Structure-based interpretation of biotransformation pathways of amide-containing compounds in sludge-seeded bioreactors.

Partial microbial degradation of xenobiotic compounds in wastewater treatment plants (WWTPs) results in the formation of transformation products, which have been shown to be released and detectable in surface waters. Rule-based systems to predict the structures of microbial transformation products often fail to discriminate between alternate transformation pathways because structural influences on enzyme-catalyzed reactions in complex environmental systems are not well understood. The amide functional group is one such common substructure of xenobiotic compounds that may be transformed through alternate transformation pathways. The objective of this work was to generate a self-consistent set of biotransformation data for amide-containing compounds and to develop a metabolic logic that describes the preferred biotransformation pathways of these compounds as a function of structural and electronic descriptors. We generated transformation products of 30 amide-containing compounds in sludge-seeded bioreactors and identified them by means of HPLC-linear ion trap-orbitrap mass spectrometry. Observed biotransformation reactions included amide hydrolysis and N-dealkylation, hydroxylation, oxidation, ester hydrolysis, dehalogenation, nitro reduction, and glutathione conjugation. Structure-based interpretation of the results allowed for identification of preferences in biotransformation pathways of amides: primary amides hydrolyzed rapidly; secondary amides hydrolyzed at rates influenced by steric effects; tertiary amides were N-dealkylated unless specific structural moieties were present that supported other more readily enzyme-catalyzed reactions. The results allowed for the derivation of a metabolic logic that could be used to refine rule-based biotransformation pathway prediction systems to more specifically predict biotransformations of amide-containing compounds.

[1]  A. López-Munguía,et al.  The amidase activity of Candida antarctica lipase B is dependent on specific structural features of the substrates , 2006 .

[2]  Lynda B. M. Ellis,et al.  The University of Minnesota pathway prediction system: predicting metabolic logic , 2008, Nucleic Acids Res..

[3]  Gilles Klopman,et al.  META, 3. A Genetic Algorithm for Metabolic Transform Priorities Optimization , 1997, J. Chem. Inf. Comput. Sci..

[4]  J. Iley,et al.  The oxidative dealkylation of tertiary amides: mechanistic aspects , 2000 .

[5]  A. Boxall,et al.  When synthetic chemicals degrade in the environment. , 2004, Environmental science & technology.

[6]  E. Thurman,et al.  Occurrence of selected pesticides and their metabolites in near-surface aquifers of the Midwestern U , 1996 .

[7]  T. Bhalla,et al.  Amidases: versatile enzymes in nature , 2009 .

[8]  S Dimitrov,et al.  Probabilistic assessment of biodegradability based on metabolic pathways: CATABOL System , 2002, SAR and QSAR in environmental research.

[9]  Adriano Joss,et al.  Biological degradation of pharmaceuticals in municipal wastewater treatment: proposing a classification scheme. , 2006, Water research.

[10]  Manfred Wagner,et al.  Multistep approach for the structural identification of biotransformation products of iodinated X-ray contrast media by liquid chromatography/hybrid triple quadrupole linear ion trap mass spectrometry and (1)H and (13)C nuclear magnetic resonance. , 2009, Analytical chemistry.

[11]  Edward J. Bouwer,et al.  Biodegradation and removal of pharmaceuticals and personal care products in treatment systems: a review , 2009, Biodegradation.

[12]  H. Govers,et al.  Quantitative structure-activity relationships for biodegradation. , 1990, Ecotoxicology and environmental safety.

[13]  Lynda B. M. Ellis,et al.  The University of Minnesota Biocatalysis/Biodegradation Database: the first decade , 2005, Nucleic Acids Res..

[14]  Kevin V Thomas,et al.  Impacts of competitive inhibition, parent compound formation and partitioning behavior on the removal of antibiotics in municipal wastewater treatment. , 2010, Environmental science & technology.

[15]  Dirk Löffler,et al.  Transformation of the X-ray contrast medium iopromide in soil and biological wastewater treatment. , 2008, Environmental science & technology.

[16]  Keli Han,et al.  Theoretical study of N-dealkylation of N-cyclopropyl-N-methylaniline catalyzed by cytochrome P450: insight into the origin of the regioselectivity. , 2009, Dalton transactions.

[17]  Felix E. Wettstein,et al.  Environmental fate of phenolic endocrine disruptors: field and laboratory studies , 2009, Philosophical Transactions of the Royal Society A: Mathematical, Physical and Engineering Sciences.

[18]  C. Criddle,et al.  The kinetics of cometabolism , 1993, Biotechnology and bioengineering.

[19]  D. Barceló,et al.  Identification and structural characterization of biodegradation products of atenolol and glibenclamide by liquid chromatography coupled to hybrid quadrupole time-of-flight and quadrupole ion trap mass spectrometry. , 2008, Journal of chromatography. A.

[20]  R. Hanzlik,et al.  N-dealkylation of tertiary amides by cytochrome P-450. , 1991, Xenobiotica; the fate of foreign compounds in biological systems.

[21]  J. Coats,et al.  Fate of Transformation Products of Synthetic Chemicals , 2009 .

[22]  A. Hay,et al.  Bacterial Degradation of N,N-Diethyl-m-Toluamide (DEET): Cloning and Heterologous Expression of DEET Hydrolase , 2007, Applied and Environmental Microbiology.

[23]  V. de Lorenzo,et al.  Systems biology approaches to bioremediation. , 2008, Current opinion in biotechnology.

[24]  Margarita Martín,et al.  Characterization of Two Novel Propachlor Degradation Pathways in Two Species of Soil Bacteria , 1999, Applied and Environmental Microbiology.

[25]  C. Peters,et al.  Polycyclic aromatic hydrocarbon biodegradation rates: a structure-based study. , 2005, Environmental science & technology.

[26]  D. Aga,et al.  Application of ion trap-MS with H/D exchange and QqTOF-MS in the identification of microbial degradates of trimethoprim in nitrifying activated sludge. , 2005, Analytical chemistry.

[27]  D. Barceló,et al.  Metabolism studies of diclofenac and clofibric acid in activated sludge bioreactors using liquid chromatography with quadrupole - time-of-flight mass spectrometry , 2009 .

[28]  D. Aga,et al.  Formation and transport of the sulfonic acid metabolites of alachlor and metolachlor in soil. , 2001, Environmental science & technology.

[29]  Heinz Singer,et al.  High-throughput identification of microbial transformation products of organic micropollutants. , 2010, Environmental science & technology.

[30]  Thorsten Reemtsma,et al.  Pathways and metabolites of microbial degradation of selected acidic pharmaceutical and their occurrence in municipal wastewater treated by a membrane bioreactor. , 2005, Water research.

[31]  J. Morel,et al.  Effect of sludge-amendment or nutrient addition on the biodegradation of the herbicide isoproturon in soil. , 2001, Chemosphere.

[32]  D. L. Freedman,et al.  Reduction and Acetylation of 2,4-Dinitrotoluene by a Pseudomonas aeruginosa Strain , 1996, Applied and environmental microbiology.

[33]  T. Vicent,et al.  Degradation of the drug sodium diclofenac by Trametes versicolor pellets and identification of some intermediates by NMR. , 2010, Journal of hazardous materials.

[34]  R. H. Nimmo-Smith Aromatic N-deacylation by chick-kidney mitochondria. , 1960, The Biochemical journal.

[35]  René P Schwarzenbach,et al.  Identification of transformation products of organic contaminants in natural waters by computer-aided prediction and high-resolution mass spectrometry. , 2009, Environmental science & technology.

[36]  D. Fournand,et al.  Aliphatic and enantioselective amidases: from hydrolysis to acyl transfer activity , 2001, Journal of applied microbiology.