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NTP Toxicology and Carcinogenesis Studies of Xylenes (Mixed) (60% m-Xylene, 14% p-Xylene, 9% o-Xylene, and 17% Ethylbenzene) (CAS No. 1330-20-7) in F344/N Rats and B6C3F1 Mice (Gavage Studies).

The technical grade of xylenes (mixed) (hereafter termed xylenes) contains the three isomeric forms and ethylbenzene (percentage composition shown above). The annual production for 1985 was approximately 7.4 x 108 gallons. Xylenes is used as a solvent and a cleaning agent and as a degreaser and is a constituent of aviation and automobile fuels. Xylenes is also used in the production of benzoic acid, phthalate anhydride, and isophthalic and terephthalic acids as well as their dimethyl esters. Toxicology and carcinogenesis studies of xylenes were conducted in laboratory animals because a large number of workers are exposed and because the long- term effects of exposure to xylenes were not known. Exposure for the present studies was by gavage in corn oil. In single-administration studies, groups of five F344/N rats and B6C3F1 mice of each sex received 500, 1,000, 2,000, 4,000, or 6,000 mg/kg. Administration of xylenes caused deaths at 6,000 mg/kg in rats and mice of each sex and at 4,000 mg/kg in male rats. In rats, clinical signs observed within 24 hours of dosing at 4,000 mg/kg included prostration, muscular incoordination, and loss of hind limb movement; these effects continued through the second week of observation. Tremors, prone position, and slowed breathing were recorded for mice on day 3, but all mice appeared normal by the end of the 2- week observation period. In 14- day studies, groups of five rats of each sex were administered 0, 125, 250, 500, 1,000, or 2,000 mg/kg, and groups of five mice of each sex received 0, 250, 500, 1,000, 2,000, or 4,000 mg/kg. Chemical- related mortality occurred only at 2,000 mg/kg in rats and at 4,000 mg/kg in mice. Rats and mice exhibited shallow breathing and prostration within 48 hours following dosing at 2,000 mg/kg. These signs persisted until day 12 for rats, but no clinical signs were noted during the second week for mice. In 13- week studies, groups of 10 rats of each sex received 0, 62.5, 125, 250, 500, or 1,000 mg/kg, and groups of 10 mice of each sex received 0, 125, 250, 500, 1,000, or 2,000 mg/kg. No deaths or clinical signs of toxicity were recorded in rats. However, high dose male rats gained 15% less weight and females 8% less weight than did the vehicle controls. Two female mice died at the 2,000 mg/kg dose. Lethargy, short and shallow breathing, unsteadiness, tremors, and paresis were observed for both sexes in the 2,000 mg/kg group within 5- 10 minutes after dosing and lasted for 15- 60 minutes. Two- year toxicology and carcinogenesis studies were conducted by administering 0, 250, or 500 mg/kg xylenes in corn oil by gavage to groups of 50 F344/N rats of each sex, 5 days per week for 103 weeks. Groups of 50 B6C3F1 mice of each sex were administered 0, 500, or 1,000 mg/kg xylenes on the same schedule. Although the mortality was dose related in male rats (final survival: vehicle control, 36/50; low dose, 26/50; high dose, 20/50), many of the early deaths in the dosed males were gavage related. Body weights of the high dose male rats were 5%- 8% lower than those of the vehicle controls after week 59. The mean body weights of low dose and vehicle control male rats and those of dosed and vehicle control female rats were comparable. Survival rates of female rats and both sexes of dosed mice were not significantly different from those of the vehicle controls. The mean weights of dosed male and female mice were comparable to those of the vehicle controls. Hyperactivity lasting 5- 30 minutes was observed in high dose mice after dosing, beginning after week 4 and continuing through week 103. At no site was the incidence of nonneoplastic or neoplastic lesions in dosed rats or mice of either sex considered to be related to the administration of xylenes. Neither xylenes nor any of its components (o- xylene, m-xylene, p- xylene, or ethylbenzene) were mutagenic when tested with or without metabolic activation in Salmonella typhimurium strains TA100, TA1535, TA97, or TA98 with the preincubation protocol. In addition, ethylbenzene was tested in cytogenetic assays using cultured Cetic assays using cultured Chinese hamster ovary cells both with and without metabolic activation; neither sister- chromatid exchanges nor chromosomal aberrations were induced by ethylbenzene. An audit of the experimental data was conducted for the 2-year studies of xylenes. No data discrepancies were found that influenced the final interpretations. Under the conditions of these 2-year gavage studies, there was no evidence of carcinogenicity of xylenes (mixed) for male or female F344/N rats given 250 or 500 mg/kg or for male or female B6C3F1 mice given 500 or 1,000 mg/kg.

Journal Article↗

Metabolism of antipyrine and m-xylene in rats after prolonged pretreatment with xylene alone or xylene with ethanol, phenobarbital or 3-methylcholanthrene.

1. The metabolic disposition of antipyrine (AP) and m-xylene (XYL) has been studied in rats pretreated for a prolonged period with XYL, dosed alone or in combination with ethanol, phenobarbital (PB), or 3-methylcholanthrene (MC). 2. XYL inhalation exposure at 300 ppm in air (7 h/day, 4 days/week, for 1 or 4 weeks) did not alter the total 24-h recovery of AP and its major metabolites in urine, but the excretion profile changed compared with controls: 3-hydroxymethylantipyrine (3-HMA) increased (less than or equal to 14%, P less than 0.001), norantipyrine (NORA) (less than or equal to 23%, P less than 0.01) and AP (less than or equal to 53%, P less than 0.01) decreased. 4-Hydroxyantipyrine (4-OHA) was unchanged. 3. Oral dosage of XYL at 800 mg/kg per day (5 days/week, for 12 days) altered the metabolic disposition of AP similarly to inhalation. 4. XYL + ethanol did not alter the xylene-type effect on AP metabolism. This was at variance with the changes following XYL + PB and, to a greater extent, XYL + MC pretreatments: 4-OHA increased (53-74%, P less than 0.01), 3-HMA (11-42%, P less than 0.05) and AP (greater than or equal to 50%, P less than 0.05) decreased. The effect on NORA was less clear. 5. XYL pretreatment accelerated metabolic disposition of its major urinary metabolite, methylhippuric acid (MHA) and formation of thioethers. 6. Thioether excretion in 24 h urine was enhanced about 10-fold after XYL inhalation and 20-fold after oral administration. Only XYL + PB treatment enhanced further the excretion of xylene-derived thioethers (P less than 0.05). 7. Drug-metabolizing activity (phase I and II reactions) in liver, lung and kidney showed that the treatments resulted in marked and differential biochemical alterations. 8. In conclusion, m-xylene enhanced the rate of its own metabolism and induced differential changes on urinary AP metabolite profile depending on the pretreatment.

Administration, Inhalation↗

Possible preferential metabolism of xylene isomers following occupational exposure to mixed xylenes.

OBJECTIVES: Solvent exposures commonly involve mixtures of substances or mixtures of isomers of a single solvent. These may be metabolised through common pathways, resulting in the potential for metabolic interactions. These may then lead to accumulation of solvent or metabolic intermediates, some of which may be toxic. This paper describes a pilot study conducted to determine the correlation between airborne xylene isomers and the appearance of methylhippuric acid (MHA) isomers in urine of workers exposed mainly to xylene. The project also aimed to determine whether there is preferential metabolism of any isomer by comparison of the ratios of airborne isomers with the ratios of metabolite isomers appearing in urine. SUBJECTS AND METHODS: A total of 12 workers (11 male, 1 female) were recruited into this study, with 2 of the participants providing samples on more than one occasion. Workers included flooring contractors (5), printers (2), chemical manufacturers (2), histology technicians (2) and one householder using a xylene-based varnish. Subjects were aged between 24 and 48 years (37.6+/-2.0 years; mean +/- SEM). After giving informed consent, workers provided a prework and postwork urine sample on a midweek work day. Samples were stored frozen prior to analysis. Breathing-zone air samples were collected using personal air samplers at 50 ml/min. Solvents were trapped on activated-charcoal sampling tubes. Subjects wore pumps for 18-304 (178+/-24) min on the same day on which urine samples were collected. RESULTS: Xylene exposures ranged from 1.6 to over 7000 ppm. In all, 7 of 16 measurements exceeded the Australian TWA standard of 80 ppm. Two of the flooring contractors wore respiratory protective equipment (RPE) and the two histopathology technicians used workplace ventilation systems. Total urinary MHA output ranged from 10 to 8000 mmol/mol creatinine, with 6 of 16 samples exceeding the modified biological exposure index of 702 mmol/mol. Correlations between airborne concentrations of individual xylene isomers and their corresponding MHA isomers were poor but improved when workers using RPE were excluded from the analysis. Gradients of the regression lines (millimoles of MHA per mole of creatinine per parts per million of xylene) were 3.2 for o-isomers, 7.0 for p-isomers, and 14.4 for m-isomers. Comparisons of isomer ratios of xylene in air were made with the corresponding ratio of MHA isomers in urine. These revealed higher ratios of m-MHA to other MHA isomers than those of m-xylene to the other xylene isomers. The MHA isomer ratios were expected to be the same as the airborne xylene isomer ratios if there were no preferential elimination of any isomer. m-MHA appeared in urine in a greater proportion than would be predicted from the proportion of m-xylene detected in air. The time course of the appearance of MHA isomers in urine also suggests that interactions were taking place, with m-MHA appearing in high proportion in urine following several days of repeated heavy xylene exposure. On a single moderate exposure, m-MHA appeared initially in high proportion in the first few hours but was undetectable in urine after 18 h. p-MHA was detectable for up to 6 h after exposure, and o-MHA remained detectable after 18 h. CONCLUSIONS: This study suggests that excretion of m-MHA in urine is favoured over that of the other isomers following exposure to mixed xylenes. This is independent of airborne xylene isomer composition and suggests that the metabolism of m-xylene occurs preferentially to that of the other isomers. It is not clear at which step in the metabolism of xylene this preference occurs, although other work indicates that the initial oxidation of xylene to methylbenzyl alcohol by cytochrome P450 2E1 occurs at the same rate for each isomer. These findings suggest that there is potential for metabolic interactions between xylene isomers and that these may be the basis for xylene toxicity.

Adult↗

Importance of Debye and Keesom interactions in separating m-xylene and p-xylene in GC-MS analysis utilizing PEG stationary phase.

In electron impact gas chromatography (GC)-mass spectrometry analysis of a complex mixture, such as gasoline, two coeluting solutes can be distinguished if each has a unique major ion. The boiling-point difference between m-xylene and p-xylene, which also has identical major ions (mz-1: 91 and 106 Da), is 0.77 degrees C. These cannot be separated even on a crossed-linked polydimethylsiloxane capillary column, which has a minimum of 5000 plates/m. They are separated on a crossed-linked polar polyethylene glycol (PEG) capillary column. GC separation on a stationary phase depends on the relative strengths of solute-solute, stationary phase-stationary phase, and solute-stationary phase interactions. Although the calculated molar electronic polarization and refractivity factor of Lorenz-Lorentz equation for m-xylene and p-xylene are nearly equal because of its greater dipole moment difference (0.30 and 0.02), the calculated orientation polarization of m-xylene is 80 times greater than p-xylene. This implies the dipole reinforcement through inductive polarization by the hydroxyl of PEG stationary phase molecules is greater on m-xylene than p-xylene. In addition, as the permanent dipole moment of m-xylene is 15 times greater than p-xylene, m-xylene has a stronger Keesom interaction with PEG. In order for m-xylene and p-xylene to solvate in PEG, analytes must overcome the PEG-PEG Keesom/hydrogen bonding interaction forces. Physical and chemical parameters indicate that compared with p-xylene, m-xylene has a greater Debye-Keesom interaction tendency with PEG molecules. This is supported by the 0.12-min. retention-time difference between them.

Journal Article↗

Effects of xylene and xylene isomers on cytochrome P-450 and in vitro enzymatic activities in rat liver, kidney and lung.

Rats were exposed for 3 days by inhalation to 2000 ppm of a xylene mixture, or the individual constituents, o-xylene, m-xylene, p-xylene and ethylbenzene. All solvents increased hepatic cytochrome P-450 concentrations and NADPH-cytochrome c reductase activity, although p-xylene did not increase the cytochrome P-450 content as much as the other compounds, showing the importance of the substitution pattern. Increases were observed in the in vitro O-deethylation of 7-ethoxyresorufin and in the hydroxylation of n-hexane and benzo[a]pyrene. The metabolite profiles obtained with these substrates and the results of gel electrophoresis in the presence of sodium dodecyl sulfate indicate that the induction is of the phenobarbital type. In kidney microsomes an increased concentration of cytochrome P-450 was obtained following exposure to a xylene mixture or to o- or m-xylene. The O-deethylation of 7-ethoxyresorufin was increased by exposure to all solvents. In lung microsomes xylene and xylene isomers but not ethylbenzene caused a decrease in cytochrome P-450 content and a reduction in n-hexane hydroxylation. However, the O-deethylation of 7-ethoxyresorufin was not affected. In general the effect of the xylene mixture reflected the content of the dominating component m-xylene. The ability of xylene and xylene isomers to modify the metabolism of other potentially toxic substances in liver, kidney and lung microsomes suggests the possibility of synergistic toxic responses.

Animals↗

Developmental toxicities of ethylbenzene, ortho-, meta-, para-xylene and technical xylene in rats following inhalation exposure.

The developmental toxicities of ethylbenzene, o-, m-, p-xylene and technical xylene were studied in Sprague-Dawley rats after inhalation exposure. Animals were exposed to either of these agents at 100, 500, 1000 or 2000 ppm, for 6 h/day, during days 6-20 of gestation. All the agents tested caused maternal toxicity expressed as a reduction in maternal body weight gain at 1000 and 2000 ppm. Decreased corrected weight gain and food consumption were observed at 1000 and 2000 ppm ethylbenzene, o-, m- or p-xylene, and at 2000 ppm technical xylene. No evidence of teratogenic effects was found after exposure to any of these agents up to 2000 ppm. Fetal toxicity evidenced by significant decreases in fetal body weights occurred at concentrations of 500 ppm or greater of o-xylene or technical xylene, and 1000 ppm or greater of ethylbenzene, m- or p-xylene. A significant increase in the mean percentage of fetuses per litter with skeletal variations was also noted at 2000 ppm ethylbenzene, o- and p-xylene. In summary, all tested agents produced developmental toxicity at 1000 and 2000 ppm, concentrations that also produced significant maternal toxicity. With o-xylene and technical xylene, developmental toxicity also occurred at 500 ppm, in the absence of maternal toxic effects. However, the only indication of a treatment-related effect was a slight decrease in fetal weight.

Administration, Inhalation↗

Excretion of methylhippuric acids in urine of workers exposed to a xylene mixture: comparison among three xylene isomers and toluene.

The correlation between exposure to three xylene isomers and resulting urinary excretion of corresponding methylhippuric acid (MHA) isomers was studied among 175 Chinese workers of both sexes who had been predominantly exposed to xylenes (exposure to xylenes accounting for 70% or more of the total exposure on a ppm basis). Nonexposed controls (281 men and women) were also studied to define the background level of MHAs in urine. The solvent exposure of xylene-exposed workers during their workshift was monitored by diffusive sampling of breathing zone air, and MHAs in shift-end urine were determined by high-performance liquid chromatography. Regression analysis showed that the concentration of each MHA isomer correlated significantly with the time-weighted average intensity of exposure to the corresponding xylene isomer, and therefore the correlation between the sum of three xylene isomers in air and that of three MHA isomers in urine was also significant; the slope of the regression line was essentially the same among the three isomers. The calculated regression line suggested that the urinary MHA level after hypothetical exposure to xylenes at 100 ppm will be somewhat less than the proposed biological exposure index and biological tolerance value. Two social habits of smoking and drinking in combination suppressed the conversion of xylenes to MHAs in male workers.

Adult↗

Identification and characterization of o-xylene-degrading Rhodococcus spp. which were dominant species in the remediation of o-xylene-contaminated soils.

Soils contaminated with o-xylene were more difficult to bioremediate than those contaminated with other BTEX hydrocarbons (benzene, toluene, ethylbenzene, m-xylene and p-xylene). In order to identify microorganisms responsible for o-xylene degradation in soil, microbial community structure analyses were carried out with two soil samples in the presence of o-xylene and mineral nutrients. In two different soil samples, Rhodococcus opacus became abundant. We were also able to isolate o-xylene degrading Rhodococcus species from these soil samples. A primer set was developed to specifically detect a cluster of this Rhodococcus group including isolated Rhodococcus strains, Rhodococcus opacus and Rhodococcus koreensis. The growth of this bacterial group in an o-xylene-contaminated soil was followed by competitive PCR (cPCR). The decrease in o-xylene clearly paralleled the growth of the Rhodococcus group.

Base Sequence↗

Degradation of toluene and m-xylene and transformation of o-xylene by denitrifying enrichment cultures.

Seven different sources of inocula that included sediments, contaminated soils, groundwater, process effluent, and sludge were used to establish enrichment cultures of denitrifying bacteria on benzene, toluene, and xylenes in the absence of molecular oxygen. All of the enrichment cultures demonstrated complete depletion of toluene and partial depletion of o-xylene within 3 months of incubation. The depletion of o-xylene was correlated to and dependent on the metabolism of toluene. No losses of benzene, p-xylene, or m-xylene were observed in these initial enrichment cultures. However, m-xylene was degraded by a subculture that was incubated on m-xylene alone. Complete carbon, nitrogen, and electron balances were determined for the degradation of toluene and m-xylene. These balances showed that these compounds were mineralized with greater than 50% conversion to CO2 and significant assimilation into biomass. Additionally, the oxidation of these compounds was shown to be dependent on nitrate reduction and denitrification. These microbial degradative capabilities appear to be widespread, since the widely varied inoculum sources all yielded similar results.

Bacteria, Anaerobic↗

Degradation of o-xylene and m-xylene by a novel sulfate-reducer belonging to the genus Desulfotomaculum.

A strictly anaerobic bacterium, strain OX39, was isolated with o-xylene as organic substrate and sulfate as electron acceptor from an aquifer at a former gasworks plant contaminated with aromatic hydrocarbons. Apart from o-xylene, strain OX39 grew on m-xylene and toluene and all three substrates were oxidized completely to CO(2). Induction experiments indicated that o-xylene, m-xylene, and toluene degradation were initiated by different specific enzymes. Methylbenzylsuccinate was identified in supernatants of cultures grown on o-xylene and m-xylene, and benzylsuccinate was detected in supernatants of toluene-grown cells, thus indicating that degradation was initiated in all three cases by fumarate addition to the methyl group. Strain OX39 was sensitive towards sulfide and depended on Fe(II) in the medium as a scavenger of the produced sulfide. Analysis of the PCR-amplified 16S rRNA gene revealed that strain OX39 affiliates with the gram-positive endospore-forming sulfate reducers of the genus Desulfotomaculum and is the first hydrocarbon-oxidizing bacterium in this genus.

Anaerobiosis↗

New approaches to the metabolism of xylenes: verification of the formation of phenylmercapturic acid metabolites of xylenes.

It was the aim of this study to ascertain whether xylenes form phenylmercapturic acids via aromatic epoxides in the human metabolism. Aromatic epoxides are suspected to exert mutagenic properties. Therefore we developed an LC/MS/MS procedure for the determination of these mercapturic acids. Using this method we were able to detect dimethylphenylmercapturic acid (DPMA) in urine samples of persons occupationally exposed to xylenes. The unequivocal LC/MS/MS detection of phenylmercapturic acid metabolites of xylene thanks to authentic standards was verified with an independent GC/MS method. Xylene concentrations in the air of the workplaces ranged between 0.7 and 58.1 ppm (median 12.6 ppm). The excretion of methylhippuric acid in the urine samples of the workers (n=27) ranges from 19.8 to 2332.5 mg/l (median 450.9 mg/l). DPMA was detected in only 9 samples of 27 exposed persons. According to a rough calculation DPMA is only formed in a ratio of 0.0003% respective to the xylene main metabolite MHA. That means that even under occupationally relevant xylene exposure potential mutagenic potencies should be negligible. DPMA in urine is not sensitive enough for general biomonitoring purposes due to the low ratio of excretion. MHA should therefore be used for biomonitoring from now on. Furthermore, our results show that irrespective of the structure of xylene isomers there is no preferences in metabolism.

Acetylcysteine↗

Biotransformation of p-xylene and 2,6-dimethylnaphthalene by xylene monooxygenase cloned from a Sphingomonas isolate.

Sphingomonas strain ASU1 was isolated from an industrial wastewater bioreactor and grew on 2,6-dimethylnaphthalene (2,6-DMN) as the sole carbon/energy source. The genes for a xylene monooxygenase were cloned from strain ASU1. Expression of the ASU1 xylene monooxygenase was compared to expression of the pWWO xylene monooxygenase in Escherichia coli. Both monooxygenases transformed p-xylene and 2,6-DMN by initially hydroxylating one methyl group. In addition, the ASU1 monooxygenase also hydroxylated the second methyl group on p-xylene and 2,6-DMN whereas the pWWO monooxygenase hydroxylated the second methyl group only on p-xylene. Endogenous E. coli enzymes contributed to further oxidation of the resulting aromatic alcohols to form aromatic carboxylates.

Chromosome Mapping↗

The effect of m-xylene on rat lung benzo[a]pyrene metabolism and microsomal membrane lipids: comparison with p-xylene.

m-Xylene (1 g/kg, i.p., 1 h) was shown to decrease aryl hydrocarbon hydroxylase (AHH) activity, a detoxification pathway for benzo[a]pyrene (BaP), in the rat lung. Inhibition was maximal at 1 g/kg, 1 h after treatment and was sustained for at least 24 h. Reduction in cytochrome P-450 activity in rat lung was also observed, while liver activity was unchanged. p-Xylene has been previously shown to produce a similar pattern of MFO changes in rat lung. The lipid composition of the microsomal membrane is important to mixed function oxidase (MFO) regulation and function. Since the xylenes are lipophilic, these compounds were studied to determine whether they alter pulmonary microsomal lipids. p-Xylene produced an organ specific increase in lipid peroxidation in the rat lung. This was accompanied by decreases in lung microsomal total phospholipid (PL) and phosphatidylcholine (PC) content. Pulmonary microsomal membrane fluidity was also reduced by p-xylene administration. In comparison, m-xylene administration did not change any of the lipid membrane parameters tested. These divergent results leave unresolved the role of altered PL metabolism in solvent-induced inhibition of MFO activity.

Animals↗

Anaerobic oxidation of o-xylene, m-xylene, and homologous alkylbenzenes by new types of sulfate-reducing bacteria.

Various alkylbenzenes were depleted during growth of an anaerobic, sulfate-reducing enrichment culture with crude oil as the only source of organic substrates. From this culture, two new types of mesophilic, rod-shaped sulfate-reducing bacteria, strains oXyS1 and mXyS1, were isolated with o-xylene and m-xylene, respectively, as organic substrates. Sequence analyses of 16S rRNA genes revealed that the isolates affiliated with known completely oxidizing sulfate-reducing bacteria of the delta subclass of the class Proteobacteria. Strain oXyS1 showed the highest similarities to Desulfobacterium cetonicum and Desulfosarcina variabilis (similarity values, 98.4 and 98.7%, respectively). Strain mXyS1 was less closely related to known species, the closest relative being Desulfococcus multivorans (similarity value, 86.9%). Complete mineralization of o-xylene and m-xylene was demonstrated in quantitative growth experiments. Strain oXyS1 was able to utilize toluene, o-ethyltoluene, benzoate, and o-methylbenzoate in addition to o-xylene. Strain mXyS1 oxidized toluene, m-ethyltoluene, m-isoproyltoluene, benzoate, and m-methylbenzoate in addition to m-xylene. Strain oXyS1 did not utilize m-alkyltoluenes, whereas strain mXyS1 did not utilize o-alkyltoluenes. Like the enrichment culture, both isolates grew anaerobically on crude oil with concomitant reduction of sulfate to sulfide.

Alkylation↗

The toxic effects of combined exposure to toluene and m-xylene in animals. II. Blood toluene and m-xylene during single and combined exposure in rats.

The influence of combined exposure to m-xylene and toluene vapours at a concentration of 100 + 100 ppm on blood m-xylene concentration in rats was investigated. Within 6-7 hours of coexposure to m-xylene and toluene a significant increase in blood m-xylene concentration, in comparison to single exposure to m-xylene at concentration of 100 ppm, was observed. Study results may suggest that, reported earlier, the more than additive toxic effects of combined exposure to m-xylene and toluene in animals may result from its metabolic interaction.

Animals↗

Effect of preadsorbed water on the adsorption of p-xylene and m-xylene mixtures on BaX and BaY zeolites.

Adsorption of an equimolar p-xylene/m-xylene mixture on partially hydrated barium-exchanged X and Y zeolites is studied at 423 K in the pressure range 10(-2)-8 hPa by differential calorimetry coupled with manometry and chromatography. Results are consistent with structural studies and Monte Carlo simulations of the literature. The presence of preadsorbed water in supercages increases the adsorption selectivity toward p-xylene to the detriment of the adsorption capacity and the adsorption affinity, as indicated by a sharp decrease of the Henry constants. However, the coadsorption heats at zero filling are not influenced by the presence of water. Therefore, entropic effects seem to play an important role in the coadsorption process. Two adsorption sites whose energy differs are identified by calorimetry. The more energetic site could correspond to the p-xylene or m-xylene molecule in interaction with the compensation cation located in sites II in the supercage, the less energetic to the adsorption of p-xylene molecule in the 12-ring window joining two supercages. The presence of this second site for p-xylene could be at the origin of the selectivity.

Journal Article↗

Protein engineering of toluene-o-xylene monooxygenase from Pseudomonas stutzeri OX1 for enhanced chlorinated ethene degradation and o-xylene oxidation.

Toluene-o-xylene monooxygenase (ToMO) from Pseudomonas stutzeri OX1 has been shown to degrade all chlorinated ethenes individually and as mixtures. Here, DNA shuffling of the alpha hydroxylase fragment of ToMO (TouA) and saturation mutagenesis of the TouA active site residues I100, Q141, T201, F205, and E214 were used to enhance the degradation of chlorinated aliphatics. The ToMO mutants were identified using a chloride ion screen and then were further examined by gas chromatography. Escherichia coli TG1/pBS(Kan)ToMO expressing TouA saturation mutagenesis variant I100Q was identified that has 2.8-fold better trichloroethylene (TCE) degradation activity (apparent Vmax of 1.77 nmol min-1 mg-1 protein-1 vs 0.63 nmol min-1 mg-1 protein-1). Another variant, E214G/D312N/M399V, has 2.5-fold better cis-1,2-dichloroethylene (cis-DCE) degradation activity (apparent Vmax of 8.4 nmol min-1 mg-1 protein-1 vs 3.3 nmol min-1 mg-1 protein-1). Additionally, the hydroxylation regiospecificity of o-xylene and naphthalene were altered significantly for ToMO variants A107T/E214A, T201G, and T201S. Variant T201S produced 2.0-fold more 2,3-dimethylphenol (2,3-DMP) from o-xylene than the wild-type ToMO, whereas variant A107T/E214A had 6.0-fold altered regiospecificity for 2,3-DMP formation. Variant A107T/E214A also produced 3.0-fold more 2-naphthol from naphthalene than the wild-type ToMO, whereas the regiospecificity of variant T201S was altered to synthesize 3.0-fold less 2-naphthol, so that it made almost exclusively 1-naphthol (96%). Variant T201G was more regiospecific than variants A107T/E214A and T201S and produced 100% 3,4-DMP from o-xylene and >99% 1-naphthol from naphthalene. Hence, ToMO activity was enhanced for the degradation of TCE and cis-DCE and for the regiospecific hydroxylation of o-xylene and naphthalene through DNA shuffling and saturation mutagenesis.

Dichloroethylenes↗