Metabolism of Diethyl Ether and Cometabolism of Methyl tert-Butyl Ether by a Filamentous Fungus, a Graphium sp

In this study, evidence for two novel metabolic processes catalyzed by a filamentous fungus, Graphium sp. strain ATCC 58400, is presented. First, our results indicate that this Graphium sp. can utilize the widely used solvent diethyl ether (DEE) as the sole source of carbon and energy for growth. The kinetics of biomass accumulation and DEE consumption closely followed each other, and the molar growth yield on DEE was indistinguishable from that with n-butane. n-Butane-grown mycelia also immediately oxidized DEE without the extracellular accumulation of organic oxidation products. This suggests a common pathway for the oxidation of both compounds. Acetylene, ethylene, and other unsaturated gaseous hydrocarbons completely inhibited the growth of this Graphium sp. on DEE and DEE oxidation by n-butane-grown mycelia. Second, our results indicate that gaseous n-alkane-grown Graphium mycelia can cometabolically degrade the gasoline oxygenate methyl tert-butyl ether (MTBE). The degradation of MTBE was also completely inhibited by acetylene, ethylene, and other unsaturated hydrocarbons and was strongly influenced by n-butane. Two products of MTBE degradation, tert-butyl formate (TBF) and tert-butyl alcohol (TBA), were detected. The kinetics of product formation suggest that TBF production temporally precedes TBA accumulation and that TBF is hydrolyzed both biotically and abiotically to yield TBA. Extracellular accumulation of TBA accounted for only a maximum of 25% of the total MTBE consumed. Our results suggest that both DEE oxidation and MTBE oxidation are initiated by cytochrome P-450-catalyzed reactions which lead to scission of the ether bonds in these compounds. Our findings also suggest a potential role for gaseous n-alkane-oxidizing fungi in the remediation of MTBE contamination.     

Thermodynamics and Kinetics of MTBE Degradation: A Density Functional Theory Study

Computational studies using density functional theory can help define which of a variety of reactions may be involved in the degradation of the fuel oxygenate methyl tert-butyl ether (MTBE). It is shown that hydrolysis of MTBE in the vapor phase or in neutral aqueous media, as well as its unimolecular decomposition, are not significant degradation mechanisms. The acid catalyzed hydrolysis of MTBE is a more feasible degradation pathway and is shown to proceed via tert-butyl carbonium ion formation. Hydrogen abstraction is shown to be the dominant first step in the degradation of MTBE initiated by hydroxyl radicals.     

Degradation of alkyl ethers, aralkyl ethers, and dibenzyl ether by Rhodococcus sp. strain DEE5151, isolated from diethyl ether-containing enrichment cultures

Twenty strains isolated from sewage sludge were found to degrade various ethers, including alkyl ethers, aralkyl ethers, and dibenzyl ether. In Rhodococcus strain DEE5151, induction of ether degradation needed substrates exhibiting at least one unsubstituted Calpha-methylene moiety as the main structural prerequisite. The cleavage reaction observed with anisole, phenetole, and dibenzyl ether indicates that the initial oxidation occurs at such respective Calpha positions. Diethyl ether-induced strain DEE5151 degraded dibenzyl ether via intermediately accumulated benzoic acid. Phenetole seems to be subject also to another ether-cleaving enzyme. Other strains of this group showed different enzymatic activities towards the substrate classes investigated.     

Mineralization of methyl tert-butyl ether and other gasoline oxygenates by Pseudomonads using short n-alkanes as growth source

Biodegradation of methyl tert-butyl ether (MTBE) by cometabolism has shown to produce recalcitrant metabolic intermediates that often accumulate. In this work, a consortium containing Pseudomonads was studied for its ability to fully degrade oxygenates by cometabolism. This consortium mineralized MTBE and TBA with C3-C7 n-alkanes. The highest degradation rates for MTBE (75 +/- 5 mg g(protein) (-1) h(-1)) and TBA (86.9 +/- 7.3 mg g(protein) (-1) h(-1)) were obtained with n-pentane and n-propane, respectively. When incubated with radiolabeled MTBE and n-pentane, it converted more than 96% of the added MTBE to (14)C-CO(2). Furthermore, the consortium degraded tert-amyl methyl ether, tert-butyl alcohol (TBA), tert-amyl alcohol, ethyl tert-butyl ether (ETBE) when n-pentane was used as growth source. Three Pseudomonads were isolated but only two showed independent MTBE degradation activity. The maximum degradation rates were 101 and 182 mg g(protein) (-1) h(-1) for Pseudomonas aeruginosa and Pseudomonas citronellolis, respectively. The highest specific affinity (a degrees (MTBE)) value of 4.39 l g(protein) (-1) h(-1) was obtained for Pseudomonas aeruginosa and complete mineralization was attained with a MTBE: n-pentane ratio (w/w) of 0.7. This is the first time that Pseudomonads have been reported to fully mineralize MTBE by cometabolic degradation.     

The Comparative and Combined Inhibitory Effects of MTBE and TBA on the Activities of Soil Exoenzymes

Methyl tert-butyl ether (MTBE) and tert-butyl alcohol (TBA) are major soil contaminants, and they have been actively investigated for their toxic effects on living organisms in soil ecosystems. Although previous studies have been used as tools to evaluate the health of soil, they have been limited in scope and ability to analyze the overall microbial activity. In the present study, the effects of MTBE and TBA on the activity of soil exoenzymes including urease, acid phosphatase, arylsulfatase, β-glucosidase, dehydrogenase, and fluorescein diacetate hydrolase, which are involved in nutrient cycles and overall microbial activities, were investigated. Soil samples were treated with 0–2% of MTBE and TBA solutions, and the comparative effects and combined effects on quantity of active soil exoenzymes were determined. The activity of six exoenzymes exposed solely to MTBE and TBA did not significantly change with dose concentration or exposure time, but did show significant changes when exposed to high concentrations of MTBE and TBA combined, with dehydrogenase being the most affected. Therefore, we proposed dehydrogenase as a potential biomarker to assess the risk of co-contamination of MTBE and TBA.     

Effects of environmental settings on MTBE removal for a mixed culture and its monoculture isolation

A mixed culture was utilized to evaluate methyl tert-butyl ether (MTBE) removal under various conditions and to isolate a MTBE-degrading pure culture. The results showed that high MTBE removal efficiencies can be reached even in the presence of other substrates. The biodegradation sequence of the target compounds by the mixed culture, in order of removal rate, was toluene, ethyl benzene, p-xylene, benzene, MTBE, ethyl ether, tert-amyl methyl ether, and ethyl tert-butyl ether. In addition, preincubation of the mixed cultures with benzene and toluene showed no negative effect on MTBE removal; on the contrary, it could even increase the degradation rate of MTBE. The kinetic behavior showed that the maximum specific growth rate and the saturation constant of the mixed culture degrading MTBE are 0.000778 h⁻¹ and 0.029 mg l⁻¹, respectively. However, a high MTBE concentration (60 mg l⁻¹) was slightly inhibiting to the growth of the mixed culture. The pure culture isolated from the enrichments in the bubble-air bioreactor showed better efficiency in MTBE removal than the mixed culture; whereas, tert-butyl alcohol was formed as a metabolic intermediate during the breakdown of MTBE.     

Effects of co-substrates and inhibitors on the anaerobic O-demethylation of methyl <Emphasis Type="Italic">tert</Emphasis>-butyl ether (MTBE)

Methyl tert-butyl ether (MTBE) contamination is widespread in aquifers near urban areas around the world. Since this synthetic fuel oxygenate is resistant to most physical methods of treating fuel-contaminated water, biodegradation may be a useful means of remediation. Currently, information on anaerobic MTBE degradation is scarce. Depletion has been observed in soil and sediment microcosms from a variety of locations and under several redox conditions, but the responsible organisms are unknown. We are studying anaerobic consortia, enriched from contaminated sediments for MTBE-utilizing microorganisms for over a decade. MTBE degradation occurred in the presence of other fuel components and was not affected by toluene, benzene, ethanol, methanol, or gasoline. Many aryl O-methyl ethers, such as syringic acid, that are O-demethylated by acetogenic bacteria, were also O-demethylated by the MTBE-utilizing enrichment cultures. The addition of these compounds as co-substrates increased the rate of MTBE degradation, offering a potentially useful method of stimulating the MTBE degradation rate in situ. Propyl iodide caused light-reversible inhibition of MTBE degradation, suggesting that the MTBE degradation process is corrinoid dependent. The anaerobic MTBE degradation process was not directly coupled to methanogenesis or sulfidogenesis and was inhibited by the bactericidal antibiotic, rifampicin. These results suggest that MTBE degradation is mediated by acetogenic bacteria.     

Candida Antarctica Lipase B-Catalysed Synthesis Of Dihydroxyacetone Fatty Acid Esters

The enzymatic syntheses of 1-lauroyl-dihydroxyacetone and 1, 3-dilauroyl-dihydroxyacetone were investigated. Lipase B from Candida Antarctica (SP435) was used to catalyse the acylation of dihydroxyacetone (DHA) with lauric acid in organic solvent media at controlled water activity. High conversions of dihydroxyacetone (< 90%) are achieved when the water activity is 0.11 or below in solvents of various hydrophobicities, such as diethyl ether, methyl-terr-butyl ether (MTBE) and diphenyl ether. The main product in the esterification of DHA with lauric acid is 1-lauroyl-DHA, while the amount of 1, 3-dilauroyl-DHA that is produced can be increased by changing the reaction conditions. Thus, hasing the water activity from 0.75 to 0.06 resulted in an increase in the total yield of 1, 3-dilauroyl-DHA from 3% to 20%. Solvents which have high logP values favoured the acylation of 1-lauroyl-DHA and thereby the formation of 1, 3-dilauroyl-DHA. Thus, when diphenyl ether was used in this reaction, the yield of 1, 3-dilauroyl-DHA was 45%. Complete acylation to 1, 3-dilauroyl-DHA was achieved when a fatty acid vinyl ester was used as acyl donor in a closed reactor.     

Inhibition of diethyl ether degradation in Rhodococcus sp. strain DEE5151 by glutaraldehyde and ethyl vinyl ether

Alkyl ether-degrading Rhodococcus sp. strain DEE5151, isolated from activated sewage sludge, has an activity for the oxidation of a variety of alkyl ethers, aralkyl ethers and dibenzyl ether. The whole cell activity for diethyl ether oxidation was effectively inhibited by 2,3-dihydrofurane, ethyl vinyl ether and glutaraldehyde. Glutaraldehyde of less than 30 microM inhibited the activity by a competitive manner with the inhibition constant, K(I) of 7.07+/-1.36 microM. The inhibition type became mixed at higher glutaraldehyde concentrations >30 microM, probably due to the inactivation of the cell activity by the Schiff-base formation. Structurally analogous ethyl vinyl ether inhibited the diethyl ether oxidation activity in a mixed manner with decreasing the apparent maximum oxidation rate, v(max)(app), and increasing the apparent Michaelis-Menten constant, K(M)(app). The mixed type inhibition by ethyl vinyl ether seemed to be introduced not only by the structure similarity with diethyl ether, but also by the reactivity of the vinyl ether with cellular components in the whole cell system.     

Antichaperone activity and heme degradation effect of methyl tert‐butyl ether (MTBE) on normal and diabetic hemoglobins

Because of the extensive use of methyl tert‐butyl ether (MTBE) as an additive to increase the octane quality of gasoline, the environmental pollution by this compound has increased in recent decades. Environmental release of MTBE may lead to its entry to the blood stream through inhalation or drinking of contaminated water, and its interactions with biological molecules such as proteins. The present study was proposed to comparatively investigate the interactions of MTBE with hemoglobin (Hb) from diabetic and nondiabetic individuals using various spectroscopic methods including UV‐visible, fluorescence, chemiluminescence, and circular dichroism. These results demonstrated the effects of MTBE on heme degradation of Hb and the reaction of these degradation products with water generating reactive oxygen species. Interaction of Hb with MTBE enhanced its aggregation rate and decreased lag time, indicating the antichaperone activity of MTBE upon interaction with Hb. Furthermore, the diabetic Hb showed more severe effects of MTBE, including heme degradation, reactive oxygen species production, unfolding, and antichaperone behavior than the nondiabetic Hb. The results from molecular docking suggested that the special interaction site of MTBE in the vicinity of Hb heme group is responsible for heme degradation.     

Phytoremediation of MTBE with hybrid poplar trees

This research investigates the fate and transport of methyl tert-butyl ether (MTBE) in phytoremediation, particularly the uptake and volatilization of MTBE in lab-scale hydroponic systems. The research reveals that MTBE was taken up by hybrid poplar cuttings and volatilized to the atmosphere. Volatilization of MTBE occurred through both stems and leaves. The concentration of MTBE in the transpiration stream declined exponentially with height, indicating that the uptake and volatilization along the stems are an important removal mechanism of MTBE in phytoremediation. Volatilization, via diffusion from the stems, has not been directly measured previously. No volatile MTBE metabolites were detected; however, mass balance closure and metabolite detection were not primary objectives of this study. The greatest amount of MTBE in plant biomass was associated with the woody stems from the previous year's growth, owing in part to the large biomass of stems. MTBE in the plant tissues appears to reach a steady state concentration and there does not appear to be an accumulation process that could lead to highly elevated concentrations relative to the groundwater source.     

Protease-catalyzed synthesis of melanocyte-stimulating hormone (MSH) fragments

In the present study on enzymatic peptide bond formation the proteosynthetic potential of several proteases was explored. Trypsin, α-chymotrypsin, papain, carboxypeptidase Y (CPD-Y), and thermolysin served as catalysts for the protease-controlled synthesis of some fragments of melanocyte-stimulating hormones. To obviate possible proteolytic cleavage of preexisting peptide bonds—a drawback often encountered during enzymatic peptide syntheses—several expedients leading to the target peptides were developed. The enzymatic procedure enabled under mild conditions the preparation of the desired peptides whose amino acid composition may give rise to severe complications during conventional syntheses.     

Modern geochemical and molecular tools for monitoring in-situ biodegradation of MTBE and TBA

Methyl tert-butyl ether (MTBE) is a major gasoline oxygenate worldwide and a widespread groundwater contaminant. Natural attenuation of MTBE is of practical interest as a cost effective and non-invasive approach to remediation of contaminated sites. The effectiveness of MTBE attenuation can be difficult to demonstrate without verification of the occurrence of in-situ biodegradation. The aim of this paper is to discuss the recent progress in assessing in-situ biodegradation. In particular, compound-specific isotope analysis (CSIA), molecular techniques based on nucleic acids analysis and in-situ application of stable isotope labels will be discussed. Additionally, attenuation of tert-butyl alcohol (TBA) is of particular interest, as this compound tends to occur alongside MTBE introduced from the gasoline or produced by (mainly anaerobic) biodegradation of MTBE.     

Field note phytovolatilization of oxygenated gasoline-impacted groundwater at an underground storage tank site via conifers

A stand of five conifers (Pinus sp.) bordering a gasoline service station was studied to estimate the methyl tert-butyl ether (MTBE) emission rate from gasoline-impacted groundwater. Groundwater was impacted with gasoline oxygenates MTBE and tert-butyl alcohol (TBA) at combined concentrations exceeding 200,000 microg/L. Condensate from trees was collected in sealed environmental chambers and analyzed. Concentrations of MTBE in condensate ranged from 0.51 to 460 microg/L; TBA ranged from 12 to 4100 microg/L (n=19). Transpirate concentrations were derived from MTBE air-liquid partitioning data exhibited in controls spiked with known concentrations of analyte. Tree emissions were estimated by multiplying average transpirate concentrations by transpiration rates derived from evapotranspiration data. Stand evapotranspiration was calculated using meteorological data from the California Irrigation Management Information System (CIMIS) applied in the Standardized Reference Evapotranspiration Equation.     

柳树对叔丁醇的降解试验

甲基叔丁基醚(MTBE)是目前北美燃料市场最常用的汽油添加剂。由于其化学稳定性强且难于转化,MTBE已成为一种蔓延性的地下水污染物。有氧微生物降解技术被认为是目前对MTBE污染治理最为有效的方法之一,其作用机理是：MTBE在细胞色素酶(CYP-450s)的作用下首先分解成为叔丁醇(TBA),进而完全转化为CO2和H2O。细胞色素酶(CYP-450s)是维管束植物中最为常见的一种酶,我们有理由相信维管束植物细胞能降解MTBE,但试验研究表明超过25种以上的常见植物细胞并不能降解MTBE。TBA是MTBE降解过程中最为稳定的中间产物,植物对其降解的研究目前尚未见报道。本实验用一自行设计的植物反应器来研究柳树(Sallx alba)对TBA降解的可能性。长出新根须和嫩叶的柳树枝条在一容积500ml的植物反应器中生长12d(其中TBA溶液450ml)来观察TBA对柳树生长的影响,同时测定柳树对TBA的吸收和降解。TBA及其它可能的降解产物用气相色谱来检测。本实验结果表明在为期12d的时间内,水溶液中15．26％的TBA可以通过柳树的蒸腾作用去除,但是没有检测到任何可能的降解产物,在植物体内也只发现了少量的TBA残留(＜1％)。同时柳树的根细胞和叶细胞也用来研究对TBA的降解可能性,在为期3d的试验中;柳树的根细胞和叶细胞对TBA的吸收是非常有限的(＜10％),也没有检测到任何可能的降解产物。本研究结果表明柳树同样也不能降解TBA,也许TBA难被降解就是富含CYP-450s酶的维管束植物不能降解MTBE的原因所在。     

Microbial degradation and fate in the environment of methyl tert-butyl ether and related fuel oxygenates

Oxygenates, mainly methyl tert-butyl ether (MTBE), are commonly added to gasoline to enhance octane index and improve combustion efficiency. Other oxygenates used as gasoline additives are ethers such as ethyl tert-butyl ether (ETBE), tert-amyl methyl ether (TAME), and alcohols such as tert-butyl alcohol (TBA). As a result of its wide use, MTBE has been detected, mainly in the USA, in groundwater and surface waters, and is a cause of concern because of its possible health effects and other undesirable consequences. MTBE is a water-soluble and mobile compound that generates long pollution plumes in aquifers impacted by gasoline releases from leaking tanks. Field observations concur in estimating that, because of recalcitrance to biodegradation, natural attenuation is slow (half-life of at least 2 years). However, quite significant advances have been made in recent years concerning the microbiology of the degradation of MTBE and other oxygenated gasoline additives. The recalcitrance of these compounds results from the presence in their structure of an ether bond and of a tertiary carbon structure. For the most part, only aerobic microbial degradation systems have been reported so far. Consortia capable of mineralizing MTBE have been selected. Multiple instances of the cometabolism of MTBE with pure strains or with microflorae, growing on n-alkanes, isoalkanes, cyclohexane or ethers (diethyl ether, ETBE), have been described. MTBE was converted into TBA in all cases and was sometimes further degraded, but it was not used as a carbon source by the pure strains. However, mineralization of MTBE and TBA by several pure bacterial strains using these compounds as sole carbon and energy source has recently been reported. The pathways of metabolism of MTBE involve the initial attack by a monooxygenase. In several cases, the enzyme was characterized as a cytochrome P-450. After oxygenation, the release of a C -unit as formaldehyde or formate leads to the production of TBA, which can be converted to 2-hydroxyisobutyric acid and further metabolized. Developments in microbiology make biological treatment of water contaminated with MTBE and other oxygenates an attractive possibility. Work concerning ex situ treatment in biofilters by consortia and by pure strains, and involving or not cometabolism, is under way. Furthermore, the development of in situ treatment processes is a promisinggoal.     

Biotin reagents for antibody pretargeting. 7. Investigation of chemically inert biotinidase blocking functionalities for synthetic utility

An investigation was conducted to evaluate three biotin derivatives designed to block biotinidase cleavage of the biotinamide bond. Difficulties in multistep syntheses of molecules containing tert-butyl protected hydroxymethyl and carboxylate groups positioned alpha to a biotinamide bond led to the investigation of alternative biotinidase-blocking moieties that do not require protection and deprotection. The targeted biotin derivatives contained serine-O-methyl ether, 2-aminobutyric acid, and valine moieties conjugated to the biotin carboxylate functionality. Those derivatives were further modified with a radioiodinated aryl ring to study their biotinidase stability. As a comparison to previously studied biotin derivatives, radioiodinated versions of biotin conjugates that contained (a) no biotinidase stabilizing group, (b) an N-methyl (sarcosine) stabilizing group, (c) an alpha-carboxylate (aspartate) stabilizing group and hydroxymethyl (serine) stabilizing group were also prepared and tested. When tested in human serum, all of the radioiodinated biotinidase-stabilized biotin derivatives had <1% biotinamide cleavage. Thus, under the conditions studied, all of the tested biotinidase blocking moieties appeared to be equal with regards to protection from biotinidase cleavage. Further testing of the biotin derivatives included a HPLC assay to determine their relative dissociation from recombinant streptavidin (rSAv). The dissociation of cyanocobalamin (CN-Cbl) adducts of biotin-serine-O-methyl ether, biotin-aminobutyric acid, and biotin-valine were compared with the CN-Cbl adduct of biotin-sarcosine. The relative rates of dissociation found were biotin-sarcosine-CN-Cbl > biotin-valine-CN-Cbl > biotin-serine-O-methyl ether-CN-Cbl > biotin-aminobutyric acid-CN-Cbl. Due to the high cost of serine-O-ethyl ether (and its N-Boc derivative) and difficulty in syntheses of its biotin derivatives, that adduct is not an attractive candidate for application to compounds used in vivo. The higher lipophilicity and diminished binding of the biotin-valine adduct also makes its use in vivo less attractive. Thus, the biotin-aminobutyric acid adduct appears to be the best candidate for incorporation into biotin derivatives used in vivo, as it simplifies the synthetic procedures, has low cost, and provides effective blocking of biotinidase while retaining high binding affinity.     

Methyl <Emphasis Type="Italic">tert</Emphasis>-butyl Ether and <Emphasis Type="Italic">tert</Emphasis>-butyl Alcohol Degradation by <Emphasis Type="Italic">Fusarium solani</Emphasis>

Fusarium solani degraded methyl tert-butyl ether (MTBE) and other oxygenated compounds from gasoline including tert-butyl alcohol (TBA). The maximum degradation rate of MTBE was 16 mg protein h and 46 mg/g protein h for TBA. The culture transformed 77% of the total carbon to ¹⁴CO₂. The estimated yield for MTBE was 0.18 g dry wt/g MTBE.     

Review of MTBE Biodegradation and Bioremediation

Conclusive evidence of methyl tert-butyl ether (MTBE) biotransformation and complete mineralization under aerobic conditions in environmental samples and enrichment cultures is reviewed, in addition to increasing evidence of MTBE biotransformation under anaerobic conditions. The metabolic pathway of MTBE appears to have two key intermediates, tert-butyl alcohol (TBA) and 2-hydroxy isobutyric acid (HIBA). The first enzyme in MTBE biodegradation has been identified as either a cytochrome P450 or a nonhemic monooxygenase in different isolates. Mixed and pure cultures of microorganisms have utilized MTBE as a sole carbon and energy source. Cometabolism of MTBE with n-alkanes at rates of 3.9 to 52 nmol/min/mg protein has been documented. The presence of co-contaminants such as BTEX has either not affected or seemed to limit MTBE biodegradation. Some studies of MTBE natural attenuation have attributed mass loss to biodegradation, while others have attributed mass loss to dilution and dispersion. Recent advances in the assessment of MTBE biodegradation have indicated the potential for natural anaerobic transformation of MTBE. In situ bioremediation of MTBE has been enhanced by adding air or oxygen, or by adding microorganisms and air or oxygen. Bioreactors have attained significant removal of MTBE from MTBE-contaminated influent. Despite historical concerns about the biodegradability of MTBE, several biological methods can now be used for MTBE remediation.     

Methyl tert-butyl ether biodegradation by microbial consortia obtained from soil samples of gasoline-polluted sites in Mexico

Microbial consortia obtained from soil samples of gasoline-polluted sites were individually enriched with pentane, hexane, isooctane and toluene. Cometabolism with methyl tert-butyl ether, (MTBE), gave maximum degradation rates of 49, 12, 32 and 0 mg g(-1)protein h(-1), respectively. MTBE was fully degraded even when pentane was completely depleted with a cometabolic coefficient of 1 mgMTBE mg(-1)pentane. The analysis of 16S rDNA from isolated microorganisms in the pentane-adapted consortia showed that microorganisms could be assigned to Pseudomonas. This is the first work reporting the cometabolic mineralization of MTBE by consortium of this genus.