Key Data Set Information | |
Location | GLO |
Reference year | 2020 |
Name |
Base name
; Treatment, standards, routes
; Mix and location types
; Quantitative product or process properties
polyester, petrochemical based; fossil-based PET is turned into fibres; production mix, at plant; petrochemical based PET fibres
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Use advice for data set | Notice: this data set supersedes the EF3.0-compliant version (see link under "preceding data set version" below calculated with the EF3.0). The life cycle inventory is not changed from the original EF3.0 data set. The LCIA results are calculated based on the EF3.1 methods which provide updated characterisation factors in the following impact categories: Climate Change, Ecotoxicity freshwater, Photochemical Ozone Formation, Acidification, Human Toxicity non-cancer, and Human Toxicity cancer. The review report and the data quality ratings refer to the original results. The data set has been updated by the European Commission on the basis of the original EF3.0 data set delivered by the data provider. |
Classification |
Class name
:
Hierarchy level
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General comment on data set | The dataset models the production of 1kg polyester, petrochemical. The type of polyester used is polyethylene terephthalate (PET) fibre. PET fibre is chosen for two reasons. Firstly, because the dataset focuses on the production of polyester used for synthetic turf application, that is needed in fibre form. Secondly, when PET is used as a fibre, it is typically called polyester. This type of fibre has good elasticity, wrinkle resistance, shape retention, excellent wash-and-wear performance and durability. Other applications of PET fibres include all kinds of fabrics and apparel, home furnishings, filtration, automobile interiors, geotextiles, and material for the sewing trade. References: AstroTurf, 2018. Synthetic Turf Glossary of Terms, AstroTurf Available at: https://www.astroturf.com/synthetic-turf-glossary-of-terms/ Package All, 2021. Why is PET sometimes called polyester?, Package All Corp. Available at: https://www.packageall.com/support/why-is-pet-sometimes-called-polyester PETRA, 2021. DI YOU KNOW? Little-Known Facts about PET plastic, PET Resin Association Available at: http://www.petresin.org/pdf/DidYouKnow.pdf Textile School, 2021. Polyester Fiber and its uses, Textile School Available at: https://www.textileschool.com/234/polyester-fiber-and-its-uses/ |
Copyright | Yes |
Owner of data set | |
Quantitative reference | |
Reference flow(s) |
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Biogenic carbon content |
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Time representativeness | |
Data set valid until | 2024 |
Technological representativeness | |
Technology description including background system | Petrochemical polyester is produced from polyethylene terephthalate (PET). First, the raw inputs of PET are polymerized to produce the needed polymer in chips. The chips are converted to dope by heat. Dope fluid is extruded through a spinneret and then converted to viscoelastic filament. The viscoelastic filament is solidified into solid filament fibre (usually called filament), which may be formed by extending the viscoelastic filament. Finally, when the viscoelastic filament is solidified into solid filament fibre, it is extended by the drawing process. The drawing process decreases the diameter, and the orientation of solid filament fibre could increase, while it improves the degree of crystallinity. References: Deopura, B.L., Alagirusamy, R., Joshi, M. and Gupta, B. eds., 2008. Polyesters and polyamides. Elsevier. |
Flow diagram(s) or picture(s) |
LCI method and allocation | |||||||||||||||||||||||||||||||||
Type of data set | LCI result | ||||||||||||||||||||||||||||||||
LCI Method Principle | Attributional | ||||||||||||||||||||||||||||||||
Deviation from LCI method principle / explanations | Background data: - the \xe2\x80\x9cRecycled content cut-off\xe2\x80\x9d approach to allocate end-of-life by-products and secondary materials. This allocation is explained in the description of the recycled content system model (http://www.ecoinvent.org/database/system-models-in-ecoinvent-3/cut-off-system-model/allocation-cut-off-by-classification.html). The ecoinvent database mostly relies on “Allocation – market values” apart for few exceptions particularly in the energy sector. ecoinvent energy data is replaced with EF3.0 core data as per the EF guidelines version 2.0. OR - EF compliant data | ||||||||||||||||||||||||||||||||
LCI method approaches |
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Deviations from LCI method approaches / explanations | Background data: - the \xe2\x80\x9cRecycled content cut-off\xe2\x80\x9d approach to allocate end-of-life by-products and secondary materials. This allocation is explained in the description of the recycled content system model (http://www.ecoinvent.org/database/system-models-in-ecoinvent-3/cut-off-system-model/allocation-cut-off-by-classification.html). The ecoinvent database mostly relies on “Allocation – market values” apart for few exceptions particularly in the energy sector. ecoinvent energy data is replaced with EF3.0 core data as per the EF guidelines version 2.0. OR - EF compliant data | ||||||||||||||||||||||||||||||||
Modelling constants | All modelling constants follow the requirements listed in the Tender Specifications 070201/2020/SER/ENV.B1. Completeness: There are no intentional cut-offs in the inventory no matter how small their contribution to all the EF impact categories is. Eventual cut-offs are in compliance with the Guide for EF compliant data sets (JRC 2020), i.e. only if below the 3% cut-off rule. Water use: water use is modelled at country level using separate flows for water withdrawal, water release and water evaporation. Handling multi-functional processes: the following PEF multi- functionality decision hierarchy is applied for resolving all multi- functionality problems: (1) subdivision or system expansion; (2) allocation based on a relevant underlying physical relationship (substitution may apply here); (3) allocation based on some other relationship. Direct land use change: GHG emissions from direct LUC allocated to good/service for 20 years after the LUC occurs, with IPCC default values. Carbon storage and delayed emissions: credits associated with temporary (carbon) storage or delayed emissions up to 300 years are not be considered. Emissions off-setting: are not included. Capital goods (including infrastructures) and their End of life: they are included. System boundaries: system boundaries include all processes linked to the product supply chain (e.g. maintenance). Time period: emissions and removals are modelled as if released or removed at the beginning of the assessment method. Fossil and biogenic carbon emissions and removals: removals and emissions are modelled as follows: All GHG emissions from fossil fuels (including peat and limestone) are modelled consistently with the most updated ILCD list of elementary flows. The non-fossil (biogenic) carbon flows are modelled consistently with the most updated ILCD list of elementary flows. | ||||||||||||||||||||||||||||||||
Deviation from modelling constants / explanations | None | ||||||||||||||||||||||||||||||||
Data sources, treatment and representativeness | |||||||||||||||||||||||||||||||||
Data cut-off and completeness principles | There are no intentional cut-offs in the inventory no matter how small their contribution to all the EF impact categories is. Eventual cut-offs are in compliance with the Guide for EF compliant data sets (JRC 2020), i.e. only if below the 3% cut-off rule. The dataset dry mass and water balance has been checked to ensure the inventory is complete. Capital goods (e.g. infrastructure) and their end-of-life are included. | ||||||||||||||||||||||||||||||||
Deviation from data cut-off and completeness principles / explanations | None | ||||||||||||||||||||||||||||||||
Data selection and combination principles | These datasets include, in both their foreground and background data, links to EF3.0 compliant data. The relevant background data on energy, transport, and End of Life are from the LCDN data node (http://lcdn.thinkstep.com/Node/). All other background data in the supply of this product for which no EF3.0 process was available are from ecoinvent v3.7 database (www.ecoinvent.org) or other data sources. | ||||||||||||||||||||||||||||||||
Deviation from data selection and combination principles / explanations | None | ||||||||||||||||||||||||||||||||
Data treatment and extrapolations principles | Several data sources have been used to model the inventory. | ||||||||||||||||||||||||||||||||
Deviation from data treatment and extrapolations principles / explanations | None | ||||||||||||||||||||||||||||||||
Data source(s) used for this data set | |||||||||||||||||||||||||||||||||
Uncertainty adjustments | None | ||||||||||||||||||||||||||||||||
Completeness | |||||||||||||||||||||||||||||||||
Completeness of product model | All relevant flows quantified | ||||||||||||||||||||||||||||||||
Supported impact assessment methods |
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Completeness elementary flows, per topic |
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Compliance Declarations |
Compliance |
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Approval of overall compliance
Fully compliant |
Nomenclature compliance
Fully compliant |
Methodological compliance
Fully compliant |
Review compliance
Fully compliant |
Documentation compliance
Fully compliant |
Quality compliance
Not defined |
Compliance |
Compliance system name
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Approval of overall compliance
Fully compliant |
Nomenclature compliance
Fully compliant |
Methodological compliance
Fully compliant |
Review compliance
Fully compliant |
Documentation compliance
Fully compliant |
Quality compliance
Fully compliant |
Compliance |
Compliance system name
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Approval of overall compliance
Fully compliant |
Nomenclature compliance
Not defined |
Methodological compliance
Fully compliant |
Review compliance
Fully compliant |
Documentation compliance
Not defined |
Quality compliance
Not defined |
Compliance |
Compliance system name
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Approval of overall compliance
Fully compliant |
Nomenclature compliance
Not defined |
Methodological compliance
Fully compliant |
Review compliance
Not defined |
Documentation compliance
Fully compliant |
Quality compliance
Not defined |
Compliance |
Compliance system name
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Approval of overall compliance
Not defined |
Nomenclature compliance
Fully compliant |
Methodological compliance
Not defined |
Review compliance
Not defined |
Documentation compliance
Not defined |
Quality compliance
Not defined |
Commissioner and goal | |
Commissioner of data set | |
Project | Provision of process-based 3.0 Environmental Footprint-compliant life cycle inventory datasets - Plastics - contract number 070201/2020/839443/SER/ENV.B.1 |
Intended applications | Implementation of regular Product Environmental Footprint (PEF) studies and Organisation Environmental Footprint (OEF) studies exclusively under the specified Product groups and sectors as defined in the Product Environmental Footprint Category Rules (PEFCR) and Organisation Environmental Footprint Sectorial Rules (OEFSR) listed in http://ec.europa.eu/environment/eussd/smgp/PEFCR_OEFSR.htm |
Data generator | |
Data set generator / modeller | |
Data entry by | |
Time stamp (last saved) | 2022-12-01T22:27:36.169+01:00 |
Data set format(s) | |
Data entry by | |
Publication and ownership | |
UUID | 3c9e2d5e-28f9-5a73-806b-dafb535a147a |
Date of last revision | 2020-09-02T14:36:46.214668+02:00 |
Data set version | 01.01.000 |
Preceding Data set version | |
Workflow and publication status | Data set finalised; entirely published |
Owner of data set | |
Copyright | Yes |
Reference to entities with exclusive access | |
License type | Free of charge for some user types or use types |
Access and use restrictions | Free of charge for all final users implementing a regular Product Environmental Footprint (PEF) studies and Organisation Environmental Footprint (OEF) studies exclusively under the specified Product groups and sectors as defined in the Product Environmental Footprint Category Rules (PEFCR) and Organisation Environmental Footprint Sectorial Rules (OEFSR) listed in http://ec.europa.eu/environment/eussd/smgp/PEFCR_OEFSR.htm and in accordance with the terms and conditions of the EULA (available at https://ecoinvent.lca-data.com/) exclusively until 31st December 2024. Any use of this dataset or any derivative data not within the specific context of one of the PEF/OEF projects or after the end of 2024 is not permitted. |