Hopp til hovedinnholdet

Division of Environment and Natural Resources

DGRADE - Constraints to degradation of biodegradable plastics in terrestrial systems

Finished Last updated: 21.02.2024
End: sep 2023
Start: jan 2020

There is an increasing interest in plastics, both as a resource and as a pollutant. Climate change and environmental concerns have boosted the development of biodegradable plastics, spanning from disposable food containers to waste bags and agricultural mulch films. But how fast do these products degrade in Nordic soils and waste streams?

Status Active
Start - end date 01.01.2020 - 30.09.2023
Project manager Claire Coutris
Division Division of Environment and Natural Resources
Department Bioresources and Recycling Technologies
Partners NIBIO, NORSUS, Green Dot Norway, SIMAS IKS, Norsk Landbruksrådgiving, Agri Råd.
Total budget 6480000
Funding source Norwegian Research Council and Handelens Miljøfond (Grant number 303560)

There is an increasing interest in plastics, both as a resource and as a pollutant. Although a lot of emphasis is placed on recycling, the use of recycled plastics is still low in Europe. In this context, climate change and environmental concerns have boosted the development of various types of biodegradable plastics.

The use of biodegradable plastics spans from disposable containers for food/drink, serviceware and wipes, via waste bags for food waste collected for biogas production, to agricultural films used to cover soil during vegetable production. Waste and recycling companies are poorly prepared for such a transition, as is the public, which struggles in keeping a profusion of products and their waste separation apart. In addition, biodegradable plastics may not degrade so quickly and completely that the products disappear in nature, and the label may encourage people think otherwise, enhancing littering.

Plastic types.png
In DGRADE, we are investigating biodegradable polymers, which can be fossil-based or bio-based. A biodegradable polymer is a material designed to undergo a significant change in its chemical structure (broken chemical bonds of the macromolecules), as a result of biological activity and under specific environmental conditions.

Non-degradable bio-based polymers (such as bio-PET, bio-PE, etc.) are outside the scope of this project. The ambiguous term "bioplastics" should be avoided, as the prefix "bio" doesn't indicate whether it stands for biodegradable or bio-based.​​​​

Our three main objectives

  • Firstly, we wanted to know how fast biodegradable mulch films used in agriculture are degraded in cold climatic regions like Norway. There is public concern that degradation may not occur fast enough, and that macro- and microplastics could accumulate in soils.
  • Secondly, we wanted to describe the fate of biodegradable plastics, such as compostable waste bags, glasses and cutlery, during composting and biogas production. It is important to verify that the intended end-of-life treatments are not a source of plastics to the environment.
  • Finally, we wanted to describe the environmental costs/benefits of biodegradable plastics and provide a life-cycle perspective in both agriculture and waste streams.

Ultimately, the project helped providing the recycling and composting sector with the information needed to make sound decisions on questions regarding these materials, and provide farmers with advice on which type of biodegradable plastic products to use for specific purposes and conditions.

Work packages

WP English.png
Work packages in DGRADE: WP1 Project management (NIBIO), WP2 Degradation in soil (NIBIO, with support from NLR and Agri Råd), WP3 Degradation in waste streams (NIBIO, with support from SIMAS), WP4 Life cycle analysis (NORSUS, with support from GDN and SIMAS), WP5 Dissemination (All)

Results achieved

  • ​​​​​​​Degradation in soil (WP2)

Before this project, the fate of biodegradable plastic mulch in soil was unknown under Nordic conditions. It has now been established that degradation occurs, albeit at a slower pace, with worse-case scenarios for complete degradation in Norwegian soils lying between 2.5 and 9 years, depending on climatic conditions, soil properties and agricultural practices. Beside higher soil temperature, higher soil organic matter content has been shown to accelerate degradation.

 

  • Degradation in waste streams (WP3)

The project has demonstrated through a full-scale experiment conducted at an industrial composting plant that compostable plastic products, such as polylactic acid (PLA) glasses, are successfully degraded within the time frame of the composting process. Metagenomics analysis during the whole composting process also demonstrated that the main actors of degradation are fungi, naturally present in compost.

For biodegradable plastics entering biogas production, on the other end, we demonstrated that the biodegradable plastic bags used in Norway for food waste collection were only marginally degraded during biogas process, even after thermal hydrolysis pretreatment and high temperature conditions. So, unless biogas digestate is further treated to remove biodegradable plastic residues, the application of digestate will lead to accumulation of plastics in agricultural soils.

 

  • Life cycle analysis (WP4)

We showed that biodegradable mulch was not necessarily the most environmentally friendly alternative compared to e.g. conventional polyethylene mulch, and uncovered important knowledge gaps related to biodegradable plastic production. LCA also showed that food waste collection in paper bags results in a lower climatic impact compared to food waste collection in biodegradable and conventional plastic bags and is the only option removing the risk for plastic pollution.

A short summary of the results (in Norwegian)

Forum Landbruksplast made a short video (3 min, in Norwegian) summarizing the project's results.

For special interested (and Norwegian speakers), we have also recorded the final seminar, where all topics and results are presented and discussed. This (over 4 hour-long) video is available upon request.

Publications in the project

Abstract

De siste årene har det kommet en rekke bionedbrytbare plastvarianter, også i Norge. Men hvor nedbrytbar er egentlig denne plasten under norske forhold med relativt lave temperaturer? Brytes den fullstendig ned, eller omdannes den til makro- eller mikroplast i stedet? Gjennom prosjektet DGRADE – Nedbrytning av bionedbrytbar plast i jord og avfallsstrømmer har forskere forsøkt å finne svar på disse spørsmålene. De kan nå slå fast at plasten brytes ned, men kun hvis forholdene ligger til rette for det. Hvis ikke forholdene er gode nok, kan også nedbrytbare plastprodukter bidra til plastforsøpling

Abstract

Søkelyset på utfordringene med plast og forsøplingsproblematikken har sammen med nye krav og forbud fra EU, ført til at mange produsenter ønsker seg gode alternativer til fossil plast. Et resultat av dette er at stadig flere velger bionedbrytbar plast i emballasje eller som alternativ i landbruket. Men hva skjer med den bionedbrytbare plasten? Enten ute på jordet eller i kommunale biokomposteringsanlegg. Blir den brutt ned? Det er noe Grønt Punkt Norge ønsker bedre svar på. Derfor har vi vært initiativtaker til et 3-årig prosjekt hvor NIBIO skal forske på dette. Prosjektet er nå halvveis og onsdag 24. mars vil forsker Claire Coutris fra NIBIO dele noen foreløpige resultater.

Abstract

There is an increasing interest in plastics, both as a resource and as a pollutant. In Europe, 25.8 million tons of plastic waste are generated each year, and their effects on climate, economy, human and environmental health are major challenges that society needs to address. Although a lot of emphasis is placed on recycling, the use of recycled plastics is still low in the EU. In this context, climate change and environmental concerns have boosted the development of various types of biodegradable plastics. The use of biodegradable plastics spans from disposable containers for food/drink, serviceware and wipes, via waste bags for organic waste collected for biogas production, to agricultural films used to cover soil during vegetable production. However, biodegradable plastics are rarely degraded so quickly and completely that the products disappear in nature, and the label may encourage people think otherwise, enhancing littering. The aim of our study was to describe the fate of biodegradable materials and products during waste treatment, and more specifically during composting. How long does it take these materials to degrade? What are the conditions for degradation, and ultimately, for obtaining plastic-free compost products? To answer these questions, we selected relevant materials, including compostable serviceware, biodegradable plastic bags used for organic waste collection, and biodegradable agricultural mulch films. Composting experiments were performed both at lab-scale (1.5 L containers with externally applied heating) and larger scale (in 140 L insulated compost tumblers, with natural heating from the composting processes, continuously monitored). The endpoints studied were recovery, mass loss, changes in morphology and composition, and microbial analysis of the various composts. In addition, we assessed the applicability of chemical digestion methods used for sample pretreatment of environmental samples containing conventional plastics to biodegradable plastics. Biodegradable plastics is an umbrella term covering materials with diverse polymeric compositions and thus material properties. This was well demonstrated by our selected materials, which displayed distinct degradation behaviors under similar controlled conditions. The time-course of degradation during composting will be presented for all selected materials, together with the main parameters influencing their degradation rates. In addition, some methodological challenges in this research field will be discussed. Finally, experience from a municipal composting facility receiving biodegradable plastic waste will also be presented to put our laboratory-based results into perspective.

Abstract

Stadig flere bønder bytter ut tradisjonell landbruksplast med bionedbrytbar plastfilm som kan freses rett ned i jorda etter bruk. Nå er forskere i gang med å undersøke hvor nedbrytbar den faktisk er under norske forhold.

Abstract

Resirkulering av organisk avfall er et prioritert tema innen sektorene landbruk, klima og avfall, og skal bidra til at organisk materiale og næringsstoffer føres tilbake til jord. Dette kan motvirke en langsiktig trend der moldinnholdet i matjorda gradvis blir lavere, noe som ser ut til å bli et økende problem i forbindelse med klimaendringer og økende behov for mat. Tilbakeføring av næringsstoffene i organisk avfall skal på sin side bidra til å redusere behovet for mineralgjødsel, og dermed minske behovet for energikrevende gjødselproduksjon og uttømming av begrensete ressurser av mineralsk fosfat.

Abstract

Organic industrial and household waste is increasingly used in biogas plants to produce bioenergy, generating at the same time extensive amounts of organic residues, called biogas digestates. While agricultural soils can benefit from the organic matter and nutrients, in particular nitrogen and phosphorus, contained in biogas digestates, we need to assess the environmental and health risks associated to the undesirable substances that may come along. Among those, only a few are covered by actual regulations. For instance, the quantity of plastic materials below 4 mm in biogas digestate is currently not limited to any threshold, despite its likely occurrence in organic waste (waste bag remains and wrong waste sorting) and persistence in the environment. The aim of our study was identify and quantify plastic materials in digestates from Norwegian biogas plants, that are using various types of organic waste sources (e.g. sewage sludge, food waste, animal manure). In addition, a lab-scale experiment was set up to assess the physical and chemical transformations undergone during biogas processes by plastic materials commonly found in digestates. The methods used in our study included simultaneous thermal analysis coupled to Fourier transform-Infrared spectroscopy (for analysis of polymer composition), scanning electron microscopy (for assessment of physical transformations), and a range of physical and chemical extractions for recovering plastic materials from biogas digestates. While all digestates complied with current regulations, plastic particles with a size of 0.2-3 mm made up to 1% (on dry mass basis) of the samples analyzed. Analysis of the polymeric composition of the recovered plastic fragments confirmed that they originated both from the waste bags themselves (shredded during the first steps of waste handling) and from wrong waste sorting. In addition, the lab-scale biogas treatment was shown to considerably change the structure of the studied plastic materials, illustrating a pathway for the formation of secondary microplastics. Some analytical challenges linked to the size and aging of the plastic materials, as well as the complex composition of the digestates, will be discussed. From a broader perspective, a few options will be presented to address the presence of plastic materials in biogas digestates, and thereby minimize the risk associated to their use as soil amendment.

Abstract

Vi har alle hørt om problemene plast i havet kan føre med seg. Men plast havner også i jord, blant annet via avløpsslam, biogjødsel og fra plastbruk i landbruket. Akkurat hvor mye plast det er snakk om er imidlertid uvisst.

Abstract

Vi har alle hørt om problemene plast i havet kan føre med seg. Men plast havner også i jord, blant annet via avløpsslam, biogjødsel og fra plastbruk i landbruket. Akkurat hvor mye plast det er snakk om, er imidlertid uvisst.

Abstract

Vi har alle hørt om problemene plast i havet kan føre med seg. Men plast havner også i jord, blant annet via avløpsslam, biogjødsel og fra plastbruk i landbruket. Akkurat hvor mye plast det er snakk om, er imidlertid uvisst.