Delftia acidovorans MC1 Resists High Herbicide Concentrations — a Study of Nutristat Growth on (RS)-2-(2,4-Dichlorophenoxy)propionate and 2,4-Dichlorophenoxyacetate

Delftia acidovorans MC1 was continuously cultivated under nutristat conditions with elevated concentrations of the herbicides (RS)-2-(2,4-dichlorophenoxy)propionate [(RS)-2,4-DP] and 2,4-dichlorophenoxyacetate (2,4-D). The presence of 1–5 mM of either of these compounds did not essentially inhibit growth. Moreover, substrate consumption was not essentially affected at pH values of 7.0–9.0 selected by reason of alkaline in situ conditions found e.g. on contaminated building rubble but was decreased at pH 9.3. The adenylate energy charge declined to some degree as the herbicide concentration rose, the extent of this increasing as the pH rose. This was caused by an increase in the concentration of ADP and in particular AMP, in contrast to the fairly constant ATP level of around 4 nmol/mg dry mass with (RS)-2,4-DP and 2 nmol/mg with 2,4-D. Comparison of the individual growth parameters with theoretical data taking into account maintenance coefficients of 0.48 mmol (RS)-2,4-DP/g*h and 0.6 mmol 2,4-D/g*h revealed that the culture followed purely kinetic rules. This excludes the necessity of using substrate to a significant extent to satisfy extra efforts in energy for homeostasic work under these accentuated conditions.

[1]  K. Oh,et al.  Degradation of 2,4-dichlorophenoxyacetic acid by mixed cultures of bacteria , 1990, Journal of Industrial Microbiology.

[2]  W. Babel,et al.  Phenol and its derivatives as heterotrophic substrates for microbial growth—An energetic comparison , 1994, Applied Microbiology and Biotechnology.

[3]  G. Ditzelmüller,et al.  Isolation and characterization of a 2-(2,4-dichlorophenoxy) propionic acid-degrading soil bacterium , 1990, Applied Microbiology and Biotechnology.

[4]  K. Engesser,et al.  Regulation of catabolic pathways of phenoxyacetic acids and phenols in Alcaligenes eutrophus JMP 134 , 1989, Archives of Microbiology.

[5]  K. Engesser,et al.  Metabolism of 2,4-dichlorophenoxyacetic acid, 4-chloro-2-methylphenoxyacetic acid and 2-methylphenoxyacetic acid by Alcaligenes eutrophus JMP 134 , 1988, Archives of Microbiology.

[6]  H. Sträuber,et al.  Evidence of Cytochrome P450-Catalyzed Cleavage of the Ether Bond of Phenoxybutyrate Herbicides in Rhodococcus Erythropolis K2-3 , 2004, Biodegradation.

[7]  S. Kleinsteuber,et al.  A transposon encoding the complete 2,4-dichlorophenoxyacetic acid degradation pathway in the alkalitolerant strain Delftia acidovorans P4a. , 2003, Microbiology.

[8]  W. Babel,et al.  Purification and Characterisation of the Enantiospecific Dioxygenases from Delftia acidovorans MC1 Initiating the Degradation of Phenoxypropionate and Phenoxyacetate Herbicides , 2003 .

[9]  F. Ataullakhanov,et al.  What Determines the Intracellular ATP Concentration , 2002, Bioscience reports.

[10]  D. Benndorf,et al.  The two enantiospecific dichlorprop/alpha-ketoglutarate-dioxygenases from Delftia acidovorans MC1--protein and sequence data of RdpA and SdpA. , 2002, Microbiological research.

[11]  W. Babel,et al.  Pseudo‐recalcitrance of Chlorophenoxyalkanoate Herbicides – Correlation to the Availability of α‐Ketoglutarate , 2001 .

[12]  S. Kleinsteuber,et al.  Physiological and genetic characteristics of two bacterial strains utilizing phenoxypropionate and phenoxyacetate herbicides. , 2001, Microbiological research.

[13]  W. Babel,et al.  A Theoretical Study on the Metabolic Requirements Resulting from α-Ketoglutarate-Dependent Cleavage of Phenoxyalkanoates , 2000, Applied and Environmental Microbiology.

[14]  S. Kleinsteuber,et al.  Comamonas acidovorans strain MC1: a new isolate capable of degrading the chiral herbicides dichlorprop and mecoprop and the herbicides 2,4-D and MCPA. , 1999, Microbiological research.

[15]  M. Santamaría,et al.  Comparative performance of enterobacterial repetitive intragenic consensus-polymerase chain reaction and lipopolysaccharide electrophoresis for the identification of Bradyrhizobium sp. (Lotus) strains , 1999 .

[16]  J. Tiedje,et al.  Evidence for Interspecies Gene Transfer in the Evolution of 2,4-Dichlorophenoxyacetic Acid Degraders , 1998, Applied and Environmental Microbiology.

[17]  W. Babel,et al.  Etherolytic cleavage of 4‐(2,4‐dichlorophenoxy)butyric acid and 4‐(4‐chloro‐2‐methylphenoxy)butyric acid by species of Rhodococcus and Aureobacterium isolated from an alkaline environment , 1998, Journal of basic microbiology.

[18]  A. Zehnder,et al.  Enantioselective Uptake and Degradation of the Chiral Herbicide Dichlorprop [(RS)-2-(2,4-Dichlorophenoxy)propanoic acid] by Sphingomonas herbicidovorans MH , 1998, Journal of bacteriology.

[19]  W. Babel,et al.  Substrate inhibition under stationary growth conditions – nutristat experiments with Ralstonia eutropha JMP 134 during growth on phenol and 2,4-dichlorophenoxyacetate , 1997, Applied Microbiology and Biotechnology.

[20]  C. Nakatsu,et al.  Distribution of the tfdA Gene in Soil Bacteria That Do Not Degrade 2,4-Dichlorophenoxyacetic Acid (2,4-D) , 1997, Microbial Ecology.

[21]  W. Babel,et al.  The toxicity of substituted phenolic compounds to a detoxifying and an acetic acid bacterium. , 1997, Ecotoxicology and environmental safety.

[22]  W. Babel,et al.  Isolation of phenoxy herbicide‐degrading Rhodoferax species from contaminated building material , 1997 .

[23]  H. Kohler,et al.  Complete microbial degradation of both enantiomers of the chiral herbicide mecoprop [(RS)-2-(4-chloro-2-methylphenoxy)propionic acid] in an enantioselective manner by Sphingomonas herbicidovorans sp. nov , 1996, Applied and environmental microbiology.

[24]  T. Vallaeys,et al.  The metabolic pathway of 2,4‐dichlorophenoxyacetic acid degradation involves different families of tfdA and tfdB genes according to PCR‐RFLP analysis , 1996 .

[25]  W. Babel,et al.  Rapid extraction of (di) nucleotides from bacterial cells and determination by ion-pair reversed-phase HPLC , 1996 .

[26]  W. Babel,et al.  Isolation and characterization of an alkaliphilic bacterium capable of growing on 2,4‐dichlorophenoxyacetic acid and 4‐chloro‐2‐methylphenoxyacetic acid , 1996 .

[27]  R. Hausinger,et al.  Alcaligenes eutrophus JMP134 "2,4-dichlorophenoxyacetate monooxygenase" is an alpha-ketoglutarate-dependent dioxygenase , 1993, Journal of bacteriology.

[28]  A. Kahru,et al.  Role of adenine nucleotides in the regulation of bacterial energy metabolism: theoretical problems and experimental pitfalls. , 1990, Microbios.

[29]  J. K. Hurst,et al.  Viability and metabolic capability are maintained by Escherichia coli, Pseudomonas aeruginosa, and Streptococcus lactis at very low adenylate energy charge , 1988, Journal of bacteriology.

[30]  R. Seidler,et al.  Characterization of aquatic bacteria and cloning of genes specifying partial degradation of 2,4-dichlorophenoxyacetic acid , 1985, Applied and environmental microbiology.

[31]  W. Babel,et al.  pH‐linked control of energy charge in Acetobacter methanolicus sp. MB 70 , 1985 .