Coupling pathway prediction and fluorescence spectroscopy to assess the impact of auxiliary substrates on micropollutant biodegradation

Author:

Schittich Anna‐Ricarda123ORCID,Fenner Kathrin45ORCID,Stedmon Colin A.6ORCID,Xu Jianxin1ORCID,McKnight Ursula S.7ORCID,Smets Barth F.12ORCID

Affiliation:

1. Department of Environmental and Resource Engineering Technical University of Denmark Lyngby Denmark

2. Sino‐Danish Center for Education and Research Denmark

3. Department of Civil and Environmental Engineering University of California Berkeley Berkeley California USA

4. Eawag, Swiss Federal Institute of Aquatic Science and Technology Dübendorf Switzerland

5. University of Zürich, Department of Chemistry Zürich Switzerland

6. National Institute of Aquatic Research Technical University of Denmark Lyngby Denmark

7. Swedish Meteorological and Hydrological Institute Norrköping Sweden

Abstract

AbstractSome bacteria can degrade organic micropollutants (OMPs) as primary carbon sources. Due to typically low OMP concentrations, these bacteria may benefit from supplemental assimilation of natural substrates present in the pool of dissolved organic matter (DOM). The biodegradability of such auxiliary substrates and the impacts on OMP removal are tightly linked to biotransformation pathways. Here, we aimed to elucidate the biodegradability and effect of different DOM constituents for the carbofuran degrader Novosphingobium sp. KN65.2, using a novel approach that combines pathway prediction, laboratory experiments, and fluorescence spectroscopy. Pathway prediction suggested that ring hydroxylation reactions catalysed by Rieske‐type dioxygenases and flavin‐dependent monooxygenases determine the transformability of the 11 aromatic compounds used as model DOM constituents. Our approach further identified two groups with distinct transformation mechanisms amongst the four growth‐supporting compounds selected for mixed substrate biodegradation experiments with the pesticide carbofuran (Group 1: 4‐hydroxybenzoic acid, 4‐hydroxybenzaldehyde; Group 2: p‐coumaric acid, ferulic acid). Carbofuran biodegradation kinetics were stable in the presence of both Group 1 and Group 2 auxiliary substrates. However, Group 2 substrates would be preferable for bioremediation processes, as they showed constant biodegradation kinetics under different experimental conditions (pre‐growing KN65.2 on carbofuran vs. DOM constituent). Furthermore, Group 2 substrates were utilisable by KN65.2 in the presence of a competitor (Pseudomonas fluorescens sp. P17). Our study thus presents a simple and cost‐efficient approach that reveals mechanistic insights into OMP‐DOM biodegradation.

Publisher

Wiley

Subject

Ecology, Evolution, Behavior and Systematics,Microbiology

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