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Highlights: Automotive Foam Basics: Biodegradation

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However, the resulting JRC “Plastics LCA method”, turned<br />

out to be highly problematic and rather biased, making it<br />

impossible to carry out complete and well-balanced LCA<br />

comparisons between biobased and fossil-based plastics.<br />

In its current form, the method strengthens the current<br />

dominance of fossil-based plastics and often just neglects<br />

the negative impacts of the extraction of fossil resources<br />

on climate and environment. This is grossly at odds with<br />

the EU’s commitment towards reducing the dependency<br />

on fossil-carbon and becoming climate neutral. The<br />

methodology also undermines many of the targets set out<br />

in the EU Green Deal and Plastics Strategy. It is therefore<br />

also not in line with the latest IPCC report saying we need<br />

to stop using fossil resources.<br />

However, the whole <strong>issue</strong> is not only about bioplastics.<br />

European Bioplastics drafted a two-page Position Paper [2]<br />

N.N.: EUBA position on the JRC LCA Methodology and got<br />

the support of other European Biobased Industry Groups,<br />

organized in the European Bioeconomy Alliance (EUBA).<br />

This is important support since this is not only touching the<br />

bioplastics industry but the whole EU bioeconomy industry.<br />

Therefore, EUBP, together with the other members of the<br />

European Bioeconomy Alliance, have recently called upon<br />

the Commission not to make use of the methodology until it<br />

has been re-opened and significantly revised and improved.<br />

Herewith a summary of our findings to illustrate<br />

the significant asymmetry and shortcomings of the<br />

methodology.<br />

Biogenic carbon sequestration<br />

The methodology ignores the key advantage of biobased<br />

products, which is the uptake of carbon dioxide from<br />

the atmosphere, sequestering it into products, and so<br />

preventing that carbon dioxide from contributing to climate<br />

change. This is a key advantage over fossil-based plastics.<br />

Biobased products replace fossil carbon in plastics and<br />

reduce the emissions of greenhouse gases. This fact should<br />

be accounted for by being a mandatory part of a fair and<br />

balanced assessment of environmental impacts. As an<br />

example, the EU standard EN 16760 (“Biobased products –<br />

Life cycle assessment”) provides guidance on how biogenic<br />

carbon uptake should be accounted for in the assessment of<br />

biobased plastics, but this calculation remains a voluntary,<br />

meaningless option in the suggested methodology.<br />

Comparing mature and immature production<br />

systems<br />

For fossil-based plastics, the raw material extraction,<br />

production, conversion, logistics, and end-of-life options<br />

have been optimized for the last 50–70 years, while<br />

many biobased plastics are still in their early stage of<br />

development. They are at the beginning of their maturity or<br />

optimization curve.<br />

The LCA methodology provides no real answer on how to<br />

compare systems that have different levels of maturity. In a<br />

meaningful assessment (LCA should inform about decisions<br />

that shape the future) of biobased plastics, this potential<br />

for further improvements should be incorporated. By not<br />

acknowledging these differences, the LCA methodology<br />

mainly supports the status-quo and ignores the potential of<br />

innovation. That clearly can’t be the goal.<br />

Data reporting requirements<br />

In an area where the report really goes wrong are the<br />

requirements on data reporting (this is the basic data that<br />

goes into the life cycle inventory). It is not demanding for<br />

the same requirements for data sets for biobased and<br />

fossil-based feedstocks. For biobased production systems,<br />

detailed company-specific data are required, while for<br />

fossil-based systems, the industry average (black boxes)<br />

data sets are still acceptable. It is still allowed to just exclude<br />

emissions coming from accidents, spills, and oil fires. After<br />

30 years of performing LCA studies, these practices need<br />

to be stopped. For biobased plastics products, all kind<br />

sof details are requested, which as such is totally correct,<br />

about agricultural emissions, machinery use, heavy metals,<br />

chemical use, resource types, production locations and<br />

water consumption, while there is no or hardly any attention<br />

paid to similar aspects for the fossil-based alternatives.<br />

Incorporation of Land Use Change (LUC)<br />

For biobased plastics, LUC shall be included, while for<br />

fossil-based plastics, the methodology is much less strict.<br />

This is not correct, including aspects should be consistent<br />

for all types of materials. Even if the contributions seem<br />

to be relatively small (which is often used as an excuse for<br />

ignoring it), they should be included to increase awareness<br />

and the fact that several relatively small contributions<br />

can lead to a significant contribution. Further, continuous<br />

improvement of agricultural practices, such as soil carbon<br />

uptake by improved management, needs to be taken up in<br />

the LCA calculations, instead of being parked at the side-line<br />

under the header: ‘additional environmental information.’<br />

Inconsistent inclusion of indirect effects<br />

Negative indirect effects for biobased plastics, such as<br />

Indirect Land Use Change(iLUC), are considered relevant<br />

and recommended to be included, while the inclusion of<br />

negative indirect effects of fossil-based plastics is explicitly<br />

ruled out. A big omission is the lack of methodology to<br />

include the direct and indirect effects of the leakage of<br />

persistent plastics into our environment. On the other<br />

hand, great importance is given in the LCA methodology<br />

to the scientifically controversial <strong>issue</strong> of Indirect Land<br />

Use Change (iLUC). It’s based on mere model calculations<br />

that vary greatly due to the lack of standardized methods<br />

– interestingly, unlike the calculation methods for biogenic<br />

carbon uptake. Despite of the uncertainty, the assessment<br />

of iLUC is considered important and mandatory in the LCA<br />

methodology. Further iLUC contributions are often included<br />

while no proof has been provided if it also takes place.<br />

Requirements for providing proof<br />

Also, with this aspect, the methodology is not consistent.<br />

For positive indirect effects of biobased plastic products,<br />

such as soil carbon storage by improved agricultural<br />

management, proof is required, while no proof is required<br />

for negative indirect effects of biobased materials, like iLUC.<br />

Biodiversity impacts<br />

In the JRC LCA method, the topic of biodiversity is<br />

strongly linked to the agricultural production process of<br />

biobased products. For fossil-based products, there is<br />

much less attention for this topic, while there is a direct,<br />

Opinion<br />

bioplastics MAGAZINE [<strong>01</strong>/22] Vol. 17 43

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