Degradation and dechlorination of low-chlorinated biphenyls by a three-membered bacterial co-culture

A Pseudomonas sp. strain, designated CPE1, was found to be capable of completely mineralizing 4-chlorobiphenyl via 4-chlorobenzoate and of partially dechlorinating 3,4-dichlorobiphenyl in the presence of biphenyl. A three-membered bacterial consortium, designated ECO3, prepared by combining CPE1 with two chlorobenzoate (CBA)-degrading strains, was capable of extensively degrading and dechlorinating all the monochlorinated biphenyls and several dichlorinated biphenyls in the presence of bipheny. Both CPE1 and ECO3 were capable of co-metabolizing several low-chlorinated biphenyl congeners of Fenclor 42 in the presence of biphenyl; however, only in ECO3 cultures were high degradation rates and chloride release observed. The higher rate of degradation and mineralization of some polychlorinated biphenyls (PCBs) of Fenclor 42 due to the concerted action of ECO3 members both on PCBs and CBAs suggested that the removal of CBAs from the culture medium may favour PCB degradation, and, therefore, that CBAs may be ivollved in the regulation of the degradation process of several chlorinated biphenyl congeners.Correspoeence to: F. Fava     

Epidemiological study of sporotrichosis and histoplasmosis in captive Latin American wild mammals,São Paulo,Brazil

Sporotrichosis and histoplasmosis are deep mycosis with a high incidence in human beings in Brazil. In domestic animals histoplasmosis has been described only in dogs, but the occurence of sporotrichosis among domestic animals in Brazil has been described in dogs, cats, mules and asses. There is also a case of this disease reported in a chimpanzee (Pan troglodites). The purpose of this research was to perform an epidomiological study of these mycoses using delayed hypersensitivity tests (histoplasmin and sporotrichin) in Latin American wild mammals. This research was assayed using 96 healthy animals at Parque Zoológico de São Paulo, Brazil: Primates: 33Cebus apella — weeping-capuchin and 16Callithrix jacchus — marmoset; Procyonidae: 37Nasua nasua — coatimundi and 10 Felidae (Panthera onca — jaguar;Felis pardalis — ocelotFelis wiedii — margay;Felis tigrina — wild cat). For intradermic tests, the following antigens were used:Sporothrix schenkii cell suspension (sporotrichin, histoplasmin-filtrate),Histoplasma capsulatum cell suspension (histoplasmin), andHistoplasma capsulatum (polysaccharide). The positivity to histoplasmin was 44.79% (Cebidae 15.15%; Callithricidae 6.25%; Procyonidae 86.49% and Felidae 50.00%, respectively). With respect to sporotrichin, 30.21% (Cebidae 6.06%, Callithricidae 0.0%; Procyonidae 64.86% and Felidae 30.00% respectively). The pattern of infection is similar to that shown by human beings and this may suggest that these animals could be involved in the epidemiologic chain of sporotrichosis and histoplasmosis, the second most prevalent human deep mycoses in Brazil. It is important to point out the absence of similar studies in Latin American wild animals.     

Inhibition of Mitochondrial ATP Generation by Nitric Oxide Switches Apoptosis to Necrosis

Under pathological conditions, the mode of cell death, apoptosis or necrosis, is relevant for the subsequent fate of the tissue. Cell demise may be shaped by endogenous mediators such as nitric oxide (NO) which interfere with subroutines of the death program. Here we show that apoptosis of Jurkat cells elicited by either staurosporine (STS) or anti-CD95 antibodies in glucose-free medium is converted to necrosis by NO donors. In the presence of NO, release of mitochondrial cytochrome c was delayed and activation of execution caspases was prevented. Stimulated cells died nonetheless. The switch in the mode of cell death was due to NO-dependent failure of mitochondrial energy production. Restoration of intracellular ATP by glucose supplementation recovered the cells' ability to activate caspases and undergo apoptosis. In this system, the apoptosis/necrosis conversion promoted by NO was not mediated by cyclic guanosine monophosphate-dependent mechanisms, poly-(ADP-ribose)-polymerase (PARP) activation, or inhibition of caspases due to S-nitrosylation and glutathione depletion. In contrast, depleting intracellular ATP with rotenone, an inhibitor of mitochondrial complex I mimicked the effect of NO. The findings presented here suggest that NO can decide the shape of cell death by lowering intracellular ATP below the level required to allow the coordinated execution of apoptosis.     

哈尔滨西郊赤狐冬季巢区的初步研究

本文利用雪地跟踪方法对哈尔滨西郊5只赤狐在1985-1986年冬季的巢区做了观察。结果表明,5只狐对巢区内各部分使用的强度是不等的,对巢区中部的某些地块使用强度要高于对外围的使用,并具有明显的方向性。5个巢区的平均活动半径为320±68米至557±82米,面积为1.44-4.O9平方公里,线性指数为1.079至2。5只狐相邻距离约1000米。     

Nonglucosylated oligosaccharides are transferred to protein in MI8-5 Chinese hamster ovary cells

A CHO mutant MI8-5 was found to synthesize Man9-GlcNAc2-P-P-dolichol rather than Glc3Man9GlcNAc2-P-P-dolichol as the oligosaccharide-lipid intermediate in N-glycosylation of proteins. MI8-5 cells were incubated with labeled mevalonate, and the prenol was found to be dolichol. The mannose-labeled oligosaccharide released from oligosaccharide-lipid of MI8-5 cells was analyzed by HPLC and alpha-mannosidase treatment, and the data were consistent with a structure of Man9GlcNAc2. In addition, MI8-5 cells did not incorporate radioactivity into oligosaccharide- lipid during an incubation with tritiated galactose, again consistent with MI8-5 cells synthesizing an unglucosylated oligosaccharide-lipid. MI8-5 cells had parental levels of glucosylphosphoryldolichol synthase activity. However, in two different assays, MI8-5 cells lacked dolichol- P-Glc:Man9GlcNAc2-P-P-dolichol glucosyltransferase activity. MI8-5 cells were found to synthesize glucosylated oligosaccharide after they were transfected with Saccharomyces cerevisiae ALG 6, the gene for dolichol-P-Glc:Man9GlcNAc2-P-P-dolichol glucosyltransferase. MI8-5 cells were found to incorporate mannose into protein 2-fold slower than parental cells and to approximately a 2-fold lesser extent.      

Dehalogenation of dichloroethene in a contaminated soil: fatty acids and alcohols as electron donors and an apparent requirement for tetrachloroethene

Environmental soil contamination at an industrial site in Marion, Ohio (USA) with tetrachloroethene (perchloroethene, PCE) resulted in residual cis-1, 2-dichloroethene (DCE) contamination that had not declined after more than 15 years. Microcosm slurries containing 2.6% soil from this site were supplemented with different electron donors, i.e., individual fatty acids or alcohols. None of the microcosms supported complete DCE dechlorination, unless PCE was added to the microcosm at initiation. The addition of fresh PCE resulted in the dehalogenation of PCE to DCE in the microcosms supplemented with fatty acids having an even number of carbon atoms (acetate, butyrate, and caproate), but not in those with an odd number of carbon atoms (formate, propionate, and valerate), where negligible or no activity was detected. No significant further DCE degradation was observed in any of the microcosms supplied with fatty acids as electron donors. Microcosms supplemented with freshly added PCE bioconverted PCE to DCE and completely dehalogenated both the ex-novo and soil-supplied DCE within 60 days, but only if alcohols having an even number of carbon atoms (ethanol or butanol) were also added as electron donors. Odd-numbered alcohols either did not produce dehalogenation (as with methanol) or only dehalogenated PCE to DCE (as with propanol).     

Soya lecithin effects on the aerobic biodegradation of polychlorinated biphenyls in an artificially contaminated soil

The effects of the phytogenic surfactant soya lecithin (SL) on the aerobic biodegradation of polychlorinated biphenyls (PCBs) spiked into a synthetic soil were studied. Soil was spiked with both biphenyl (4 g/kg) and Fenclor 42 (1,000 mg/kg) and treated in aerobic batch slurry-phase microcosms (17.5% w/v). Microcosms were prepared either with or without the exogenous aerobic PCB-dechlorinating bacterial co-culture ECO3 (inoculum:10(8) CFU/mL). In some inoculated microcosms, SL was added at 15 or 30 g/kg. Indigenous bacteria having the capability of metabolizing biphenyl and 2-chlorobenzoic acid were found to develop in the microcosms during the experiment, and were responsible for the significant PCB biodegradation and dechlorination observed in the uninoculated controls. The addition of ECO3 bacteria resulted in only a slight PCB biodegradation increase. In the presence of SL, a higher availability of biphenyl- and chlorobenzoic acid-degrading bacteria and higher PCB biodegradation and dechlorination yields were observed; the effects increased proportionally with the concentration of the applied SL. A significant decrease of soil ecotoxicity was also revealed in SL-supplemented microcosms. At both concentrations, SL was found to be a good carbon source for both the indigenous and ECO3 bacteria, as well as a product capable of enhancing the PCB bioavailability in the microcosms.     

Aerobic mineralization of chlorobenzoates by a natural polychlorinated biphenyl-degrading mixed bacterial culture

A natural mixed aerobic bacterial culture, designated MIXE1, was found to be capable of degrading several low-chlorinated biphenyls when 4-chlorobiphenyl was used as a co-substrate. MIXE1 was capable of using all the three monochlorobenzoate (CBA) isomers tested as well as 2,5-, 3,4- and 3,5-dichlorobenzoate (dCBA) as the sole carbon and energy source. During MIXE1 growth on these substrates, a nearly stoichiometric amount of chloride was released: 0.5 g/l of each chlorobenzoate was completely mineralized by MIXE1 after 2 or 3 days of culture incubation. Two strains, namely CPE2 and CPE3, were selected from MIXE1: CPE2, referred to the Pseudomonas genus, was found to be capable of totally degrading both 2-CBA and 2,5-dCBA, whereas Alcaligenes strain CPE3 was capable of mineralizing 3-, 4-CBA and 3,4-dCBA. Substrate uptake studies carried out with whole cells of strain CPE2 suggested that 2-CBA was metabolized through catechol, while 2,5-dCBA was degraded via 4-chlorocatechol. 3-CBA, 4-CBA, and 3,4-dCBA appeared to be degraded through 3,4-dihydroxybenzoate by the CPE3 strain. MIXE1, which is capable of degrading several chlorobenzoates, should therefore be able to mineralize a number of low-chlorinated congeners of simple and complex polychlorinated biphenyl mixtures. Correspondence to: F. Fava