Identification of the flavin monooxygenase responsible for ipso substitution of alkyl and alkoxyphenols in Sphingomonas sp. TTNP3 and Sphingobium xenophagum Bayram.

We previously showed that opdA from Sphingomonas sp. PWE1 encodes a putative flavin monooxygenase capable of transforming octylphenol (OP) via type II ipso substitution. Here, we demonstrate that an opdA homolog is responsible for OP and related alkyl/alkoxyphenol degradation in the nonylphenol degrader Sphingomonas sp. TTNP3. PCR and Southern blot analyses revealed that TTNP3 contained an opdA homolog, while a TTNP3 derivative unable to grow on nonylphenol (TTNP3d) did not. OpdA expression was confirmed in wild-type TTNP3 via two dimensional gel electrophoresis. Activity was restored to TTNP3d following complementation with opdA. Sequence analysis of an opdA homolog from another nonylphenol degrader, Sphingobium xenophagum Bayram, revealed that the predicted protein sequences from PWE1 and Bayram were identical, but differed from TTNP3 by four amino acids. In order to assess differences, we heterologously expressed the two unique opdA homologs and compared their effect on the disappearance of five alkyl/alkoxyphenol substrates and subsequent appearance of hydroquinone. For all substrates, except OP, the levels of substrate disappearance and hydroquinone appearance were significantly lower in cultures expressing odpA (TTNP3) than those expressing opdA (PWE1/Bayram). These differences in substrate specificity were consistent with an in silico model which predicted that two of the amino acid differences between odpA (TTNP3) and opdA (PWE1/Bayram) lay in a putative substrate binding pocket. While these strains are known to use the same type II ipso substitution mechanism for alkylphenol degradation, this work provides the first preliminary evidence that opdA homologs also encode the type I ipso substitution activity responsible for the degradation of alkoxyphenols.

Identification of opdA, a gene involved in biodegradation of the endocrine disrupter octylphenol.

Octylphenol (OP) is an estrogenic detergent breakdown product. Structurally similar nonylphenols are transformed via type II ispo substitution, resulting in the production of hydroquinone and removal of the branched side chain. Nothing is known, however, about the gene(s) encoding this activity. We report here on our efforts to clone the gene(s) encoding OP degradation activity from Sphingomonas sp. strain PWE1, which we isolated for its ability to grow on OP. A fosmid library of PWE1 DNA yielded a single clone, aew4H12, which accumulated a brown polymerization product in the presence of OP. Sequence analysis of loss-of-function transposon mutants of aew4H12 revealed a single open reading frame, opdA, that conferred OP degradation activity. Escherichia coli subclones expressing opdA caused OP disappearance, with the concomitant production of hydroquinone and 2,4,4-trimethyl-1-pentene as well as small amounts of 2,4,4-trimethyl-2-pentanol. These metabolites are consistent with a type II ipso substitution reaction, the same mechanism described for nonylphenol biodegradation in other sphingomonads. Based on opdA's sequence homology to a unique group of putative flavin monooxygenases and the recovery of hydroxylated OP intermediates from E. coli expressing opdA, we conclude that this gene encodes the observed type II ipso substitution activity responsible for the initial step in OP biodegradation.

Natural selection for 2,4,5-trichlorophenoxyacetic acid mineralizing bacteria in agent orange contaminated soil.

Agent Orange contaminated soils were utilized in direct enrichment culture studies to isolate 2,4,5-trichlorophenoxyacetic acid (2,4,5-T) and 2,4-dichlorophenoxyacetic acid (2,4-D) mineralizing bacteria. Two bacterial cultures able to grow at the expense of 2,4,5-T and/or 2,4-D were isolated. The 2,4,5-T degrading culture was a mixed culture containing two bacteria, Burkholderia species strain JR7B2 and Burkholderia species strain JR7B3. JR7B3 was able to metabolize 2,4,5-T as the sole source of carbon and energy, and demonstrated the ability to affect metabolism of 2,4-D to a lesser degree. Strain JR7B3 was able to mineralize 2,4,5-T in pure culture and utilized 2,4,5-T in the presence of 0.01% yeast extract. Subsequent characterization of the 2,4-D degrading culture showed that one bacterium, Burkholderia species strain JRB1, was able to utilize 2,4-D as a sole carbon and energy source in pure culture. Polymerase chain reaction (PCR) experiments utilizing known genetic sequences from other 2,4-D and 2,4,5-T degrading bacteria demonstrated that these organisms contain gene sequences similar to tfdA, B, C, E, and R (Strain JRB1) and the tftA, C, and E genes (Strain JR7B3). Expression analysis confirmed that tftA, C, and E and tfdA, B, and C were transcribed during 2,4,5-T and 2,4-D dependent growth, respectively. The results indicate a strong selective pressure for 2,4,5-T utilizing strains under field condition.

Cometabolism of 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene by Pseudomonas acidovorans M3GY grown on biphenyl.

1,1-Dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE), a toxic breakdown product of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT), has traditionally been viewed as a dead-end metabolite: there are no published reports detailing enzymatic ring fission of DDE by bacteria in either soil or pure culture. In this study, we investigated the ability of Pseudomonas acidovorans M3GY to transform DDE and its unchlorinated analog, 1,1-diphenylethylene (DPE). While strain M3GY could grow on DPE, cells grown on DPE as a sole carbon source could not degrade DDE. Cells grown on biphenyl, however, did degrade DDE. Mass balance analysis of [14C]DDE showed transformation of more than 40% of the recoverable radioactivity. Nine chlorinated metabolites produced from DDE were identified by gas chromatography-mass spectrometry-Fourier-transform infrared spectrometry (GC-MS-FTIR) from cultures grown on biphenyl. Recovery of these metabolites demonstrates that biphenyl-grown cells degrade DDE through a meta-fission pathway. This study provides a possible model for biodegradation of DDE in soil by biphenyl-utilizing bacteria.

Affective symptoms in women attending a menopause clinic.

All new attenders at the Menopause Clinic in Edinburgh over six months were interviewed to detect current depressive disorder (MADRS) and past psychiatric disorders (SADS-L), to find out whether women who were depressed at the time of clinic attendance had a history of depression. Of the 95 subjects who entered the study, 78 had gone through a natural menopause and 17 had undergone hysterectomy with or without oophorectomy. Of the 78 who had experienced a natural menopause, 35 were found to be depressed at the time of clinic attendance and 43 were not. A strong association was found between current and past depressive illness, 29 of the patients depressed at the time of clinic attendance having had depression previously. However, a clear peak of illness was seen in the perimenopausal period (four years either side of the last menstrual period): 35% of all patients with past or current depressive illness experienced their first episode of illness in this period.

Growth of a bacterial consortium on triclosan.

Triclosan is a polychlorinated hydroxy diphenylether that has been widely used as an antimicrobial compound. An enrichment using triclosan as a sole source of carbon and energy yielded a consortium of bacteria capable of growing on this compound. The dichloro ring was partially mineralized, resulting in the conversion of approximately 35% of the [(14)C]triclosan to [(14)C]CO(2). Use of molecular fingerprinting techniques and 16S rDNA cloning and sequencing aided in the identification and eventual isolation of an auxotrophic Sphingomonas-like organism, strain Rd1, which was able to partially mineralize triclosan when grown on complex media.

The binary treatment of aqueous metribuzin using anodic fenton treatment and biodegradation.

An advanced oxidation process, anodic Fenton treatment (AFT), and a mixed microbial culture were used to degrade metribuzin [4-amino-6-tert-butyl-3-methylthio-1,2,4- triazin-5(4H)-one], a broad-use triazinone herbicide. Complete and rapid removal of metribuzin was demonstrated. The appearance and subsequent degradation of metribuzin oxidation products--deaminated metribuzin (DA), diketo metribuzin (DK), as well as the production of deaminated diketo metribuzin (DADK)--were observed. To support the use of AFT as a chemical pretreatment, the ratio of 5-day biochemical oxygen demand (BOD5) as measured in the standard test to chemical oxygen demand (COD) was investigated, and an increase from 0.03, a nonbiodegradable solution, to 0.35, a biodegradable solution, was observed. This increase in biodegradability was associated with decreased metribuzin, DA, and DK concentrations and increased DADK concentration. AFT effluent was inoculated with either an enriched microbial culture or Polyseed, a commercially available inoculum. Although there was minimal biodegradation of the remaining metribuzin, there was a significant decrease in DA concentration in inoculated incubations compared with sterile controls after 5- and 10-minute AFT treatment. The enrichment inoculate appeared more adapted toward the less-oxidized, 5-minute-treated effluent, whereas the Polyseed culture, developed to degrade complex waste solutions, appeared to be more effective in a moreoxidized, 10-minute-treated, and potentially more complex effluent. This research supports the continued investigation of AFT and biodegradation as a binary treatment of aqueous pesticide wastes.

The physiological and genetic diversity of bovine Streptococcus bovis strains(1).

Laboratory Streptococcus bovis strains and isolates obtained from a steer fed increasing amounts of grain had similar growth characteristics, but they differed in their sensitivity to 2-deoxyglucose (2DG), a non-metabolizable glucose analog. The addition of 2DG decreased both growth rate (0.92+/-0.34 h(-1)) and growth yield (ranging from 25 to 63%), but these differences could not be correlated with diet. However, isolates from a steer fed a 90% grain diet were more prone to 2DG-dependent lysis than those from a hay diet (P<0.001). All S. bovis laboratory strains and isolates had an identical restriction fragment length polymorphism pattern, when their 16S rDNA was digested with HaeIII and HhaI. However, when genomic BOX elements were amplified, 5-12 bands were observed, and the S. bovis isolates and laboratory strains could be grouped into 13 different BOX types. Strains 26 and 581AXY2 had the same BOX type, but the remaining laboratory strains did not form closely related clusters. Strains JB1 and K27FF4 were most closely related to each other. Most of the fresh isolates (24 out of 30) could be grouped into a single cluster (>90% Dice similarity). This cluster contained isolates from all three diets, but it did not have any of the laboratory strains. The majority (90%) of the isolates obtained from the hay-fed steer exhibited the same BOX type. Because more BOX types were observed if grain was added to the diet, it appears that ruminal S. bovis diversity may be a diet-dependent phenomenon.

A bioluminescent whole-cell reporter for detection of 2, 4-dichlorophenoxyacetic acid and 2,4-dichlorophenol in soil.

A bioreporter was made containing a tfdRP(DII)-luxCDABE fusion in a modified mini-Tn5 construct. When it was introduced into the chromosome of Ralstonia eutropha JMP134, the resulting strain, JMP134-32, produced a sensitive bioluminescent response to 2, 4-dichlorophenoxyacetic acid (2,4-D) at concentrations of 2.0 microM to 5.0 mM. This response was linear (R(2) = 0.9825) in the range of 2.0 microM to 1.1 x 10(2) microM. Saturation occurred at higher concentrations, with maximal bioluminescence occurring in the presence of approximately 1.2 mM 2,4-D. A sensitive response was also recorded in the presence of 2,4-dichlorophenol at concentrations below 1.1 x 10(2) microM; however, only a limited bioluminescent response was recorded in the presence of 3-chlorobenzoic acid at concentrations below 1.0 mM. A significant bioluminescent response was also recorded when strain JMP134-32 was incubated with soils containing aged 2,4-D residues.