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Biodegradation of poly(butylene succinate) in soil laboratory incubations assessed by stable carbon isotope labelling

Nature Communications 2022 126 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 50 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Michael Sander, Taylor F. Nelson, Michael Sander, Hans‐Peter E. Kohler, Rebekka Baumgartner, Rebekka Baumgartner, Michael Sander, Kristopher McNeill Michael Sander, Madalina Jaggi, Kristopher McNeill Kristopher McNeill Glauco Battagliarin, Glauco Battagliarin, Stefano M. Bernasconi, Andreas Künkel, Andreas Künkel, Andreas Künkel, Glauco Battagliarin, Glauco Battagliarin, Glauco Battagliarin, Glauco Battagliarin, Glauco Battagliarin, Glauco Battagliarin, Andreas Künkel, Glauco Battagliarin, Glauco Battagliarin, Glauco Battagliarin, Carsten Sinkel, Glauco Battagliarin, Glauco Battagliarin, Carsten Sinkel, Andreas Künkel, Andreas Künkel, Andreas Künkel, Andreas Künkel, Andreas Künkel, Andreas Künkel, Glauco Battagliarin, Glauco Battagliarin, Hans‐Peter E. Kohler, Michael Sander, Kristopher McNeill Michael Sander, Michael Sander, Michael Sander, Kristopher McNeill

Summary

Researchers used carbon isotope labeling to precisely track how biodegradable plastic (poly(butylene succinate)) breaks down in agricultural soil over more than a year, finding that 65% fully converted to CO2 while the rest integrated into the soil. This new tracking method provides a reliable way to evaluate whether "biodegradable" plastics actually decompose as claimed in real soil conditions.

Using biodegradable instead of conventional plastics in agricultural applications promises to help overcome plastic pollution of agricultural soils. However, analytical limitations impede our understanding of plastic biodegradation in soils. Utilizing stable carbon isotope (<sup>13</sup>C-)labelled poly(butylene succinate) (PBS), a synthetic polyester, we herein present an analytical approach to continuously quantify PBS mineralization to <sup>13</sup>CO<sub>2</sub> during soil incubations and, thereafter, to determine non-mineralized PBS-derived <sup>13</sup>C remaining in the soil. We demonstrate extensive PBS mineralization (65 % of added <sup>13</sup>C) and a closed mass balance on PBS-<sup>13</sup>C over 425 days of incubation. Extraction of residual PBS from soils combined with kinetic modeling of the biodegradation data and results from monomer (i.e., butanediol and succinate) mineralization experiments suggest that PBS hydrolytic breakdown controlled the overall PBS biodegradation rate. Beyond PBS biodegradation in soil, the presented methodology is broadly applicable to investigate biodegradation of other biodegradable polymers in various receiving environments.

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