Biodegradation of 2,4,6-tribromophenol by Ochrobactrum sp. strain TB01

A bacterium that utilizes 2,4,6-tribromophenol (2,4,6-TBP) as sole carbon and energy source was isolated from soil contaminated with brominated pollutants. This bacterium, designated strain TB01, was identified as an Ochrobactrum species. The organism degraded 100 microM of 2,4,6-TBP within 36 h in a growing culture. In addition, it released 3 mol of bromine ions from 1 mol of 2,4,6-TBP during the complete degradation of 2,4,6-TBP in a resting cell assay. Moreover, cells grown on 2,4,6-TBP degraded 2,6-dibromophenol (2,6-DBP), 4-bromophenol (4-BP), 2,4,6-trichlorophenol (2,4,6-TCP) and phenol. Metabolic intermediates were detected in the reaction mixture of an in vitro assay for 2,4,6-TBP, and they were identified as 2,4-DBP and 2-BP. NADH was required for the debromination of 2,4,6-TBP. These results suggest that 2,4,6-TBP is converted to phenol through sequential reductive debromination reactions via 2,4-DBP and 2-BP by this strain.     

Transformation of nitroaromatic compounds by a methanogenic bacterium,Methanococcus sp. (strain B)

The transformation of several nitroaromatic compounds by a newly isolated methanogenic bacterium, Methanococcus sp. (strain B) was studied. The presence of nitroaromatic compounds (0.5 mM) viz., nitrobenzene, 2,4-dinitrobenzene, 2,4,6-trinitrobenzene, 2,4-dinitrophenol, 2,4-dinitrobenzene, and 2,6-dinitrotoluene in the culture medium did not inhibit growth of the isolate. The bacteria grew rapidly and reached stationary phase within seven days of incubation. All the nitroaromatic compounds tested were 80 to 100% transformed by the bacterium to amino compounds by a reduction process. The isolate did not use the nitroaromatic compounds as the sole source of carbon or nitrogen. The transformation of nitroaromatic compounds by this isolate was compared to that of other methanogenic bacteria. Out of five methanogens studied, only Methanococcus deltae and Methanococcus thermolithotrophicus could transform the nitroaromatic compounds; however, the transformation rates were significantly less than that of the new isolate Methanococcus sp. (strain B). The nitroaromatic compounds were not transformed by Methanosarcina barkeri, Methanobacterium thermoautotrophicum, and Methanobrevibacter ruminantium.Abbreviations NB Nitrobenzene - DNB 2,4-Dinitrobenzene - TNB 2,4,6-Trinitrobenzene - DNP 2,4-Dinitrophenol - 2,4-DNT 2,4-Dinitrotoluene - 2,6-DNT 2,6-Dinitrotoluene     

Isolation and Characterization of Phenol-Degrading Soil Bacterium Xanthobacter flavus

A soil bacterium isolated from a contaminated site degraded phenol when provided as the sole carbon and energy source in the medium. The bacterium was identified as Xanthobacter flavus MTCC 9130. This microbial strain was able to tolerate phenol up to 1000 mg L^?1 concentration. The lag phase increased with the increase in phenol concentration. The optimum growth temperature was 37°C. The organism efficiently utilized phenol and could degrade it completely within 120 h when initial concentration was less than 600 mg L^?1. Degradation of phenol was through ortho pathway, enzyme assay through cell-free extract exhibited the presence of catechol 1,2-dioxygenase. The specific activity was 0.146 μ mol min^?1 mg^?1 protein. However, higher concentrations of phenol in the medium had a negative effect on the growth of the bacterium. Hence this ability of Xanthobacter flavus can be effectively used for bioremediation studies of phenol-contaminated sites.     

Degradation of polychlorinated phenols by Streptomyces rochei 303

The strain Streptomyces rochei 303 (VKM Ac-1284D) is capable of utilizing 2-chloro-,2,4-,2,6-dichloro- and 2,4,6-trichlorophenols as the sole source of carbon. Its resting cells completely dechlorinated and degraded 2-, 3-chloro-; 2,4-, 2,6-, 2,3-, 2,5-, 3,4-, 3,5-dichloro-; 2,4-, 2,6-dibromo-; 2,4,6-, 2,4,5-, 2,3,4-, 2,3,5-, 2,3,6-trichlorophenols; 2,3,5,6-tetrachloro- and pentachlorophenol. During chlorophenol degradation, a stoichiometric amount of chloride ions was released and chlorohydroquinols were formed as intermediates. In cell-free extracts of S. rochei, the activity of hydroxyquinol 1,2-dioxygenase was found. The enzyme was induced with chlorophenols. Of all so far described strains degrading polychlorophenols, S. rochei 303 utilized a wider range of chlorinated phenols as the sole sourse of carbon and energy.Abbreviations CP chlorophenol - DCP dichlorophenol - TCP trichlorophenol - TeCP tetrachlorophenol - PCP pentachlorophenol - DBrP dibromophenol - CHQ chlorohydroquinol - DCHQ dichlorohydroquinol - HHQ hydroxyhydroquinol - CHHQ chlorohydroxyhydroquinol - CC chlorocatechol - TLC thin layer chromatography - GC/MC chromato-mass-spectrometry - HPLC high-performance liquid chromatography     

Degradation of 2,4,6-trichlorophenol by Azotobacter sp. strain GP1.

A bacterium which utilizes 2,4,6-trichlorophenol (TCP) as a sole source of carbon and energy was isolated from soil. The bacterium, designated strain GP1, was identified as an Azotobacter sp. TCP was the only chlorinated phenol which supported the growth of the bacterium. Resting cells transformed monochlorophenols, 2,6-dichlorophenol, and 2,3,6-trichlorophenol. Phenol and a number of phenolic compounds, including 4-methylphenol, all of the monohydroxybenzoates, and several dihydroxybenzoates, were very good carbon sources for Azotobacter sp. strain GP1. The organism utilized up to 800 mg of TCP per liter; the lag phase and time for degradation, however, were severely prolonged at TCP concentrations above 500 mg/liter. Repeated additions of 200 mg of TCP per liter led to accelerated degradation, with an optimum value of 100 mg of TCP per liter per h. TCP degradation was significantly faster in shaken than in nonshaken cultures. The optimum temperature for degradation was 25 to 30 degrees C. Induction studies, including treatment of the cells with chloramphenicol prior to TCP or phenol addition, revealed that TCP induced TCP degradation but not phenol degradation and that phenol induced only its own utilization. Per mol of TCP, 3 mol of Cl- was released. 2,6-Dichloro-p-benzoquinone was detected in the resting-cell medium of Azotobacter sp. strain GP1. By chemical mutagenesis, mutants blocked in either TCP degradation or phenol degradation were obtained. No mutant defective in the degradation of both phenols was found, indicating separate pathways for the dissimilation of the compounds. In some of the phenol-deficient mutants, pyrocatechol was found to accumulate, and in some of the TCP-deficient mutants, 2,6-dichlorohydroquinone was found to accumulate.     

Degradation of 2,4,6-trichlorophenol by Azotobacter sp. strain GP1

A bacterium which utilizes 2,4,6-trichlorophenol (TCP) as a sole source of carbon and energy was isolated from soil. The bacterium, designated strain GP1, was identified as an Azotobacter sp. TCP was the only chlorinated phenol which supported the growth of the bacterium. Resting cells transformed monochlorophenols, 2,6-dichlorophenol, and 2,3,6-trichlorophenol. Phenol and a number of phenolic compounds, including 4-methylphenol, all of the monohydroxybenzoates, and several dihydroxybenzoates, were very good carbon sources for Azotobacter sp. strain GP1. The organism utilized up to 800 mg of TCP per liter; the lag phase and time for degradation, however, were severely prolonged at TCP concentrations above 500 mg/liter. Repeated additions of 200 mg of TCP per liter led to accelerated degradation, with an optimum value of 100 mg of TCP per liter per h. TCP degradation was significantly faster in shaken than in nonshaken cultures. The optimum temperature for degradation was 25 to 30 degrees C. Induction studies, including treatment of the cells with chloramphenicol prior to TCP or phenol addition, revealed that TCP induced TCP degradation but not phenol degradation and that phenol induced only its own utilization. Per mol of TCP, 3 mol of Cl- was released. 2,6-Dichloro-p-benzoquinone was detected in the resting-cell medium of Azotobacter sp. strain GP1. By chemical mutagenesis, mutants blocked in either TCP degradation or phenol degradation were obtained. No mutant defective in the degradation of both phenols was found, indicating separate pathways for the dissimilation of the compounds. In some of the phenol-deficient mutants, pyrocatechol was found to accumulate, and in some of the TCP-deficient mutants, 2,6-dichlorohydroquinone was found to accumulate.     

Catabolism of 2,6-dinitrophenol by Alcaligenes eutrophus JMP 134 and JMP 222

Both Alcaligenes eutrophus JMP 134 and its plasmid-free derivative Alcaligenes eutrophus JMP 222 utilize 2,6-dinitrophenol as sole source of carbon, energy, and nitrogen. In the presence of ammonia resting cells of these strains release two mol of nitrite per mol of 2,6-dinitrophenol. Alcaligenes eutrophus JMP 222-1D, a mutant of strain JMP 222 obtained by transposon (Tn5) mutagenesis, is able to use 2,6-dinitrophenol as nitrogen source but not as source of carbon and energy. Resting cells of this mutant liberate only one mol of nitrite per mol of 2,6-dinitrophenol. A single metabolite was detected by high-pressure liquid chromatography and identified as 2-hydroxy-5-nitropenta-2,4-dienoic acid from the mass spectrum, the ¹H-, and ¹³C-NMR spectra. Strain JMP 222-1S, a spontaneous mutant of strain JMP 222-1D, accumulates 4-nitropyrogallol which was identified as the initial metabolite of 2,6-dinitrophenol degradation.Non-standard abbreviations 2,4-D 2,4-dichlorophenoxyacetic acid - 2,6-DNP 2,6-dinitrophenol - HNMA 2-hydroxy-5-nitromuconic acid - HNPA 2-hydroxy-5-nitropenta-2,4-dienoic acid - NB nutrient broth - NMR nuclear magnetic resonance - NPG 4-nitropyrogallol - O.D. optical density - t_R retention time - UV/Vis ultraviolet/visible     

Biodegradation of the mixtures of 4-chlorophenol and phenol by Comamonas testosteroni CPW301

A 4-chlorophenol (4-CP)-degrading bacterium, strain CPW301, was isolated from soil and identified as Comamonas testosteroni. This strain dechlorinated and degraded 4-CP via a meta-cleavage pathway. CPW301 could also utilize phenol as a carbon and energy source without the accumulation of any metabolites via the same meta-cleavage pathway. When phenol was added as a additional substrate, CPW301 could degrade 4-CP and phenol simultaneously. The addition of phenol greatly accelerated the degradation of 4-CP due to the increased cell mass. The simultaneous degradation of the 4-CP and phenol is useful not only for enhanced cell growth but also for the bioremediation of both compounds, which are normally present in hazardous waste sites as a mixture.     

厌氧微生物菌群XH-1对2,4,6-三氯苯酚的降解特性

有机污染物2,4,6-三氯苯酚(2,4,6-TCP)普遍存在于地下水和河流底泥等厌氧环境中。为了探究厌氧微生物菌群XH-1对2,4,6-TCP的降解能力,本研究以2,4,6-TCP为底物,接种XH-1建立微宇宙培养体系,并以中间产物4-氯苯酚(4-CP)和苯酚为底物分别进行分段富集培养,利用高效液相色谱分析底物的降解转化,同时基于16S rRNA基因高通量测序分析微生物群落结构变化。结果表明: 2,4,6-TCP(122 μmol·L^-1)以0.15 μmol·d^-1的速率在80 d内被完全降解转化,降解中间产物分别为2,4-二氯苯酚(2,4-DCP)、4-氯苯酚和苯酚,所有中间产物最终在325 d被完全降解。高通量测序结果表明,脱卤杆菌和脱卤球菌可能驱动2,4,6-TCP还原脱氯,其中,脱卤球菌可能在4-CP的脱氯转化中发挥重要作用,并与丁酸互营菌和产甲烷菌联合作用彻底降解2,4,6-TCP。     

Bioremediation 2,4,6,-Trichlorophenol (2,4,6-TCP) by Shigella sp. S2 Isolated from Industrial Dumpsite

A bacterium that utilizes 2,4,6-trichlorophenol (2,4,6-TCP) as a sole source of carbon and energy was isolated from an industrial dumpsite, the bacterium designated as strain S2. Degradation was routinely monitored by observing growth analysis, chloride release assay, and ring cleavage activity and was further confirmed by gas chromatography (GC) analysis. The bacterium was found to degrade up to 90% of 2,4,6-TCP at 1.5 mM concentration. The bacteria were characterized morphologically, biochemically, and by 16S rRNA gene sequencing, which showed 99% sequence similarity with Shigella sp. This is the first report that Shigella sp. was able to degrade 2,4,6-TCP. This strain was found to be novel and a potential 2,4,6-TCP degrader. Further, this strain may be used for bioremediation of 2,4,6-TCP–containing waste in the environment.     

Microbial Transformation of Nitroaromatics in Surface Soils and Aquifer Materials

Microorganisms indigenous to surface soils and aquifer materials collected at a munitions-contaminated site transformed 2,4,6-trinitrotoluene (TNT), 2,4-dinitrotoluene (2,4-DNT), and 2,6-dinitrotoluene (2,6-DNT) to amino-nitro intermediates within 20 to 70 days. Carbon mineralization studies with both unlabeled (TNT, 2,4-DNT, and 2,6-DNT) and radiolabeled ([¹⁴C]TNT) substrates indicated that a significant fraction of these source compounds was degraded to CO₂.     

Loss of the ssrA genome island led to partial debromination in the PBDE respiring Dehalococcoides mccartyi strain GY50

Polybrominated diphenyl ethers (PBDEs), chemicals commonly used as flame‐retardants in consumer products, are emerging persistent organic pollutants that are ubiquitous in the environment. In this study, we report a PBDE‐respiring isolate – Dehalococcoides mccartyi strain GY50, which debrominates the most toxic tetra‐ and penta‐BDE congeners (～1.4 µM) to diphenyl ether within 12 days with hydrogen as the electron donor. The complete genome sequence revealed 26 reductive dehalogenase homologous genes (rdhAs), among which three genes (pbrA1, pbrA2 and pbrA3) were highly expressed during PBDE debromination. After 10 transfers of GY50 with trichloroethene or 2,4,6‐trichlorophenol as the electron acceptor instead of PBDEs, the ssrA‐specific genome island (ssrA‐GI) containing pbrA1 and pbrA2 was deleted from the genome of strain GY50, leading to two variants (strain GY52 with trichloroethene, strain GY55 with 2,4,6‐trichlorophenol) with identically impaired debromination capabilities (debromination of penta‐/tetra‐BDEs ceased at di‐BDE 15). Through analysis of Illumina paired‐end sequencing data, we identified read pairs that probably came from variants that contain ssrA‐GI deletions, indicating their possible presence in the original strain GY50 culture. The two variant strains provide real‐time examples on rapid evolution of organohalide‐respiring organisms. As PBDE‐respiring organisms, GY50‐like strains may serve as key players in detoxifying PBDEs in contaminated environments.     

TNT and nitroaromatic compounds are chemoattractants for Burkholderia cepacia R34 and Burkholderia sp. strain DNT

Nitroaromatic compounds are toxic and potential carcinogens. In this study, a drop assay was used to detect chemotaxis toward nitroaromatic compounds for wild-type Burkholderia cepacia R34, wild-type Burkholderia sp. strain DNT, and a 2,4-dinitrotoluene (2,4-DNT) dioxygenase mutant strain (S5). The three strains are chemotactic toward 2,4,6-trinitrotoluene (TNT), 2,3-DNT, 2,4-DNT, 2,5-DNT, 2-nitrotoluene (NT), 4NT, and 4-methyl-5-nitrocatechol (4M5NC), but not toward 2,6-DNT. Of these, only 2,4-DNT is a carbon and energy source for B. cepacia R34 and Burkholderia sp. strain DNT, and 4M5NC is an intermediate in the 2,4-DNT degradation pathway. It was determined that the 2,4-DNT dioxygenase genes are not required for the chemotaxis for these nitroaromatic compounds because the DNT DDO mutant S5 has a chemotactic response toward 2,4-DNT although 2,4-DNT is not metabolized by S5; hence, 2,4-DNT itself is the chemoattractant. This is the first report of chemotaxis toward TNT, 2,3-DNT, 2,4-DNT, 2,5-DNT, 2NT, 4NT, and 4M5NC.     

Co-metabolism of di- and trichlorobenzoates in a 2-chlorobenzoate-degrading bacterial culture: Effect of the position and number of halo-substituents

The degradative properties towards chlorobenzoates by a 2-chlorobenzoate-degrading mixed culture (2MC) were investigated. Although 2MC did not grow on 2,3,5-; 2,3,6- and 2,4,6-trichlorobenzoates, it was able to completely oxidise 2,3,5-trichlorobenzoate and 2,5-dichlorobenzoate. This was degraded through the intermediate formation of 4-chlorocatechol and 3-cis,cis-chloromuconate, suggesting a dioxygenation in 1,2 position. 4-Chlorobenzoate; 3,4- and 2,6-dichlorobenzoate; 2,4,6- and 2,3,6-trichlorobenzoate did not undergo any co-metabolic transformation, the only 2,4-dichlorobenzoate was scarcely transformed into a dichlorinated phenol as end-product. 2MC was constituted of three prominent species: Stenotrophomonas maltophilia, Cupriavidus necator and Flavobacterium sp. Ring-hydroxylating dioxygenase genes (BenA) were retrieved in S. maltophilia and C. necator, indicating the presence of a “modified ortho pathway” in the culture. On the basis of its degradative properties, 2MC could be a good candidate for use in the removal of ortho- and/or meta-chlorobenzoates that are the major end-products of PCB co-metabolism.     

Novel fluorescent sensor using molecularly imprinted silica microsphere‐coated CdSe@CdS quantum dots and its application in the detection of 2,4,6‐trichlorophenol from environmental water samples

In this study, a high fluorescence sensitivity and selectivity, molecularly imprinted nanofluorescent polymer sensor (MIP@SiO₂@QDs) was prepared using a reverse microemulsion method. 2,4,6‐Trichlorophenol (2,4,6‐TCP) was detected using fluorescence quenching. Tetraethyl orthosilicate (TEOS), quantum dots (QDs) and 3‐aminopropyltriethoxysilane (APTS) were used as cross‐linker, signal sources and functional monomer respectively. The sensor (MIP@SiO₂@QDs) and the non‐imprinted polymer sensor (NIP@SiO₂@QDs) were characterized using infra‐red (IR) analysis, X‐ray diffraction (XRD), transmission electron microscopy (TEM) and scanning electron microscopy (SEM). The selectivity of MIP@SiO₂@QDs was examined by comparing 2,4,6‐TCP with other similar functional substances including 2,4‐dichlorophenol (2,4‐DCP), 2,6‐dichlorophenol (2,6‐DCP) and 4‐chlorophenol (4‐CP). Results showed that MIP@SiO₂@QDs had better selectivity for 2,4,6‐TCP than the other compounds. Fluorescence quenching efficiency displayed a good linear response at the 2,4,6‐TCP concentration range 5–1000 μmol/L. The limit of detection (LOD) was 0.9 μmol/L (3σ, n = 9). This method was equally applicable for testing actual samples with a recovery rate of 98.0–105.8%. The sensor had advantages of simple pretreatment, good sensitivity and selectivity, and wide linear range and could be applied for the rapid detection of 2,4,6‐TCP in actual samples.     

Anaerobic transformation of 2,4,6-trinitrotoluene (TNT)

A sulfate-reducing bacterium using trinitrotoluene (TNT) as the sole nitrogen source was isolated with pyruvate and sulfate as the energy sources. The organism was able to reduce TNT to triaminotoluene (TAT) in growing cultures and cell suspensions and to further transform TAT to still unknown products. Pyruvate, H₂, or carbon monoxide served as the electron donors for the reduction of TNT. The limiting step in TNT conversion to TAT was the reduction of 2,4-diamino-6-nitrotoluene (2,4-DANT) to triaminotoluene. The reduction proceeded via 2,4-diamino-6-hydroxylaminotoluene (DAHAT) as an intermediate. The intermediary formation of DAHAT was only observed in the presence of carbon monoxide or hydroxylamine, respectively. The reduction of DAHAT to triaminotoluene was inhibited by both CO and NH₂OH. The inhibitors as well as DANT and DAHAT significantly inhibited sulfide formation from sulfite. The data were taken as evidence for the involvement of dissimilatory sulfite reductase in the reduction of DANT and/or DAHAT to triaminotoluene. Hydrogenase purified from Clostridium pasteurianum and carbon monoxide dehydrogenase partially purified from Clostridium thermoaceticum also catalyzed the reduction of DANT in the presence of methyl viologen or ferredoxin, however, as the main reduction product DAHAT rather than triaminotoluene was formed. The findings could explain the function of CO as an electron donor for the DANT reduction (to DAHAT) and the concomitant inhibitory effect of CO on triaminotoluene formation (from DAHAT) by the inhibition of sulfite reductase. Triaminotoluene is further anaerobically converted to unknown products by the isolate under sulfate-reducing and by a Pseudomonas strain under denitrifying conditions. Triaminotoluene conversion was also catalyzed in the absence of cells under aerobic conditions by trace elements, especially by Mn²⁺, accompanied by the elimination of ammonia in a stoichiometry of 1 NH₃ released per TAT transformed. The results might be of interest for the bioremediation of wastewater polluted with nitroaromatic compounds.Abbreviations TNT = 2,4,6-Trinitrotoluene DANT - 2,4-DANT = 2,4-Diamino-6-nitrotoluene - 2,6-DANT = 2,6-Diamino-4-nitrotoluene - ADNT = aminodinitrotoluene - 2-ADNT and 4-ADNT amino substituent at positions 2 or 4 - TAT = 2,4,6-Triaminotoluene - DAHAT = 2,4-Diamino-6-hydroxylaminotoluene - MV = Methyl viologen - Fd = Ferredoxin - H₂ase = Hydrogenase - CODH = Carbon monoxide dehydrogenase - Pyr: Fd OR = Pyruvate: ferredoxin oxidoreductase - U = Units = mol of substrate converted per min     

Chemotaxonomische Einordnung der Scheidenschn?bel (Chionidae) in die Vogelsystematik

Zusammenfassung Das Bürzeldrüsensekret des Weißgesicht-Scheidenschnabels(Chionis alba) ist ein Esterwachsgemisch, an dessen Aufbau 2,4-, 2,6-, 2,8-dimethyl- sowie 2,4,6-, 2,4,8-, 2,6,8- und 2,6,10-trimethyl-verzweigte Fettsäuren und n- sowie untergeordnete Mengen 2-, 4-Methyl-und 2,6-Dimethyl- neben Spuren von 2,4,6-Trimethylalkanolen beteiligt sind. Damit weist diese Art nahe Beziehungen zu den Möwen auf und nimmt eine Zwischenstellung zwischen Lariformes und Charadriiformes ein, währendThinocorus etwas weiter entfernt einzuordnen ist. Andere Arten werden mitChionis verglichen.

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The chemotaxonomic position of the Sheathbills(Chionidae)

Summary The uropygial gland secretion of the snowy sheathbill(Chionis alba) is shown to be a mixture of ester waxes composed of 2,4-, 2,6-, 2,8-dimethyl- as well as 2,4,6-, 2,4,8-, 2,6,8- und 2,6,10-trimethyl-substituted fatty acids and n- and minor amounts of 2-, 4-methyl, 2,6-dimethyl- as well as traces of 2,4,6-trimethyl-alkanols. This indicates thatChionis is closely related to the gulls whereasThinocorus is more distant.Chionis should be located between Lariformes and Charadriiformes. Other species are compared withChionis.

     

Isolation from estuarine sediments of a Desulfovibrio strain which can grow on lactate coupled to the reductive dehalogenation of 2,4, 6-tribromophenol

Strain TBP-1, an anaerobic bacterium capable of reductively dehalogenating 2,4,6-tribromophenol to phenol, was isolated from estuarine sediments of the Arthur Kill in the New York/New Jersey harbor. It is a gram-negative, motile, vibrio-shaped, obligate anaerobe which grows on lactate, pyruvate, hydrogen, and fumarate when provided sulfate as an electron acceptor. The organism accumulates acetate when grown on lactate and sulfate, contains desulfoviridin, and will not grow in the absence of NaCl. It will not utilize acetate, succinate, propionate, or butyrate for growth via sulfate reduction. When supplied with lactate as an electron donor, strain TBP-1 will utilize sulfate, sulfite, sulfur, and thiosulfate for growth but not nitrate, fumarate, or acrylate. This organism debrominates 2-, 4-, 2,4-, 2,6-, and 2,4,6-bromophenol but not 3- or 2,3-bromophenol or monobrominated benzoates. It will not dehalogenate monochlorinated, fluorinated, or iodinated phenols or chlorinated benzoates. Together with its physiological characteristics, its 16S rRNA gene sequence places it in the genus Desulfovibrio. The average growth yield of strain TBP-1 grown on a defined medium supplemented with lactate and 2,4,6-bromophenol is 3.71 mg of protein/mmol of phenol produced, and the yield was 1.42 mg of protein/mmol of phenol produced when 4-bromophenol was the electron acceptor. Average growth yields (milligrams of protein per millimole of electrons utilized) for Desulfovibrio sp. strain TBP-1 grown with 2,4,6-bromophenol, 4-bromophenol, or sulfate are 0.62, 0.71, and 1.07, respectively. Growth did not occur when either lactate or 2,4,6-bromophenol was omitted from the growth medium. These results indicate that Desulfovibrio sp. strain TBP-1 is capable of growth via halorespiration.     

Growth yield coefficients of Sphingomonas sp. strain P5 on various chlorophenols in chemostat culture

A polychlorophenol-degrading bacterium, Sphingomonas sp. strain P5, was grown in 2,6-dichlo-rophenol(26-DCP)-limited, 2,3,6-trichlorophenol(236-TCP)-limited, 2,4,6-trichlorophenol(246-TCP)-limited, 2,3,4,6-tetrachlorophenol(2346-TeCP)-limited, and pentachlorophenol(PCP)-limited chemostat cultures at a dilution rate of 0.02 ± 0.002 h⁻¹. The cultures were analyzed for the yield coefficient for growth on chlorophenol during steady-state conditions. The average growth yields coefficients (as carbon conversion efficiencies) were 0.252, 0.230, 0.219, 0.157, and 0.121 mol C mol C⁻¹ for 26-DCP, 236-TCP, 246-TCP, 2346-TeCP, and PCP respectively. The differences in growth yield can be interpreted in terms of the energetics of chlorinated carbon metabolism; i.e. substitution of the phenol moiety reduces the available metabolic energy by one electron per chlorine. The growth yield coefficients on chlorinated phenols were lower than the yield coefficients of heterotrophic growth reported in the literature on non-chlorinated and aliphatic compounds. Metabolic origins for low growth yield coefficients on (chlorinated) aromatic compounds are postulated. Received: 7 April 1997 / Received revision: 7 July 1997 / Accepted: 12 July 1997     

Biodegradation of p-Cresol by Bacillus sp. Strain PHN 1

A bacterium capable of utilizing p-cresol as sole source of carbon and energy was isolated from soil and identified as a Bacillus species. The organism also utilized phenol, o-cresol, m-cresol, 4-hydroxybenzoic acid, and gentisic acid as growth substrates. The organism degraded p-cresol to 4-hydroxybenzoic acid, which was further metabolized by a gentisate pathway, as evidenced by isolation and identification of metabolites and enzyme activities in the cell-free extract. Such a bacterial strain can be used for bioremediation of environments contaminated with phenolic compounds.