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| For any question on data and metadata, please contact: Eurostat user support |
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| 1.1. Contact organisation | Agência Portuguesa do Ambiente (APA) |
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| 1.2. Contact organisation unit | Divisão de Fluxos Específicos e Mercado de Resíduos |
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| 1.5. Contact mail address | Rua da Murgueira, 9 - Zambujal - Alfragide | 2610-124 Amadora Portugal |
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| 2.1. Metadata last certified | 3 July 2025 |
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| 2.2. Metadata last posted | 3 July 2025 |
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| 2.3. Metadata last update | 3 July 2025 |
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| 3.1. Data description | ||||||||||||||||
The WFD allows, by way of derogation, that the weight of recycled waste may be measured at the output of any sorting operation. Portugal (PT) has applied the derrogation since PT has standard technical specifications for packaging that municipal sorting facilities must fulfill, so that the material is considered acceptable for recycling facilities. These specifications set quality standards for the material, including a maximum level of contaminants allowed. In the preparation of these specifications a number of stakeholders were involved including recyclers and contaminants were defined taking into account recycling processes of the different materials. It is just discounted on bales prepared by the SGRU - Sistemas de Gestão de Resíduos Urbanos (Municipal Waste Management Systems) that are mixed bales ( with packaging and non-packaging), for example paper/cardboard bales or plastic film bales, the amount of non-packaging. The information reported by the PROs to APA, within the scope of the annual reports, is already only referring to the amount of packaging, but we have information on the percentage of packaging and non-packaging in another type of report. We only count for recycling the amount of packaging. |
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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 | ||||||||||||||||
It is used the standard R codes in Annexes I and II of Directive 2008/98/CE: R1, R3, R4, R5 and R12. |
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| 3.2.1. Classification of treatment operations | ||||||||||||||||
The standard R codes defined in Annexes I and II of Directive 2008/98/CE (R1, R3, R4, R5 and R12) are used. |
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| 3.3. Coverage - sector | ||||||||||||||||
We have considered information related to municipal waste and non municipal waste. |
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| 3.4. Statistical concepts and definitions | ||||||||||||||||
We don't take into account the amount of wooden packaging that is repaired for reuse. We still don't have information about the amounts involved. We 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 | ||||||||||||||||
Reusable packaging are essentially:
Almost all reported systems are closed loop systems. |
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| 3.4.2. Other recovery of waste | ||||||||||||||||
We have not "other recovery". 100% for the 3 material reported (plastic packaging, paper packaging and wood packaging). |
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| 3.4.3. Information on temporary storage of packaging waste | ||||||||||||||||
The reports made from PROs (SPV, Novo Verde and Electrão) to APA concerning quantity of waste packaging recycled, doesn´t take into account the temporary storage (stocks) made in the waste treatment operators. |
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| 3.5. Statistical unit | ||||||||||||||||
Producer responsibility organisation (PRO). National legislation (Decree-law 152-D/2017) and each licence of each PRO defines the legal framework and the entire functioning of the system for the EPR for packaging. Based on the legal framework, and for the packaging waste stream, these entities are considered producers and have to assign with a PRO:
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| 3.6. Statistical population | ||||||||||||||||
All PROs. For Waste generation: We have used the placed on the market approach, the population is the universe for which we want to know packaging placed on the market. "Total packaged products placed on the national market for the first time by all economic operators" and service packaging placed on the national market (to be filled in PT)
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| 3.7. Reference area | ||||||||||||||||
Portugal. |
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| 3.8. Coverage - Time | ||||||||||||||||
2023 |
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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 Diretive 94/62/CE. Decree-law 152-D/2017 and PROs permits which establishes the obligation of producers/packers to report information on the quantity of packaging placed on the market on the APA electronic platform and the obligation of PRO to report information about quantities placed on market and quantities recycled. Decree-Law No. 102-D/2020 which establishes the obligation of waste producers to report on the APA electronic platform (MIRR and MTR) the waste produced, the obligation of waste management operators to report on the APA electronic platform (MIRR and MTR) the waste received and treated and the obligation of SGRU (Sitemas de Gestão de Resíduos Urbanos - municpal waste management systems) to report on the APA MRRU electronic platform information about municipal waste collected and treated (sorted, incinerated and placed in landfill) and forwarded for recycling. |
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| 6.2. Institutional Mandate - data sharing | |||
Institutional Mandate - data sharing : Statistics on packaging and packaging waste are in accordance with the Commission Decision 2005/270/EC. |
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| 7.1. Confidentiality - policy | |||
European General Data Protection Regulation (GDPR). |
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| 7.2. Confidentiality - data treatment | |||
All data are aggregated before being published. |
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| 8.1. Release calendar | |||
The reporting table of Packaging report is published on the APA website within 5 days after the data is validated (this is established in legislation decree-law 152-D/2017 -article 97ºA (5). However, it is usually published on the website immediately after submission to Eurostat, stating that the data is still being validated and that note is removed after the data has been validated by Eurostat. The PROs must send to the APA, to DGAE - Direção Geral das Atividades Económicas (General Directorate of Economic Activities) and to ERSAR - Entidade Reguladora dos Serviços de Águas e Resíduos (Water and Waste Regulatory Entity), by April 15th of the year immediately following the year to which they report, the annual activity report and must publish the respective summary on your website by that date.The summary report contains, namely, information on the quantities of packaging placed on the market and the quantities of packaging waste recycled and recovered. This deadline is also established in legislation (decree-law 152-D/2017 - article 12º (1 (j)) and in the PRO permit. Annexes: Reporting |
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| 8.2. Release calendar access | |||
Decree law 152-D/2017 establishes the deadlines referred to in question 8..1 regarding the disclosure of information. |
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| 8.3. Release policy - user access | |||
There is not a general data release policy of APA. However, for certain matters, such as the management of specific waste flows, the legislation provides for the disclosure of information on the APA website and on the PRO website |
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Anual. |
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| 10.1. Dissemination format - News release | |||
Not applicable. |
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| 10.2. Dissemination format - Publications | |||
| 10.3. Dissemination format - online database | |||
We don't have a online database. |
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| 10.4. Dissemination format - microdata access | |||
Not applicable. |
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| 10.5. Dissemination format - other | |||
The 2023 data of EPR schemes is published on the APA website in a space related to packaging. The data reported to COM/Eurostat is published also on the APA website: |
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| 10.6. Documentation on methodology | |||
Technical standars for waste packaging bales, methodology for quantifying slag and accounting for organically recovered packaging waste are also on the APA website: |
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| 10.7. Quality management - documentation | |||
Not available. |
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| 11.1. Quality assurance | |||
1.Cross-checks and Time-series checks are made to the data reported on APA's electronic platforms: MRRU Data:
The quantities reported in the MIRR by the waste treatment operators are in many cases already filled in automatically from the electronic waste tracking guides. The waste tracking guides became electronic since 2018, and communicate directly with MIRR. MIRR Data
MTR Data
2.Audits are also made:
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| 11.2. Quality management - assessment | |||
Not available. |
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| 12.1. Relevance - User Needs | |||
Academia, media, general public, NGOs, PROs, government. Information is sought for academic work, for the production of news by the media (especially in magazines with environmental content), for knowledge of information by NGOs. PROs also seek information to learn about other PROs, especially their competing PROs. |
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| 12.2. Relevance - User Satisfaction | |||
Not available. |
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| 12.3. Completeness | |||
Data are complete. |
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| 13.1. Accuracy - overall | ||||||||||||||||||
Waste generated - PoM methodology Since 2017 APA has implemented the National Electronic Register of Producers, for reporting of the packaging quantities placed on market (PoM), by packers and/or those responsible for placing packaged products on the national market and manufacturers and importers of service packaging. However, the data still presents some weaknesses. Although the collaboration between APA and INE- Instituto Nacional de Estatística (Statistics Portugal) regarding waste statistics has been going on for several years, the analysis and validation of these statements has not been carried out. Consequently, the estimate of waste generated has been made based on the data reported by the 3 PROs (SPV, Novo Verde and Elétron) and an extrapolation to the global scope. The PROs (SPV, Novo Verde and Electrão) scope is non-reusable primary, secondary and tertiary packaging (including items designed and intended to be filled at the point of sale), placed on the national market and respective packaging waste whose responsibility for management is attributed by law to SGRU – household waste and similar waste whose daily production per producer does not exceed 1100 litres. The first basis for calculating the ratio between the PROs universe and the total universe of packaging PoM comes from 2013. If the amount of packaging in the PRO universe increases every year (and this is what has been happening), the amount of packaging outside the PRO scope also increases, which may not be true. Within the scope of Own Resources, we are working with INE reviewing the methodology for quantifying the amount of plastic packaging waste generated by the 2 approaches : PoM and Waste Analysis. We are also working with the INE on a methodology for freeriding accounting. From next year's report (reference year 2024) we intend to replicate (with the necessary adaptations) the Waste Analysis methodology developed for plastic within the scope of Own Resources for the other materials and start reporting based on this methodology which we consider more robust.
Waste treatment Relating to waste treatment, PROs report to APA the quantity of packaging waste by LoW codes but also by material name (plastic, glass,...). The waste treatment operators and SGRU - Sistemas de Gestão de Resíduos Urbanos (Municipal Waste Management Systems) report to APA on electronic platforms (MRRU, MIRR and MTR) by LoW codes. In 15 01 05, 15 01 06 and 150110 waste codes we have packaging but we don't know of wich materials. Also, we believe that some metal packaging is being classified in waste scrap codes or in other codes that could contain metal, like, for example, the construction and demolition waste codes (LoW codes 17). We are losing some quantities of packaging in these LoW codes for the fulfillment of the targets by material.
Reusable packaging Some economic operators doesn't clearly distinguish between reusable and single-use packaging. But the information received from economic operators was analysed and only the information we consider that in fact refers to reusable packaging was reported in table 3 of the report excel file submited by EDAMIS (WASTE_PACKDAT_A_PT_2023_0000_V0001). |
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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 | ||||||||||||||||||
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 | ||||||||||||||||||
Not applicable. |
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| 13.3. Non-sampling error | ||||||||||||||||||
Not applicable. |
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| 14.1. Timeliness | |||
The different electronic platforms that APA has for reporting information must be completed according to the following schedule:
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| 14.2. Punctuality | |||
2023 data was sent to eurostat on 30 june 2025 |
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| 15.1. Comparability - geographical | ||||||
Not applicable. |
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| 15.2. Comparability - over time | ||||||
An important note for these year is thar we did't sum the quantities of reusable packaging PoM for the first time in 2023 to the quantity of non reusable packaging PoM in 2023. The submission of the form relating to reusable packaging (identical to the form present in the Reporting Guide) became madatory since 2024 (reference year 2023).In previous years it was not mandatory. There was a very significant increase in the number of forms submitted and consequently a very significant increase in the quantities declared. This fact made us rethink and conclude that we could not add to the quantity of non-reusable packaging placed on the market in 2023 the quantity of reusable packaging placed on the market for the first time in that year, since this quantity will not be available for recycling (unlike non-reusable packaging PoM that, by approximation, becomes waste in the same year). In the case of reusable packaging, we would have to add the quantity of reusable packaging that became waste in 2023 (waste generated). We do not have this information yet. we will change the form to request this information for the next report. Please note that the electronic platforms (MRRU, MIRR and MTR), as well as the information provided by the PROs, do not allow the distinction between reusable and non-reusable packaging when these are already waste. |
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| 15.3. Coherence - cross domain | ||||||
Not applicable. |
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| 15.4. Coherence - internal | ||||||
We have no information about "other materials" PoM (G17 cell of table 1 of WASTE_PACKDAT_A_PT_2023_0000_V0001) . However we have quantities of waste packaging recicled, classified with LoW codes 150105, 150106 and 150110 (W17 cell of table 1 of WASTE_PACKDAT_A_PT_2023_0000_V0001). There is a high probability that the quantity of these packaging (when PoM) have been considered in the cells G8, G9, G10, G11, G12, G15 and G16, since it is mandatory the report by material (even in composite packaging). So we have considered in cell G17 the value zero. That why for this line ("Other") the recycling quantity is higher than generation. We consider the quantity of cell W17 only for quantifying the overall quantity of recycled packaging waste and not the quantity per material. |
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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 available. We do not yet a planned policy for revising information. We intend however from next year's report (reference year 2024) to replicate (with the necessary adaptations) the waste analysis methodology developed for plastic within the scope of Own Resources for the other materials and start reporting based on this methodology. |
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| 17.2. Data revision - practice | |||
We did not change the reporting methodology. Within the scope of Own Resources, we are working with INE reviewing the methodology for quantifying the amount of plastic packaging waste generated by the 2 approaches : PoM and waste analysis. We are also working with the INE on a methodology for freeriding accounting. From next year's report (reference year 2024) we intend to replicate (with the necessary adaptations) the waste analysis methodology developed for plastic within the scope of Own Resources for the other materials and start reporting based on this methodology. |
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| 18.1. Source data | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| 18.1.1. Waste samples from waste analysis | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
PT didn´t use until now the metodology based on waste analysis. |
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| 18.1.2. Source of waste flow data for estimation | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
PT doesn´t use a metodology based on waste analysis. |
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| 18.2. Frequency of data collection | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Annual. (although there is information collected monthly (in MRRU platform), the annual information is what is important for this report) |
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| 18.3. Data collection | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
See details in sections below. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
No packaging waste analysis is used. |
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| 18.3.2. Description of the methodology to report on composite packaging | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
For composite packaging and other packaging made up of more than one material, the report from producers/packers to PRO and to APA platforms must be made for the different materials separately. As an example, differentiate the glass bottle, the paper label and the aluminum cap and report each quantity separately. |
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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: For municipal waste packaging we use the reports made from PRO (SPV, Novo Verde and Electrão) to APA concerning quantity of waste packaging recycled (the PRO pay to SGRU a monetary value for the quantity of packaging waste wich fullfill the technical standards/specifications for the quality requirements of sorted waste and goes to recycling and PRO sell packaging waste at auctions). |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Not applicable. |
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| 18.3.5. Explanation of the scope and validity of surveys to collect data on reusable packaging | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
From 2024 (reference year 2023) onwards, it became mandatory by law for those packers that use reusable packaging to fill in a form with data about reusable packaging ,for reference year n, by April 30 of year n+1. |
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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 the sections below. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The waste produced and treated in Portugal are accompanied by an electronic waste tracking guides (e-GAR). The waste tracking guides became electronic since 2018, and communicate directly with MIRR platform. PROs make audits to waste treatment operators to assess the quality and veracity of the information reported and compliance with technical specifications. PROs make audits to SGRU to assess the quality and veracity of the information reported and compliance with technical specifications.
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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 all the waste transboundary movements, Portugal has to comply with Regulation n.º 1013/2016, of the European Parliament and of the Council on shipment waste, and also the Decree Law 45/2008, 11th march, ensuring the implementation and compliance in the domestic law the obligations of Portugal in the Regulation. |
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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 by PROs.
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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 details in sections 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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Not applicable. |
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| 18.5.1.3. Approach 3 - Waste analysis | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Not applicable. |
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| 18.5.2. Information on estimates for packaging placed on the market | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
The quantity of packaging PoM in 2023 was calculated taking into account the declarations of the quantity of packaging PoM, by material, in 2023, made by the producers/packers to the 3 PRO (Sociedade Ponto Verde, Novo Verde and Electrão). Since PROs only covers sales (including service packaging), group and transport non reusable packaging that give rise to municipal waste from waste producers with a daily waste production under 1100 liters (waste packaging in the scope of SGRU), an estimate of the weight of this universe in relation to the total non reusable packaging PoM is used. We calculate that estimate of the weight/racio using the data from previous year (2022). With the declarations from the producers/packers (PRO universe) in 2023, we made an estimate for the total PoM in the same year, using the percentages found for the previous year (2022). Total PoM (n)= PRO PoM (n) x Total PoM (n-1) / PRO PoM (n-1). Racio of PRO universe in the total non reusable packaging PoM in 2022:
An important note for these year is thar we did't sum the quantities of reusable packaging PoM for the first time in 2023 to the quantity of non reusable packaging PoM in 2023. The submission of the form relating to reusable packaging (identical to the form present in the Reporting Guide) became madatory since 2024 (reference year 2023).In previous years it was not mandatory. There was a very significant increase in the number of forms submitted and consequently a very significant increase in the quantities declared. This fact made us rethink and conclude that we could not add to the quantity of non-reusable packaging placed on the market in 2023 the quantity of reusable packaging placed on the market for the first time in that year, since this quantity will not be available for recycling (unlike non-reusable packaging PoM that, by approximation, becomes waste in the same year). In the case of reusable packaging, we would have to add the quantity of reusable packaging that became waste in 2023 (waste generated). We do not have this information yet. we will change the form to request this information for the next report. Please note that the electronic platforms (MRRU, MIRR and MTR), as well as the information provided by the PROs, do not allow the distinction between reusable and non-reusable packaging when these are already waste. We don't have yet any estimation for freeriding, private shipments and on line sales. We have no theshold or exemptions from reporting of producers to PROs or to APA. |
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| 18.5.3. Presence and calculation of estimates and indication of added volume in % of the total | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
PT doesn't have a minimis and there are no exemptionts for reporting. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
SGRU for some material (for example paper, plastic films) make bales of packaging and non-packaging items together. Analyzes / samplings are made by SGRU to find out the packaging content (%) and only the quantity of packaging is counted and reported from PRO to APA in the scope of their anual report (but we have information on the percentage of packaging and non-packaging in another type of report). We only count for recycling the amount of packaging. PROs carry out SGRU audits and also carry out characterizations themselves. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
We have considered paper and wood packaging composting. It is considered that these paper/wood packaging are recycled if the compost where they are incorporated is used into agricultural, forestry and / or landscaped soils as an organic corrective, so that the moment of accounting for recycling these packaging residues is only carried out in the year the compost is sold to incorporation into soils. Quantities are validated by the 3 PROs (SPV, Novo Verde and Electrão).
The proportion of paper and wood packaging waste in mixed municipal waste ( entering mechanical and biological treatment, MBT, and in the rejected) are obtained through the characterization of these municipal waste flows in accordance with Ordinance No. 851/2009, of 7 August. SGRU are responsible for developing the campaigns to assess the physical composition of municipal waste, accordingly to the guidelines set out in the mentioned Order. The campaigns are carried out in two different periods of the year: for seasonality and climate conditions reasons, one campaign is carried out in the spring/summer season and a second one in the autumn/winter season. Atypical or exceptional periods, such as festive or holiday seasons, should be avoided which may interfere with the characteristics of the MW produced. Some SGRU have their own trained and dedicated human resources to supervise and carry out the composition characterization campaigns. Others, contract this task to auditing companies with recognized technical capacity to perform the analysis and produce reports accordingly. Taking into consideration the legislation and common practice, the majority of the SGRU perform, every year, a due assessment on waste composition analysis. SGRU may request to APA an exemption on doing assessment on an annual basis if there is evidence on stabilization of results and statistical evidence of no significant modifications on relevant parameters in previous years. Though, most of SGRU recognise the importance of doing such assessment every year as crucial to management decisions whether operational or investment programming. The categories and subcategories to be characterized are defined in the mentioned Order.
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| 18.5.5. Methodology to determine recycled amounts from composite packaging or packaging composed of multiple materials | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
In the specific case of ECAL (carton packaging to liquid food), like tetrapack, since reference year 2020 in order to comply with the 5% rule, we considered that these packages are made up of 75% paper, 20% plastic and 5% aluminum and we allocated the weight of the ECAL to these 3 materials, taking these percentages into account. |
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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 | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
PT does not yet have adjustments, namely for humidity, online commerce, free riding. |
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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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