Karl-Heinrich Engesser

Bacterial Rieske non‐heme iron oxygenases catalyse the transformation of a wide range of aromatic compounds to vicinal cis ‐dihydrodiols. Such compounds have been successfully applied in chemoenzymatic synthetic routes for, for example, pharmaceuticals, natural products and polymers. In the case of benzoate, only (1 S ,2 R )‐ cis ‐1,2‐dihydroxy‐2‐hydrobenzoate is readily accessible via enzymatic transformation, but not the regioisomeric cis ‐2,3‐dihydroxy‐2,3‐dihydrobenzoate (2,3‐DD) or cis ‐3,4‐dihydroxy‐3,4‐dihydrobenzoate. While trace amounts of putative cis ‐2,3‐DD have been obtained before by using p ‐cumate 2,3‐dioxygenase (PCDO) or a combination of chlorobenzene dioxygenase and nitrilase, none of these approaches enabled its production and isolation at a greater scale for potential use as a chiral building block in organic synthesis. We here provide a protocol for biotransformation of benzoate yielding (2 R ,3 S )‐2,3‐dihydroxy‐2,3‐dihydrobenzoate using the PCDO of Pseudomonas citronellolis strain EB200 with negligible formation of side products. An isolation procedure suitable for production of the 2,3‐DD sodium salt monohydrate at high purity (> 95%) at a gram scale, and a comprehensive characterisation of this novel metabolite is given.

Rhodococcus erythropolis FUR100 was isolated from a mixture of soil and activated sludge. It can use furan as a sole source of carbon and energy. Its draft genome sequence may provide insight into the genetics of furan catabolism.

Mycolicibacterium gadium IBE100 and Mycobacterium paragordonae IBE200 are aerobic, chemoorganoheterotrophic bacteria isolated from activated sludge from a wastewater treatment plant. They use 2‐methylpropene (isobutene, 2‐MP) as the sole source of carbon and energy. Here, we postulate a degradation pathway of 2‐methylpropene derived from whole genome sequencing, differential expression analysis and peptide‐mass fingerprinting. Key genes identified are coding for a 4‐component soluble diiron monooxygenase with epoxidase activity, an epoxide hydrolase, and a 2‐hydroxyisobutyryl‐CoA mutase. In both strains, involved genes are arranged in clusters of 61.0 and 58.5 kbp, respectively, which also contain the genes coding for parts of the aerobic pathway of adenosylcobalamin synthesis. This vitamin is essential for the carbon rearrangement reaction catalysed by the mutase. These findings provide data for the identification of potential 2‐methylpropene degraders.

A combined system of a biotrickling filter and a non-thermal plasma (NTP) in a downstream airflow was operated for 1220 days for treatment of emissions of styrene and secondary emissions of germs formed in the biological process. The biotrickling filter was operated at variable inlet concentrations, empty bed residence times (EBRT), type and dosage of fertilizers, irrigation densities, and starvation periods, while dielectric barrier discharge and corona discharge were operated at different specific input energy levels to achieve optimal conditions. Under these conditions, efficiencies in the removal of volatile organic compounds (VOCs), germs and styrene of 96–98%, 1–4 log units and 24.7–50.1 g C m⁻³ h⁻¹ were achieved, respectively. Fluid simulations of the NTP and a germ emission-based clocking of the discharge reveal further energy saving potentials of more than 90%. The aim of an energy-efficient elimination of VOCs through a biotrickling filter and of secondary germ emissions by a NTP stage in a downstream airflow for potential re-use of purified waste gas as process gas for industrial application was successfully accomplished.

A total of 11 bacterial strains capable of completely degrading 2-butoxyethanol (2-BE) were isolated from forest soil, a biotrickling filter, a bioscrubber, and activated sludge, and identified by 16S rRNA gene sequence analysis. Eight of these strains belong to the genus Pseudomonas; the remaining three strains are Hydrogenophaga pseudoflava BOE3, Gordonia terrae BOE5, and Cupriavidus oxalaticus BOE300. In addition to 2-BE, all isolated strains were able to grow on 2-ethoxyethanol and 2-propoxyethanol, ethanol, n-hexanol, ethyl acetate, 2-butoxyacetic acid (2-BAA), glyoxylic acid, and n-butanol. Apart from the only gram-positive strain isolated, BOE5, none of the strains were able to grow on the nonpolar ethers diethyl ether, di-n-butyl ether, n-butyl vinyl ether, and dibenzyl ether, as well as on 1-butoxy-2-propanol. Strains H. pseudoflava BOE3 and two of the isolated pseudomonads, Pseudomonas putida BOE100 and P. vancouverensis BOE200, were studied in more detail. The maximum growth rates of strains BOE3, BOE100, and BOE200 at 30 °C were 0.204 h⁻¹ at 4 mM, 0.645 h⁻¹ at 5 mM, and 0.395 h⁻¹ at 6 mM 2-BE, respectively. 2-BAA, n-butanol, and butanoic acid were detected as potential metabolites during the degradation of 2-BE. These findings indicate that the degradation of 2-BE by the isolated gram-negative strains proceeds via oxidation to 2-BAA with subsequent cleavage of the ether bond yielding glyoxylate and n-butanol. Since Gordonia terrae BOE5 was the only strain able to degrade nonpolar ethers like diethyl ether, the degradation pathway of 2-BE may be different for this strain.

Fluoroaromatics are widely and—in recent years—increasingly used as agrochemicals, starting materials for chemical syntheses and especially pharmaceuticals. This originates from the special properties the carbon-fluorine bond is imposing on organic molecules. Hence, fluoro-substituted compounds more and more are considered to be important potential environmental contaminants. On the other hand, the microbial potentials for their transformation and mineralization have received less attention in comparison to other haloaromatics. Due to the high electronegativity of the fluorine atom, its small size, and the extraordinary strength of the C-F bond, enzymes and mechanisms known to facilitate the degradation of chloro- or bromoarenes are not necessarily equally active with fluoroaromatics. Here, we review the literature on the microbial degradation of ring and side-chain fluorinated aromatic compounds under aerobic and anaerobic conditions, with particular emphasis being placed on the mechanisms of defluorination reactions.

Summary: B urkholderia fungorum FLU 100 simultaneously oxidized any mixture of toluene, benzene and mono‐halogen benzenes to (3‐substituted) catechols with a selectivity of nearly 100%. Further metabolism occurred via enzymes of ortho cleavage pathways with complete mineralization. During the transformation of 3‐methylcatechol, 4‐carboxymethyl‐2‐methylbut‐2‐en‐4‐olide (2‐methyl‐2‐enelactone, 2‐ ML ) accumulated transiently, being further mineralized only after a lag phase of 2 h in case of cells pre‐grown on benzene or mono‐halogen benzenes. No lag phase, however, occurred after growth on toluene. Cultures inhibited by chloramphenicol after growth on benzene or mono‐halogen benzenes were unable to metabolize 2‐ ML supplied externally, even after prolonged incubation. A control culture grown with toluene did not show any lag phase and used 2‐ ML as a substrate. This means that 2‐ ML is an intermediate of toluene degradation and converted by specific enzymes. The conversion of 4‐methylcatechol as a very minor by‐product of toluene degradation in strain FLU 100 resulted in the accumulation of 4‐carboxymethyl‐4‐methylbut‐2‐en‐4‐olide (4‐methyl‐2‐enelactone, 4‐ ML ) as a dead‐end product, excluding its nature as a possible intermediate. Thus, 3‐methylcyclohexa‐3,5‐diene‐1,2‐diol, 3‐methylcatechol, 2‐methyl muconate and 2‐ ML were identified as central intermediates of productive ortho cleavage pathways for toluene metabolism in B . fungorum FLU 100.