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Plastics in municipal waste


Material description and quantity estimations

Plastic waste produced in end consumption mainly consists of various packages and utility articles. Plastic packages fall under the so-called producer responsibility, i.e., the producers of plastic packages, or the producer associations formed by them, must organise the related waste management to the extent stipulated by law.

Plastics are oil-based materials and they are divided into seven types: polyethylene terephthalate (PET), high-density polyethylene (PE-HD), vinyl, i.e., PVC, low-density polyethylene (PE-LD), polypropene (PP), polystyrene (PS), and other plastics (Suomen Uusiomuovi ry). The importance of the post-use treatment of plastics is emphasised, on the one hand, by the long lifecycle of the material that may last up to hundreds of years, and, on the other hand, by the short lifecycle of the products manufactured from plastic; approximately 50% of produced plastic is utilised in the manufacture of disposable products (Hopewell ym., 2009).

Plastic waste can be recycled as a material and utilised as energy (Muoviteollisuus ry). For material efficiency, the most desirable option is the primary reuse of plastic, i.e., the converting of recycled plastic into a product with the same properties as the original one. Particularly the recycling of municipal plastic is hindered by the heterogenous consistency of plastic packages; in addition to several polymers, plastic packages also often contain other materials, such as metal, paper, additives, fillers, colourants, and food residue (Eskelinen ym., 2016; Hopewell ym., 2009).

One form of plastic recycling is the primary recycling, during which plastic is recycled as such or as a material for its original intended purpose without the loss of value. Secondary recycling refers to mechanical recycling, during which the properties of recycled plastic deteriorate slightly. (Eskelinen ym., 2016). The chemical recycling of plastic is dissolving plastic back into monomers or into some intermediate, such as wax. Chemical recycling of plastic requires large quantities of recycled plastic, and it is an expensive method. In Finland, plastic is not recycled chemically at the moment (Suomen Uusiomuovi ry 2017a)

In 2015, approximately 2,700,000 tonnes of municipal waste was produced in Finland (Tilastokeskus 2017). Of that amount, approximately 13%, i.e., 350,000 tonnes, was plastic (Salmenperä ym., 2015). The amount is predicted to increase further in the future (Salmenperä ym., 2015). These plastics will end up in either PET plastic recycling in the form of plastic bottles, the collection of mixed plastic packages, or mixed waste.

From the collection of mixed plastic packages, the plastics will end up at Fortum’s plastic refinery. At the moment, the majority (approx. two thirds) of the plastics is directed to recycling, i.e., to be used as a raw material in the production of plastic bags, wood-plastic composite, or plastic objects (such as flower pots and plastic pipes). (Saarimaa 2017.) The annual treatment capacity and, consequently, the target level of the plastic refinery is 20,000 tonnes  (Anderson 2017).

According to Fortum, 140,000 tonnes of plastic ends up in mixed waste in Finland every year (Fortum 2017a). In Finland, mixed waste is mainly utilised as energy at the waste-to-energy plants. In Fortum’s Circular Economy Village in Riihimäki, there is also a plant with a 100,000-tonne capacity where different waste types can be mechanically separated from mixed waste (Fortum 2017). In 2016, LATE sorting plant was commissioned at the Kujala Waste Centre in Lahti, Finland. The plant complements the sorting at the place of origin with an annual capacity of approximately 65,000 tonnes (PHJ 2017). In addition, a mechanical-biological treatment plant is also being planned for the Oulu region (Ympäristöministeriö 2017).

In the capital region, approximately 30,000 tonnes of plastic ends up in energy recovery along with mixed waste (HSY 2017). Respectively, approximately 14,000 tonnes of plastic ends up in combustible waste in the Turku region (JLY 2017; LSJH 2017), 21,000 tonnes in the Tampere region (JLY 2017; Pirkanmaan jätehuolto 2017), and 5,000 tonnes in the Oulu region (Kauppila 2016).


Innovation needs

There are still many innovation needs related to the recycling of plastics, as there is currently still room for improvement in the quality of plastic waste. Furthermore, the yield needs to be increased in order to achieve the recycling rate objectives.

  • Development of the collaboration in the value chain related to the lifecycle of plastic packages and the avoidance of component optimisation. Comprehensive solutions are required. For instance, package designers must interact with the recycling entities while keeping in mind the original purpose of the package, i.e., protection of the product
  • Collaboration also between different responsible bodies; how to enable the recycling of plastics other than packaging plastics?
  • Further development of sorting technologies and new recycling solutions


Business-related challenges and opportunities 

Business is already being conducted on the recycling of clean and homogenous industrial plastic, whereas in the case of heterogenous municipal plastic, this is more challenging. The tightening of legislation and the efforts to implement circular economy require the rationalisation of plastics recycling. In order for the economic appeal of the rationalisation to be improved, the demand for recycled products would have to increase significantly. This could be achieved, e.g., with the aid of public procurements. (Eskelinen ym., 2016.) Significant economic profits could be gained with the new material recovery innovations related to plastic packages (World Economic Forum 2016), but developing business operations on the basis of plastic waste material flows also has its challenges. Perhaps the most significant element of uncertainty is the aim of disconnecting plastics from fossil raw materials by increasing the production of plastic from renewable and biodegradable raw materials (Moliis ym., 2009; VTT 2012; World Economic Forum 2016), which significantly affects the properties and recycling possibilities of plastic.

The mechanical properties of recycled plastics are , however, usually inferior to the properties of virginal materials (Eskelinen ym., 2016). Thus, in practice, the recovery of plastic is secondary material recovery, in which plastic is converted into a product that is, in terms of properties, inferior to the original product (World Economic Forum 2016).  The use of recycled plastic has been restricted for the part of some sensitive applications, such as food packages and products used in the health care sector. Otherwise, there are practically no other restrictions for plastic as long as it is clean, carefully manufactured, and appropriate documents exist for it. (Suomen Uusiomuovi 2017 b). According to Lassila&Tikanoja (2016), recycled plastic is one third less expensive than virginal material, which, for its part, supports the use of recycled plastic instead of virginal material.

At the moment, recycled plastic is primarily used in plastic packages (PET bottles, straps, films, bags, and cores), agricultural and earth construction products (films, culvert pipes, etc.), other plastic products used in construction and industry (profiles, injection moulding products, etc.), as well as in individual products, such as buckets, tubs, hangers, composters, and sheets. (Kärhä 2015). Recycled plastic can also be utilised in a variety of composite products (Singh et al., 2017).  Fortum, for instance, manufactures Circo recycled plastic profile from recycled plastic (Fortum 2017c). In the future, recycled plastic could be utilised, for example, in various geosynthetics and as support structures for filters used in wastewater treatment (Eskelinen ym., 2016).

The critical phase in the recycling of plastic waste is the sorting and separation of plastic waste. The development of optical methods, such as infrared spectroscopy, enables the separation of different types of plastic from mixed waste. The careful cleaning of plastics is also a prerequisite for the production of high-quality recycled plastic (Eskelinen ym., 2016).

In the future, the plastic industry and other industries using plastic in their products should pay attention to the recyclability of the products after they are no longer used. The number of plastic types contained by a product should be reduced and products that contain only one type of plastic, or compatible types of plastic, should be favoured. The use of additives should also be considered on the same basis. (Eskelinen ym. 2016).



References (mainly in Finnish)

Anderson, R. 7.12.2017. Project Manager, Fortum Waste Solutions Oy. Henkilökohtainen tiedonanto.

Eskelinen, H., T. Haavisto, H. Salmenperä ja H. Dahlbo. 2016. Muovien kierrätyksen tilanne ja haasteet. CLIC Innovation Raportti nro D4 1-3

Fortum 2017. Kiertotalouskylä.

Fortum 2017a. Kiertotalouskylä.

Fortum 2017c, CIRCO®-kierrätysmuoviprofiilit [Luettu 14.8.2017]

Hopewell, J., R. Dvorak ja E. Kosior. 2009. Plastic recycling: challenges and opportunities. Philosophical transactions of the royal society B, 364: (1524)

HS 2018. Törkyiset kierrätys­astiat tursuavat kaduille ja pusikoihin Helsingin ympäristössä – muovin kierrätyksestä tuli sekasotku 23.1.2018.

HSY 2017. Pääkaupunkiseudun jätevirrat -palvelu

JLY 2017.

Kauppila J.,2016. Oulun Jätehuollon toimialueen polttokelpoisen jätteen koostumustutkimus.

Kärhä, V. 2015. Muoviteollisuus ry. Henkilökohtainen tiedonanto sähköpostilla 22.4.2015

Lassila&Tikanoja 2016, Muovi murskautuu uudeksi raaka-aineeksi [Luettu 14.8.2017]

LSJH 2017. Henkilökohtainen tiedonanto Alijoki Tuomas. 30.11.2017

Moliis, K., N. Teerioja ja M. Ollikainen. 2009. Ennuste yhdyskuntajätteen kehityksestä vuoteen 2030. SUSWASTE-hankkeen esiselvitys. Helsingin yliopisto, Taloustieteen laitos. Helsinki. 54 s. (Discussion Papers n:o 41)

Muoviteollisuus Ry; Muovien kierrätys. Luettu 5.7.2017

Pirkanmaan jätehuolto 2017. Tilastoja 2013-2016.

PHJ, Päijät-Hämeen Jätehuolto Oy. 2017. LATE-lajittelulaitos. Kiertotalouden kärjessä- jätteestä raaka-ainetta jalostavan teollisuuden käyttöön. Luettu 29.11.2017.

Saarimaa, K. 2017. Kiertotalousliiketoiminnan johtaja. Fortum Waste Solutions Oy. Esitys Suomen kiertovoimapäivillä 30.11.2017.

Salmenperä, H., K. Moliis ja S-M. Nevala. 2015. Jätemäärien ennakointi vuoteen 2030 –painopisteenä yhdyskuntajätteet ja kierrätystavoitteiden saavuttaminen. Ympäristöministeriön raportteja 17/2015.

Suomen Uusiomuovi Oy; Materiaalimerkit. Luettu 5.7.2017

Singh N., Hui D., Singh R., Ahuja P.S., Feo L. & Fraternali F. 2017: Recycling of plastic solid waste: A state of art review and future applications. Composites Part B: Engineering: Volume 115, Pages 409-422

Suomen Uusiomuovi Oy 2017b Kysy muovista. [Luettu 14.8.2017]

Tilastokeskus 2017.

VTT. 2012. Muovipakkausten valmistuksessa käytettävä öljy mahdollista korvata kokonaan uusiutuvilla raaka-aineilla. Luettu 5.7.2017

World Economic Forum, Ellen MacArthur Foundation ja McKinsey & Company. 2016. The New Plastics Economy — Rethinking the future of plastics. 

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