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Marine pollution / Marine degradation<br />

By:<br />

Francesco Degli Innocenti<br />

Ecology of Products and Environmental Communication<br />

Novamont,<br />

Novara, Italy<br />

biodegradation because this depositional environment<br />

is microbiologically different from composting. Similarly,<br />

tests specific to the marine environment are now under<br />

development (cf fig. 1). Novamont studied the behaviour<br />

of MATER-BI through ASTM [3] and ISO [4] test methods<br />

(cf fig. 2). Tests performed in marine sediments showed<br />

biodegradation (as CO 2<br />

evolution) in excess of 90 %<br />

(absolute or relative to cellulose) in less than one year;<br />

Certiquality (Certification Institute; Milan,) verified<br />

these results within the European Commission’s pilot<br />

program ETV [5]. These results are in agreement with<br />

previous findings [6].<br />

Biodegradability and risk assessment<br />

How should we interpret these very promising<br />

biodegradation data? Generally speaking, the<br />

environmental risk depends on the concentration of<br />

the environmental stressor and on its residence time<br />

in the environment. The lower the concentration and<br />

the shorter the residence time, the better. Bioplastics<br />

do not immediately disappear upon exposure to the<br />

sea. However, biodegradability is a factor that reduces<br />

the risk by reducing the stressor’s residence time.<br />

Therefore, on one hand the idea of solving the problem<br />

of plastics in the ocean just by shifting to bioplastics is<br />

unfounded. On the other hand, for those applications<br />

where accidental release is certain or very probable,<br />

biodegradability can become a means of decreasing<br />

the environmental risk. Materials that show full and<br />

relatively fast biodegradation may be suitable for plastic<br />

products known to wear down or become stranded<br />

(for example, fishing gear) and scatter into the sea.<br />

Bioplastics like MATER-BI materials hold promise for<br />

aquaculture professional applications (e. g. nets for<br />

mussels farming, cf. fig. 3) where the disposal of plastic<br />

waste is an inevitable outcome.<br />

Fig. 3: Mussel farming nets (Source unknown, found e. g. in<br />

presentations by ISPRA [7])<br />

www.novamont.com<br />

[1] European Parliament and Council Directive 94/62/EC of 20<br />

December 1994 on packaging and packaging waste<br />

[2] EN 13432:2000 Packaging. Requirements for packaging<br />

recoverable through composting and biodegradation. Test scheme<br />

and evaluation criteria for the final acceptance of packaging<br />

[3] ASTM D7991 – 15 Standard Test Method for Determining Aerobic<br />

Biodegradation of Plastics Buried in Sandy Marine Sediment under<br />

Controlled Laboratory Conditions<br />

[4] ISO/DIS 19679 Plastics — Determination of aerobic biodegradation<br />

of non-floating plastic materials in a seawater/sediment interface<br />

— Method by analysis of evolved carbon dioxide<br />

[5] http://iet.jrc.ec.europa.eu/etv/aerobic-biodegradation-mater-biaf03a0-and-mater-bi-af05s0-mater-bi-third-generation-undermarine<br />

[6] F. Degli Innocenti (2012) Single-use carrier bags: littering, bans and<br />

biodegradation in sea water. Bioplastic Magazine 042012 (vol 7):44-<br />

45<br />

[7] http://oceania.research.um.edu.mt/cms/calypsoweb/images/<br />

meeting2/catania-meeting/Andaloro.pdf<br />

bioplastics MAGAZINE [<strong>02</strong>/16] Vol. 11 17

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