3. Information on temporary storage of packaging waste | ||||||||
This is not relevant. |
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| 3.5. Statistical unit | ||||||||
Eurostat. |
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| 3.6. Statistical population | ||||||||
Belgian companies. |
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| 3.7. Reference area | ||||||||
Belgium. |
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| 3.8. Coverage - Time | ||||||||
1 year. |
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| 3.9. Base period | ||||||||
Not applicable. 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 | |||
Accord de coopération du 4 November 2008 concernant la prévention et la gestion des déchets d'emballages. Samenwerkingsakkoord van 4 November 2008 betreffende de preventie en het beheer van verpakkingsafval. Directive 94/62/EC sets out the EU’s rules on managing packaging and packaging waste (Directive 94/62/EC on packaging and packaging waste). |
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| 6.2. Institutional Mandate - data sharing | |||
IVCIE collects the data from the producer responsibility organisations. |
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| 7.1. Confidentiality - policy | |||
European General Data Protection Regulation (GDPR). |
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| 7.2. Confidentiality - data treatment | |||
No confidential informaton in the questionnaire. |
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| 8.1. Release calendar | |||
Not applicable. |
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| 8.2. Release calendar access | |||
Not applicable. |
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| 8.3. Release policy - user access | |||
Not applicable. |
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Yearly. |
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| 10.1. Dissemination format - News release | |||
Annually. |
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| 10.2. Dissemination format - Publications | |||
| 10.3. Dissemination format - online database | |||
Not applicable - to be developed. |
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| 10.4. Dissemination format - microdata access | |||
Not applicable. |
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| 10.5. Dissemination format - other | |||
Annual report of the Interregional Packaging Commission. |
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| 10.6. Documentation on methodology | |||
| 10.7. Quality management - documentation | |||
National quality validation standards. For details see section 18. |
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| 11.1. Quality assurance | |||
Guidelines in regional legislation apply. |
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| 11.2. Quality management - assessment | |||
For details see section 18.4. |
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| 12.1. Relevance - User Needs | |||
Eurostat and other users. |
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| 12.2. Relevance - User Satisfaction | |||
Publications are available for users on IVCIE website. |
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| 12.3. Completeness | |||
EPR scheme data controlled by Fost Plus and Valipac are additionally controlled by the Interregional Packaging Commission and are the main source of the Belgian statistics. For details see section 18. |
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| 13.1. Accuracy - overall | ||||||||||||||||||
For household one-way packaging, the recycling data are extremely complete, no extrapollation is needed. For reusable household packaging: data are statistically correct but less controls are performed on the data. For non household one-way packaging there are no issues concerning the accuracy of data. For reusable non household packaging: data are statistically correct but less controls are performed on the data. There are less reliable data on open loop reusable packaging put onto the market (for the first time). A detailed questionnaire sent by Valipac or the Belgian authorities to European multinational companies will have very limited effect. The pallet pool is an international pool and the pallets are not allocated to a specific country. The few companies replying will generally have difficulty estimating correctly a replacement rate specific for Belgium or will attribute the replacements exclusively to the country where they are based or to the country where the pallets are repaired. |
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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.
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 | ||||||||||||||||||
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 other concepts.
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 other concepts. |
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| 13.2. Sampling error | ||||||||||||||||||
No complete data as yet available. On the most important data sources, sampling errors are determined. |
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| 13.3. Non-sampling error | ||||||||||||||||||
There are few reliable data on open loop reusable packaging put onto the market (for the first time). A detailed questionnaire sent by Valipac or the Belgian authorities to European multinational companies will have very limited effect. The pallet pool is an international pool and the pallets are not allocated to a specific country. The few companies replying will generally have difficulty estimating correctly a replacement rate specific for Belgium or will attribute the replacements exclusively to the country where they are based or to the country where the pallets are repaired. |
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| 14.1. Timeliness | |||
For POM data, reporting for year N is done by members to Fost Plus and Valipac by March of year N+1. For recycling/recovery data, reporting by waste operators is done monthly or two-monthly. |
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| 14.2. Punctuality | |||
For the POM data, some members' declarations are late. Procedures are in place to remedy this, including penalties and termination of membership. There are no statistical data, but it is not considered a major problem. For recycling/recovery data punctuality is not a problem. |
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| 15.1. Comparability - geographical | ||||||||||||
Not applicable. |
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| 15.2. Comparability - over time | ||||||||||||
No differences. |
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| 15.3. Coherence - cross domain | ||||||||||||
Information not available. |
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| 15.4. Coherence - internal | ||||||||||||
Information not available. |
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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 | |||
Not applicable. |
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| 17.2. Data revision - practice | |||
No backwards corrections of data series. No revised data available on previous years. The new calculation method, applied from the referenceyear 2020 on, requires additional data, which are not available for previous years. There are no other changes to the methodology then the application of the new calculation method for the targets. |
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| 18.1. Source data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
EPR scheme data are the main source of the Belgian statistics; other sources give additional information and are used as a cross-check. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Data on selective waste flows collected for recycling are collected continuously by Fost Plus and Valipac (on a monthly or two-monthly basis). Statistical data on the presence of packaging in household and non-household residual waste are collected by the regions, normally every 5 years. |
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| 18.3. Data collection | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
See 18.1 and 18.2. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Only used as partial cross-check. |
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| 18.3.2. Description of the methodology to report on composite packaging | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The drink cartons are composite packaging, consisting of (in average) 75% cardboard fibres - which is recycled as paper and cardboard composite, and a fraction of 25% polyal. This fraction of polyal consists of plastic and less than 5% aluminum. For the reporting year 2023, a increased part of the polyal fraction was recycled (26.90%), whilst 56.15% was incinerated with energy recovery and 16,96% was landfilled. |
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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: |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Fost Plus:
Valipac: |
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| 18.3.5. Explanation of the scope and validity of surveys to collect data on reusable packaging | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Fost Plus: Members must also declare the reusable packaging in their declaration: the number of units placed on the market per retail packaging sheet or per average packaging sheet of a product family ('flat-rate' declaration). No extrapolations are applied; all members who put reusable packaging on the market must declare it.
Valipac: regularly a study is executed with regard to the newly placed on the market reusable industrial & commercial packaging waste in Belgium; this study is then updated annually. Since 2020, the IRPC has done annually a monitoring of the use of reusable packaging, analysing in detail the declarations by the companies that use the highest amonts of reusable packaging per type of product. |
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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 18.4.1-18.4.5. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Fost plus:
Valipac: |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
For household packaging waste: see above. For non-household packaging waste: see above; the described audit procedure includes the assessment of the broadly equivalent waste treatment. In the case of an infringement, an "orange or red flag"-procedure is activated, which, in most cases, obliges recyclers to remedy the problem in time for a follow-up audit. In a limited numer of cases (major infringements) a "final red flag" is given, which will end the export to that recycler. |
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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 below. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Data from Fost Plus and Valipac do not cover the total market; an extrapolation was made based on the estimate of the total market by the accredited compliance organisations Fost Plus and Valipac (based on internal studies). Over the past years, these estimates have been improved on the basis of additional analyses and internal research made by the accredited compliance organisations Fost Plus and Valipac, under the supervision of the IRPC. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Examples are included in the study ordered by the IRPC and executed by COMASE concerning "Analyse des chiffres sous-jacents servant au rapportage de la CIE sur les résultats en matière de recyclage et de valorisation des déchets d’emballages". This study can be made available. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
In 2023 there was 1409 tons of composted paper-cardboard going into anaerobic composting. |
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| 18.5.5. Methodology to determine recycled amounts from composite packaging or packaging composed of multiple materials | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Drink cartons consist for 75% of cardboard fibres that are recycled and for 25% of polyal. A part of the polyal fraction was recycled (26.90%) and another part was incinerated with energy recovery (56.15%); the remaining quantities (16.96%) were put into landfill. The average composition was determined on the basis of data received from packer/fillers and from producers of drink cartons. The cardboard fibres are recycled in paper mills. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
All data received from Fost Plus, Valipac and individual compliers have already been corrected to take into account impurities and humidity. This means that further adjustments are not necessary. More information under 18.6.2. |
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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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No further comment. |
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