Isolation and characterization of four di-<Emphasis Type="Italic">n</Emphasis>-butyl phthalate (DBP)-degrading <Emphasis Type="Italic">Gordonia</Emphasis> sp<Emphasis Type="Italic">.</Emphasis> strains and cloning the 3,4-phthalate dioxygenase gene

Four aerobic bacterial strains capable of utilizing di-n-butyl phthalate (DBP) as the sole source of carbon and energy were isolated from river sediments. Based on the morphology, biochemical characterization, and 16S rRNA gene sequence analysis, they were identified as Gordonia sp. The optimal conditions for DBP degradation by these strains were found to be pH 7.0, 30°C, and stirring at 175 rpm. These four strains could degrade, respectively, 96, 98, 98, and 78% of DBP (400 mg l⁻¹) as well as dimethyl phthalate (DMP), diethyl phthalate (DEP), di-n-octyl phthalate (DOP), di-isooctyl phthalate (DIOP), and di-isononyl phthalate (DINP). Furthermore, partial sequences of the gene for 3,4-phthalate dioxygenase were obtained from all four strains. To our knowledge, this is the first time that the 3,4-phthalate dioxygenase gene has been successfully cloned from Gordonia sp.     

Biodegradation and kinetic analysis of phthalates by an Arthrobacter strain isolated from constructed wetland soil

A bacterial strain C21 isolated from constructed wetland soil was identified as Arthrobacter sp. based on 16S rRNA gene sequence analysis and physio-biochemical characteristics and was capable of utilizing di-n-butyl phthalate (DBP) as a carbon and energy source for growth. Strain C21 can also utilize other phthalates (PAEs) up to a molecular weight of 390.56 and phthalic acid (PA). The biodegradability of these compounds decreased with the increase in the length of phthalate alkyl chains and molecular weight. Kinetic analysis indicated that the strain C21 cell growth on DBP fitted well with Haldane-Andrews’ model (R ²?>?0.98) with μ _max, K _s, and K _i of 0.12/h, 4.2 mg/L, and 204.6 mg/L, respectively. When the initial DBP concentration was lower than 100 mg/L, DBP biodegradation reaction fitted with the first-order kinetics. The results suggested that Arthrobacter strain C21 played an active role in the bioremediation of the wetland contaminated with phthalates.     

Biodegradation of di-n-butyl phthalate by Rhodococcus sp. JDC-11 and molecular detection of 3, 4-phthalate dioxygenase gene

Rhodococcus sp. JDC-11, capable of utilizing di-n-butyl phthalate (DBP) as the sole source of carbon and energy, was isolated from sewage sludge and confirmed mainly based on 16S rRNA gene sequence analysis. The optimum pH, temperature, and agitation rate for DBP degradation by Rhodococcus sp. JDC-11 was 8.0, 30 degrees C, and 175 rpm, respectively. In addition, the effect of glucose concentration on DBP degradation indicated that low concentration of glucose inhibited the degradation of DBP while high concentrations of glucose increased its degradation. Meanwhile, the substrates utilization test showed that JDC-11 could also utilize other phthalates. Furthermore, the major metabolites of DBP degradation were identified as mono-butyl phthalate and phthalic acid by gas chromatography-mass spectrometry and the metabolic pathway of DBP degradation by Rhodococcus sp. JDC-11 was tentatively speculated. Using a set of new degenerate primer, partial sequence of the 3, 4-phthalate dioxygenase gene was obtained from the strain. Sequence analysis revealed that the phthalate dioxygenase gene of JDC-11 was highly homologous to the large subunit of phthalate dioxygenase from Rhodococcus coprophilus strain G9.     

The transformation of phthalaldehydate by phthalate-grown Micrococcus strain 12B

Micrococcus strain 12B, grown with phthalate, transformed the phthalate analog, phthalaldehydate (2-formylbenzoate), to 3,4-dihydroxyphthalaldehydate which was isolated and identified as its lactol. An ¹⁸O₂ incorporation experiment indicated that a dioxygenase mechanism was involved. It is proposed by analogy, that phthalate is metabolized through cis-3,4-dihydro-3,4-dihydroxyphthalate and 3,4-dihydroxyphthalate by this bacterium.     

Kinetics and pathway of biodegradation of dibutyl phthalate by Pleurotus ostreatus

Dibutyl phthalate (DBP) is a plasticizer, whose presence in the environment as a pollutant has attained a great deal of attention due to its reported association with endocrine system disturbances on animals. Growth parameters, glucose uptake, percentage of removal efficiency (%E) of DBP, biodegradation constant of DBP (k) and half-life of DBP biodegradation (t_1/2) were evaluated for Pleurotus ostreatus grown on media containing glucose and different concentrations of DBP (0, 500 and 1000 mg l^?1). P. ostreatus degraded 99.6 % and 94 % of 500 and 1000 mg of DBP l^?1 after 312 h and 504 h, respectively. The k was 0.0155 h^?1 and 0.0043 h^?1 for 500 and 1000 mg of DBP l^?1, respectively. t_1/2 was 44.7 h and 161 h for 500 and 1000 mg of DBP l^?1, respectively. Intermediate compounds of biodegraded DBP were identified by GC-MS and a DBP biodegradation pathway was proposed using quantum chemical calculation. DBP might be metabolized to benzene and acetyl acetate, the first would be oxidated to muconic acid and the latter would enter into the Krebs cycle. P. ostreatus has the ability to degrade DBP and utilizes it as source of carbon and energy.     

Metabolism of Pyridine Compounds by Phthalate-Degrading Bacteria

Bacteria were isolated from marine sediments that grew aerobically on m-phthalate, p-phthalate, or dipicolinate (2,6-pyridine dicarboxylate [2,6-PDCA]). Strain OP-1, which grew on o-phthalate and was previously obtained from a marine source, was also studied. Intact cells of each organism demonstrated Na⁺-dependent oxidation of their growth substrates. Strain PCC5M grew on dipicolinate but did not metabolize m-phthalate. The phthalate degraders, however, demonstrated Na⁺-dependent metabolism of the appropriate PDCA analogs. 2,6-PDCA was transformed by strain CC9M when this strain was grown on m-phthalate, 2,5-PDCA was metabolized by strain PP-1 grown on p-phthalate, and 2,3-PDCA (quinolinate) was oxidized by strain OP-1 grown on o-phthalate. Spectral changes accompanying the Na⁺-dependent transformations of the PDCA analogs suggest the formation of hydroxylated compounds. Metabolism probably occurred via phthalate hydroxylases; this is a previously unrecognized route for the environmental transformation of pyridine compounds. Hydroxylated products may feed into known pathways for the catabolism of pyridines or be photochemically degraded because of their absorbance in the solar actinic range (wavelengths > 300 nm). The results reinforce recent evidence for the broad potential of aromatic hydroxylase systems for the destruction of pollutants.     

Tributyl phosphate biodegradation to butanol and phosphate and utilization by a novel bacterial isolate,Sphingobium sp. strain RSMS

A Sphingobium sp. strain isolated from radioactive solid waste management site (RSMS) completely degraded 7.98 g/L of tributyl phosphate (TBP) from TBP containing suspensions in 3 days. It also completely degraded 20 mM dibutyl phosphate (DBP) within 2 days. The strain tolerated high levels of TBP and showed excellent stability with respect to TBP degradation over several repeated subcultures. On solid minimal media or Luria Bertani media supplemented with TBP, the RSMS strain showed a clear zone of TBP degradation around the colony. Gas chromatography and spectrophotometry analyses identified DBP as the intermediate and butanol and phosphate as the products of TBP biodegradation. The RSMS strain utilized both TBP and DBP as the sole source of carbon and phosphorous for its growth. The butanol released was completely utilized by the strain as a carbon source thereby leaving no toxic residue in the medium. Degradation of TBP or DBP was found to be suppressed by high concentration of glucose which also inhibited TBP or DBP dependent growth. The results highlight the potential of Sphingobium sp. strain RSMS for bioremediation of TBP and for further molecular investigation.     

3-Nitrotoluene dioxygenase from Diaphorobacter sp. strains: cloning,sequencing and evolutionary studies

The first step in the degradation of 3-nitrotoluene by Diaphorobacter sp. strain DS2 is the dihydroxylation of the benzene ring with the concomitant removal of nitro group. This is catalyzed by a dioxygenase enzyme system. We report here the cloning and sequencing of the complete dioxygenase gene with its putative regulatory sequence from the genomic DNA of Diaphorobacter sp. strains DS1, DS2 and DS3. Analysis of the 5 kb DNA stretch that was cloned, revealed five complete open reading frames (ORFs) encoding for a reductase, a ferredoxin and two dioxygenase subunits with predicted molecular weights (MW) of 35, 12, 50 and 23 kDa respectively. A regulatory protein was also divergently transcribed from the reductase subunit and has a predicated MW of 34 kDa. Presence of parts of two functional ORFs in between the reductase and the ferredoxin subunits reveals an evolutionary route from a naphthalene dioxygenase like system of Ralstonia sp. strain U2. Further a 100 % identity of its ferredoxin subunit reveals its evolution via dinitrotoluene dioxygenase like system present in Burkholderia cepacia strain R34. A modeled structure of oxygenase_3NT from strain DS2 was generated using nitrobenzene dioxygenase as a template. The modeled structure only showed minor changes at its active site. Comparison of growth patterns of strains DS1, DS2 and DS3 revealed that Diaphorobacter sp. strain DS1 has been evolved to degrade 4-nitrotoluene better by an oxidative route amongst all three strains.     

Surface Glycolipids in Shoot-forming Culture of Nicotiana umbratica

Phthalate oxygenase was induced in Rhodococcus erythropolis S-1, a Gram-positive bacterium, when this bacterium was cultured in a medium containing phthalate as a sole carbon source. The enzyme was purified 118-fold with 4.7% activity yield. The purified enzyme appeared homogenous on native PAGE. This enzyme is a large protein (213 kDa), a tetramer of identical 56kDa monomers, and a flavoprotein containing FAD with NADH-dependent dioxygenase activity. The enzyme is specific for phthalate and other closely related aromatic compounds. Optimum pH and temperature were 6.5 and 40°C. The K_m for phthalate and NADH were 0.040 mM and 0.069 mM. The enzyme catalyzes dihydroxylation of phthalate to form 3,4-dihydro-3,4-dihydroxyphthalate with consumption of NADH and oxygen.     

Cloning of a dibutyl phthalate hydrolase gene from Acinetobacter sp. strain M673 and functional analysis of its expression product in Escherichia coli

A dibutyl phthalate (DBP) transforming bacterium, strain M673, was isolated and identified as Acinetobacter sp. This strain could not grow on dialkyl phthalates, including dimethyl, diethyl, dipropyl, dibutyl, dipentyl, dihexyl, di(2-ethylhexyl), di-n-octyl, and dinonyl phthalate, but suspensions of cells could transform these compounds to phthalate via corresponding monoalkyl phthalates. During growth in Luria–Bertani medium, M673 produced the high amounts of non-DBP-induced intracellular hydrolase in the stationary phase. One DBP hydrolase gene containing an open reading frame of 1,095 bp was screened from a genomic library, and its expression product hydrolyzed various dialkyl phthalates to the corresponding monoalkyl phthalates.     

Biodegradation of sulfamethazine by an isolated thermophile–<Emphasis Type="Italic">Geobacillus</Emphasis> sp. S-07

Sulfamethazine (SM2) is an antimicrobial drug that is frequently detected in manure compost, is difficult to degrade at high temperatures and is potentially threatening to the environment. In this study, a thermophilic bacterium was isolated from the activated sludge of an antibiotics pharmaceutical factory; this bacterium has the ability to degrade SM2 at 70?°C, which is higher than the traditional manure composting temperature. The strain S-07 is closely related to Geobacillus thermoleovorans based on its 16S rRNA gene sequence. The optimal conditions for the degradation of SM2 are 70?°C, pH 6.0, 50 rpm rotation speed and 50 mL of culture volume. More than 95% of the SM2 contained in media was removed via co-metabolism within 24 h, which was a much higher percentage than that of the type strain of G. thermoleovorans. The supernatant from the S-07 culture grown in SM2-containing media showed slightly attenuated antibacterial activity. In addition, strain S-07 was able to degrade other sulfonamides, including sulfadiazine, sulfamethoxazole and sulfamerazine. These results imply that strain S-07 might be a new auxiliary bacterial resource for the biodegradation of sulfonamide residue in manure composting.     

Neonicotinoid resistance and cDNA sequences of nicotinic acetylcholine receptor subunits of the western flower thrips Frankliniella occidentalis (Thysanoptera: Thripidae)

The western flower thrips, Frankliniella occidentalis (Pergande), is difficult to control because of high insecticide resistance. In this study, susceptibility to major insecticides was examined in two Japanese strains (H-1 and KC) and a Chinese strain (BJ) using a leaf-dipping method. All three strains were resistant to permethrin and acetamiprid at agriculturally recommended doses. The median lethal concentration (LC₅₀) for acetamiprid was 1720 ppm in strain H-1, 4780 ppm in strain KC and >6680 ppm in strain BJ. In the presence of piperonyl butoxide, an inhibitor of cytochrome P450 monooxygenases, the LC₅₀ for acetamiprid was 312 ppm in strain H-1, 837 ppm in strain KC and 1250 ppm in strain BJ. These results suggested that metabolism by cytochrome P450 monooxygenases is involved in acetamiprid resistance in these strains, though other factors also seem to play a role. Furthermore, cDNA cloning of the nicotinic acetylcholine receptor (nAChR) subunits was performed using degenerate primers, and the presence or absence of a point mutation in nAChR β1 was confirmed. The R81T mutation that had been reported in Myzus persicae (Sulzer) nAChR β1 was not found in F. occidentalis strains tested in this study.     

Phthalate catabolic gene cluster is linked to the angular dioxygenase gene in <Emphasis Type="Italic">Terrabacter</Emphasis> sp. strain DBF63

Phthalate is a metabolic intermediate of the pathway of fluorene (FN) degradation via angular dioxygenation. A gene cluster responsible for the conversion of phthalate to protocatechuate was cloned from the dibenzofuran (DF)- and FN-degrading bacterium Terrabacter sp. strain DBF63 and sequenced. The genes encoding seven catabolic enzymes, oxygenase large subunit of phthalate 3,4-dioxygenase (phtA1), oxygenase small subunit of phthalate 3,4-dioxygenase (phtA2), cis-3,4-dihydroxy-3,4-dihydrophthalate dehydrogenase (phtB), [3Fe-4S] or [4Fe-4S] type of ferredoxin (phtA3), ferredoxin reductase (phtA4), 3,4-dihydroxyphthalate decarboxylase (phtC) and putative regulatory protein (phtR), were found in the upstream region of the angular dioxygenase gene (dbfA1A2), encoded in this order. Escherichia coli carrying phtA1A2BA3A4 genes converted phthalate to 3,4-dihydroxyphthalate, and the 3,4-dihydroxyphthalate decarboxylase activity by E. coli cells carrying phtC was finally detected with the introduction of a Shine-Dalgarno sequence in the upstream region of its initiation codon. Homology analysis on the upstream region of the pht gene cluster revealed that there was an insertion sequence (IS) (ISTesp2; ORF14 and its flanking region), part of which was almost 100% identical to the orf1 and its flanking region adjacent to the extradiol dioxygenase gene ( bphC1) involved in the DF degradation of Terrabacter sp. strain DPO360 [Schmid et al. (1997) J Bacteriol 179:53-62]. This suggests that ISTesp2 plays a role in the metabolism of aromatic compounds in Terrabacter sp. strains DBF63 and DPO360.     

Influence of metal ions on bioremediation activity of protocatechuate 3,4-dioxygenase from Stenotrophomonas maltophilia KB2

The aim of this paper was to describe the effect of various metal ions on the activity of protocatechuate 3,4-dioxygenase from Stenotrophomonas maltophilia KB2. We also compared activity of different dioxygenases isolated from this strain, in the presence of metal ions, after induction by various aromatic compounds. S. maltophilia KB2 degraded 13 mM 3,4-dihydroxybenzoate, 10 mM benzoic acid and 12 mM phenol within 24 h of incubation. In the presence of dihydroxybenzoate and benzoate, the activity of protocatechuate 3,4-dioxygenase and catechol 1,2-dioxygenase was observed. Although Fe³⁺, Cu²⁺, Zn²⁺, Co²⁺, Al³⁺, Cd²⁺, Ni²⁺ and Mn²⁺ ions caused 20–80 % inhibition of protocatechuate 3,4-dioxygenase activity, the above-mentioned metal ions (with the exception of Ni²⁺) inhibited catechol 1,2-dioxygenase to a lesser extent or even activate the enzyme. Retaining activity of at least one of three dioxygenases from strain KB2 in the presence of metal ions makes it an ideal bacterium for bioremediation of contaminated areas.     

Biodegradation of 4-nitrotoluene with biosurfactant production by Rhodococcus pyridinivorans NT2: metabolic pathway, cell surface properties and toxicological characterization

A novel 4-nitrotoluene-degrading bacterial strain was isolated from pesticides contaminated effluent-sediment and identified as Rhodococcus pyridinivorans NT2 based on morphological and biochemical properties and 16S rDNA sequencing. The strain NT2 degraded 4-NT (400 mg l^?1) with rapid growth at the end of 120 h, reduced surface tension of the media from 71 to 29 mN m^?1 and produced glycolipidic biosurfactants (45 mg l^?1). The biosurfactant was purified and characterized as trehalose lipids. The biosurfactant was stable in high salinity (10 % w/v NaCl), elevated temperatures (120 °C for 15 min) and a wide pH range (2.0–10.0). The noticeable changes during biodegradation were decreased hydrophobicity; an increase in degree of fatty acid saturation, saturated/unsaturated ratio and cyclopropane fatty acid. Biodegradation of 4-NT was accompanied by the accumulation of ammonium (NH₄ ⁺) and negligible amount of nitrite ion (NO₂ ^?). Product stoichiometry showed a carbon (C) and nitrogen (N) mass balance of 37 and 35 %, respectively. Biodegradation of 4-NT proceeded by oxidation at the methyl group to form 4-nitrobenzoate, followed by reduction and hydrolytic deamination yielding protocatechuate, which was metabolized through β-ketoadipate pathway. In vitro and in vivo acute toxicity assays in adult rat (Rattus norvegicus) showed sequential detoxification and the order of toxicity was 4-NT >4-nitrobenzyl alcohol >4-nitrobenzaldehyde >4-nitrobenzoate >> protocatechuate. Taken together, the strain NT2 could be used as a potential bioaugmentation candidate for the bioremediation of contaminated sites.     

Purification and characterization of a novel type of protocatechuate 3,4-dioxygenase with the ability to oxidize 4-sulfocatechol

4-Aminobenzenesulfonate is degraded via 4-sulfocatechol by a mixed bacterial culture that consists of Hydrogenophaga palleronii strain S1 and Agrobacterium radiobacter strain S2. From the 4-sulfocatechol-degrading organism A. radiobacter strain S2, a dioxygenase that converted 4-sulfocatechol to 3-sulfomuconate was purified to homogeneity. The purified enzyme also converted protocatechuate with a similar catalytic activity to 3-carboxy-cis,cis-muconate. Furthermore, the purified enzyme oxidized 3,4-dihydroxyphenylacetate, 3,4-dihydroxycinnamate, catechol, and 3- and 4-methylcatechol. The enzyme had a mol. wt. of about 97,400 as determined by gel filtration and consisted of two different types of subunits with mol. wt. of about 23,000 and 28,500. The NH₂-terminal amino acid sequences of the two subunits were determined. An isofunctional dioxygenase was partially purified from H. palleronii strain S1. A. radiobacter strain S2 also induced, after growth with 4-sulfocatechol, an „ordinary“ protocatechuate 3,4-dioxygenase that did not oxidize 4-sulfocatechol. This enzyme was also purified to homogeneity, and its catalytic and structural characteristics were compared to the „4-sulfocatechol-dioxygenase“ from the same strain. Received: 5 February 1996 / Accepted: 18 April 1996     

Anaerobic degradation of phthalic acid esters during digestion of municipal solid waste under landfilling conditions

Anaerobic microorganisms in municipal solid waste samples from laboratory-scale landfill reactors and a pilot-plant biogas digestor were investigated with the aim of assessing their ability to transform four commercially used phthalic acid esters (PAEs) and phthalic acid (PA). The PAEs studied were diethyl phthalate (DEP), butylbenzyl phthalate (BBP), dibutyl phthalate (DBP) and bis(2-ethylhexyl) phthalate (DEHP). No biological transformation of DEHP could be detected in any of the experiments. Together with waste samples from the simulated landfilling conditions, the PAEs (except DEHP) were hydrolytically transformed to their corresponding monoesters. These accumulated as end products, and in most cases they were not further degraded. During incubation with waste from the biogas digestor, the PAEs (except DEHP) were completely degraded to methane and carbon dioxide. The influence of the landfill development phase on the transformations was investigated utilizing PA and DEP as model substances. We found that during both the intense and stable methanogenic (but not the acidogenic) phases, the microoganisms in the samples had the potential to transform PA. A shorter lag phase was observed for the PA transformation in the samples from the stable methanogenic phase as compared with earlier phases. This indicates an increased capacity to degrade PA during the aging phases of the municipal solid waste in landfills. No enhancement of the DEP transformation could be observed as conditions in the methanogenic landfill model changed over a year's time. The results indicate that microorganisms developing in a methanogenic landfill environment have a substantially lower potential to degrade PAEs compared with those developing in a biogas reactor.Abbreviations BBP butylbenzyl phthalate - DEHP bis(2-ethylhexyl) phthalate - CoA coenzyme A - DBP dibutyl phthalate - DEP diethyl phthalate - DS dry solids - MBeP monobenzyl phthalate - MBuP monobutyl phthalate - MEP monoethyl phthalate - MSW municipal solid waste - PA phthalic acid - PAE(s) phthalic acid ester(s) - VFA volatile fatty acids     

Fungal biodegradation of dibutyl phthalate and toxicity of its breakdown products on the basis of fungal and bacterial growth

Phthalates are esters of phthalic acid that give flexibility to polyvinyl chloride. Diverse studies have reported that these compounds might be carcinogenic, mutagenic and/or teratogenic. Radial growth rate, biomass, hyphal thickness of Neurospora sitophyla, Trichoderma harzianum and Aspergillus niger, grown in two different concentrations of dibutyl phthalate (DBP) (500 and 1,000 mg/l) in agar and in submerged fermentation were studied. The inhibitory concentration (IC₅₀) and the constant of biodegradation of dibutyl phthalate in Escherichia coli cultures were used to evaluate toxicity. The radial growth rate and thickness of the hypha were positively correlated with the concentration of phthalate. The pH of the cultures decreased as the fermentation proceeded. It is shown that these fungi are able to degrade DBP to non-toxic compounds and that these can be used as sole carbon and energy sources by this bacterium. It is demonstrated that the biodegradation of the DBP is directly correlated with the IC₅₀. This is the first study that reports a method to determine the biodegradation of DBP on the basis of the IC₅₀ and fungal growth, and the effect of this phthalate on the growth and thickness of hyphae of filamentous fungi in agar and in submerged fermentation.