The effect of oxidative pretreatment on cellulose degradation by Poria placenta and Trichoderma reesei cellulases

The possible role of hydrogen peroxide in brown-rot decay was investigated by studying the effects of pretreatment of spruce wood and microcrystalline Avicel cellulose with H₂O₂ and Fe²⁺ (Fenton's reagent) on the subsequent enzymatic hydrolysis of the substrates. A crude endoglucanase preparation from the brown-rot fungus Poria placenta, a purified endoglucanase from Trichoderma reesei and a commercial Trichoderma cellulase were used as enzymes. Avicel cellulose and spruce dust were depolymerized in the H₂O₂/Fe²⁺ treatment. Mainly hemicelluloses were lost in the treatment of spruce dust. The effect of the pretreatment on subsequent enzymatic hydrolysis was found to depend on the nature of the substrate and the enzyme preparation used. Pretreatment with H₂O₂/Fe²⁺ clearly increased the amount of enzymatic hydrolysis of spruce dust with both the endoglucanases and the commercial cellulase. In all cases the amount of hydrolysis was increased about threefold. The hydrolysis of Avicel with the endoglucanases was also enhanced, whereas the hydrolysis with the commercial cellulase was decreased. Received: 23 December 1996 / Received revision: 17 April 1997 / Accepted: 19 April 1997     

Inactivation of the plasma membrane ATPase ofSchizosaccharomyces pombe by hydrogen peroxide and by the fenton reagent (Fe2+/H2O2): Nonradicalvs. Radical-induced oxidation

In the absence of added Fe²⁺, the ATPase activity of isolatedSchizosaccharomyces pombe plasma membranes (5–7 μmolP _i per mg protein per min) is moderately inhibited by H₂O₂ in a concentration-dependent manner. Sizable inactivation occurs only at 50–80 mmol/L H₂O₂. The process, probably a direct oxidative action of H₂O₂ on the enzyme, is not induced by the indigenous membrane-bound iron (19.3 nmol/mg membrane protein), is not affected by the radical scavengers mannitol and Tris, and involves a decrease of both theK _m of the enzyme for ATP and theV of ATP splitting. On exposing the membranes to the Fenton reagent (50 μmol/L Fe²⁺ +20 mmol/L H₂O₂), which causes a fast production of HO⁻ radicals, the ATPase is 50–60% inactivated and 90% of added Fe²⁺ is oxidized to Fe³⁺ within 1 min. The inactivation occurs only when Fe²⁺ is added before H₂O₂ and can thus bind to the membranes. The lack of effect of radical scavengers (mannitol, Tris) indicates that HO⁻ radicals produced in the bulk phase play no role in inactivation. Blockage of the inactivation by the iron chelator deferrioxamine implies that the process requires the presence of Fe²⁺ ions bound to binding sites on the enzyme molecules. Added catalase, which competes with Fe²⁺ for H₂O₂, slows down the inactivation but in some cases increases its total extent, probably due to the formation of the superoxide radical that gives rise to delayed HO⁻ production.     

Enhanced Sono-Fenton-Like Oxidation of PAH-Contaminated Soil Using Nano-Sized Magnetite as Catalyst: Optimization with Response Surface Methodology

In the current study, Fe₃O₄ NPs were synthesized and used as catalysts in a sono-Fenton-like process for remediation of polycyclic aromatic hydrocarbon (PAH)-contaminated soil. The effects of operational variables were studied using central composite design (CCD) optimization approach. Results indicated that the effects of H₂O₂ concentration, Fe₃O₄ NPs dosage, ultrasonic power and pH were significant for pyrene removal as a contaminant model. In optimum experimental conditions, including H₂O₂ concentration of 78 mM, Fe₃O₄ NPs dosage of 18 mM, ultrasonic power of 313 W and pH value of 3.46, the observed pyrene removal was obtained 98.37%, which was verified through the additional experimental tests (99.33%). Pseudo first-order kinetic model was well fitted with the experimental data of pyrene removal with significant coefficient of correlation (R²: 0.9672). Accordingly, an unwashed real soil sample containing diffident PAHs (pyrene, flurene, acenaphthylene, phenenthrene, chrysene, etc) was subjected to sono-Fenton-like process based on optimized conditions. The obtained findings revealed that the removal (%) ranged between 37.7% and 85.19% for different PAHs.     

H<Subscript>2</Subscript>S biotreatment with sulfide-oxidizing heterotrophic bacteria

Many industrial activities produce H₂S, which is toxic at high levels and odorous at even very low levels. Chemolithotrophic sulfur-oxidizing bacteria are often used in its remediation. Recently, we have reported that many heterotrophic bacteria can use sulfide:quinone oxidoreductase and persulfide dioxygenase to oxidize H₂S to thiosulfate and sulfite. These bacteria may also potentially be used in H₂S biotreatment. Here we report how various heterotrophic bacteria with these enzymes were cultured with organic compounds and the cells were able to rapidly oxidize H₂S to zero-valence sulfur and thiosulfate, causing no apparent acidification. Some also converted the produced thiosulfate to tetrathionate. The rates of sulfide oxidation by some of the tested bacteria in suspension, ranging from 8 to 50 µmol min^?1 g^?1 of cell dry weight at pH 7.4, sufficient for H₂S biotreatment. The immobilized bacteria removed H₂S as efficiently as the bacteria in suspension, and the inclusion of Fe₃O₄ nanoparticles during immobilization resulted in increased efficiency for sulfide removal, in part due to chemical oxidation H₂S by Fe₃O₄. Thus, heterotrophic bacteria may be used for H₂S biotreatment under aerobic conditions.     

Metabolite repression inhibits degradation of benzo[a]pyrene and dibenz[a,h]anthracene by Stenotrophomonas maltophilia VUN 10,003

Large inocula of Stenotrophomonas maltophilia VUN 10,003 were used to investigate bacterial degradation of benzo[a]pyrene and dibenz[a,h]anthracene. Although strain VUN 10,003 was capable of degrading 10–15 mg l⁻¹ of the five-ring compounds in the presence of pyrene after 63 days, further addition of pyrene after degradation of the five-ring polycyclic aromatic hydrocarbons (PAHs) ceased did not stimulate significant decreases in the concentration of benzo[a]pyrene or dibenz[a,h]anthracene. However, pyrene was degraded to undetectable levels 21 days after its addition. The amount of benzo[a]pyrene and dibenz[a,h]anthracene degraded by strain VUN 10,003 was not affected by the initial concentration of the compounds when tested at 25–100 mg l⁻¹, by the accumulation of by-products from pyrene catabolism or a loss of ability by the cells to catabolise benzo[a]pyrene or dibenz[a,h]anthracene. Metabolite or by-product repression was suspected to be responsible for the inhibition: By-products from the degradation of the five-ring compounds inhibited their further degradation. Journal of Industrial Microbiology & Biotechnology (2002) 28, 88–96 DOI: 10.1038/sj/jim/7000216 Received 30 January 2001/ Accepted in revised form 10 October 2001     

Degradation of eight highly condensed polycyclic aromatic hydrocarbons by Pleurotus sp. Florida in solid wheat straw substrate

The degradation of eight unlabeled highly condensed polycyclic aromatic hydrocarbons (PAH) and the mineralization of three ¹⁴C-labeled PAH by the white-rot fungus Pleurotus sp. Florida was investigated. Three concentrations containing 50, 250 or 1250 μg each unlabeled PAH/5 g straw were added to sterile sea sand. Selected treatments were added subsequently with ¹⁴C-labeled pyrene, benzo[a]anthracene or benzo[a]pyrene. The PAH-loaded sea sand was then mixed into straw substrate and incubated. The disappearance of the unlabeled four-to six-ring PAH: pyrene, benzo[a]anthracene, chrysene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, dibenz[a,h]anthracene and benzo[ghi]perylene, was determined by high-performance liquid chromatography. After 15 weeks of incubation, the recoveries were less than 25% for initial amounts of 50 μg (controls above 85%). The recoveries of unlabeled PAH increased in the inoculated samples with increasing concentrations applied. No correlation could be determined between the number of condensed rings of the PAH and the recoveries of added PAH. Pleurotus sp. Florida mineralized 53% [¹⁴C]pyrene, 25% [¹⁴C]benzo[a]anthracene and 39% [¹⁴C]benzo[a]pyrene to ¹⁴CO₂ in the presence of eight unlabeled PAH (50 μg applied) within 15 weeks. During the course of cultivation, Pleurotus sp. Florida degraded more than 40% of the wheat straw substrate. Variation of the initial concentration of PAH did not influence the extent of degradation of the organic matter. Received: 16 December 1996 / Received revision: 17 March 1997 / Accepted: 22 March 1997     

Removal and transformation of high molecular weight polycyclic aromatic hydrocarbons in water by live and dead microalgae

The removal and transformation of seven high molecular weight polycyclic aromatic hydrocarbons (PAHs), namely benz[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, dibenzo[a,h]anthracene, indeno[1,2,3-c,d]pyrene and benzo[g,h,i]perylene, by a freshwater microalga Selenastrum capricornutum under gold and white light irradiation was studied. The two light sources did not result in significant differences in the biodegradation of the selected PAHs in live algal cells, but white light was more effective in promoting photodegradation than was gold light in dead cells. The removal efficiency of seven PAHs, as well as the difference between live and dead microalgal cells, was PAH compound-dependent. Benz[a]anthracene and benzo[a]pyrene were highly transformed in live and dead algal cells, and dead cells displayed greater transformation levels than live cells. Further investigation comparing the transformation of single PAH compound, benzo[a]pyrene, by S. capricornutum and another green microalgal species, Chlorella sp., demonstrated that the transformation in dead cells was similar, indicating the process was algal-species independent. Dead algal cells most likely acted as a photosensitizer and accelerated the photodegradation of PAHs.     

Mechanisms of Saccharomyces Cerevisiae PMA1 H+-ATPase inactivation by Fe2+, H2O2 and Fenton reagents

Although considerably more oxidation-resistant than other P-type ATPases, the yeast PMA1 H⁺-ATPase of Saccharomyces cerevisiae SY4 secretory vesicles was inactivated by H₂O₂, Fe²⁺, Fe- and Cu-Fenton reagents. Inactivation by Fe²⁺ required the presence of oxygen and hence involved auto-oxidation of Fe²⁺ to Fe³⁺. The highest Fe^2- (100 μM) and H₂O₂ (100 mM) concentrations used produced about the same effect. Inactivation by the Fenton reagent depended more on Fe²⁺ content than on H₂O₂ concentration, occurred only when Fe²⁺ was added to the vesicles first and was only slightly reduced by scavengers (mannitol, Tris, NaN₃, DMSO) and by chelators (EDTA, EGTA, DTPA, BPDs, bipyridine, 1, 10-phenanthroline). Inactivation by Fe- and Cu- Fenton reagent was the same; the identical inactivation pattern found for both reagents under anaerobic conditions showed that both reagents act via OH^·. The lipid peroxidation blocker BHT prevented Fenton-induced rise in lipid peroxidation in both whole cells and in isolated membrane lipids but did not protect the H⁺-ATPase in secretory vesicles against inactivation. ATP partially protected the enzyme against peroxide and the Fenton reagent in a way resembling the protection it afforded against SH-specific agents. The results indicate that Fe²⁺ and the Fenton reagent act via metal-catalyzed oxidation at specific metal-binding sites, very probably SH-containing amino acid residues. Deferrioxamine, which prevents the redox cycling of Fe²⁺, blocked H⁺-ATPase inactivation by Fe²⁺ and the Fenton reagent but not that caused by H₂O₂, which therefore seems to involve a direct non-radical attack. Fe-Fenton reagent caused fragmentation of the H⁺-ATPase molecule, which, in Western blots, did not give rise to defined fragments bands but merely to smears.     

Pyrene Biodegradation by Bacillus spp. Isolated from Coal Tar–Contaminated Soil

Aerobic, mesophilic bacteria from coal tar–contaminated soil were analyzed for pyrene utilization capacity and identified by 16S ribosomal DNA sequencing as members of three genera: Bacillus spp., Pseudomonas sp., and Rhodococcus sp. The soil contained nine different hazardous polyaromatic hydrocarbons (PAHs): benzo[g, h, i]perylene, dibenzo[a, h]anthracene, indeno[1,2,3-c,d]pyrene, pyrene, acenaphthylene, fluorene, phenanthrene, benzo[k]fluoranthene, and benzo[b]fluoranthene. Bacillus spp. (PK-6) MTCC 1005 showed 56.4% utilization of pyrene (C₁₆H₁₀) (50 μg ml^?1) in 4 days, with growth associated biosurfactant activity and resulted in the formation of five new intermediates: phenanthrene (C₁₄H₁₀), 9,10-diphenylphenanthrene (C₂₆H₁₈), 9-methoxyphenanthrene (C₁₅H₁₂O), 5,6,7,8-tetrahydro-1-naphthoic acid (C₁₁H₁₂O₂), and 1,6,7-trimethylnaphthalene (C₁₃H₁₄). The results suggested that Bacillus spp. could be found suitable for practical field application for effective in situ PAH bioremediation.     

Spontaneous and radical-induced plasma membrane lipid peroxidation in differently oxidant-sensitive yeast species and its suppression by antioxidants

Formation of thiobarbituric acid-reactive substances (TBRS; nmol/mg lipids) indicative of lipid peroxidation was measured in whole cells and in isolated plasma membrane lipids from three yeast species differing in oxidant sensitivity (Schizosaccharomyces pombe, Saccharomyces cerevisiae andRhodotorula glutinis) after exposure to the Fenton reagent, Fe^II, H₂O₂,tert-butyl hydroperoxide (TBHP) and azo compounds (AAPH, ACHN). In whole cells, spontaneous TBRS formation rose in the sequenceS. pombe<S. cerevisiae<R. glutinis (1:∼5:∼7). Oxidants increased the TBRS production 13–18 fold in the sequence Fe^II∼TBHP>AAPH∼ACHN∼Fe-Fenton>H₂O₂. This increase need not be solely due to increased lipid peroxidation. In isolated plasma membrane lipids from all three species, the spontaneous TBRS production referred to 1 mg lipids was 9–13-fold higher than in whole cells. InS. pombe lipids, only TBHP increased the TBRS production. In lipids fromS. cerevisiae andR. glutinis, all added oxidants increased the spontaneous TBRS production 2–3 times in the sequence TBHP>ACHN>AAPH>Fe^II>Fe-Fenton>H₂O₂. Oxidant-induced TBRS production in both whole cells and isolated membrane lipids was partially suppressed by the lipid peroxidation inhibitors 2,6-di-tert-butyl-4-methylphenol (“butylated hydroxytoluene”; BHT) and the newly synthesized PYA12 compound. Both agents were more effective in isolated lipids than in whole cells and against OH-producing than against ROO-or RO-producing oxidants. Yeast membrane lipids, which are generally poor in polyunsaturated fatty acids, are thus subject to perceptible lipid peroxidation.     

Evaluation of chemical pretreatment of contaminated soil for improved PAH bioremediation

The efficiency of several chemical treatments as potential enhancers of the biodegradation of polycyclic aromatic hydrocarbons (PAHs) in contaminated soil was evaluated by analyzing the mineralization of ¹⁴C-labeled phenanthrene, pyrene, and benzo(a)pyrene. The effect of nonionic surfactants with Fenton oxidation and combinations of surfactants with the Fenton oxidation was evaluated in a microtiter plate assay. The surfactants selected for the study were Tween 80, Brij 35, Tergitol NP-10, and Triton X-100. The addition of Fentons reagent significantly enhanced the mineralization of pyrene at the two concentrations studied: 2.8 M H₂O₂ with 0.1 M FeSO₄ and 0.7 M H₂O₂ with 0.025 M FeSO₄. Phenanthrene mineralization was also positively induced by the Fenton treatments. However, none of the treatments had a significant effect on benzo(a)pyrene mineralization. Surfactant additions at concentrations of 20% and 80% of the aqueous critical micelle concentration did not significantly affect the mineralization rates. When surfactant addition was combined with the Fenton oxidation, reduced mineralization rates were obtained when compared with mineralization after Fentons treatment alone. The results indicate that the addition of Fentons reagent may enhance the mineralization of PAHs in contaminated soil, whereas the addition of surfactants has no significant beneficial effect. The efficiency of the Fenton oxidation may decrease when surfactants are added simultaneously with Fentons reagent to contaminated soil.     

Hydrogen peroxide involvement in formation and development of adventitious roots in cucumber

Hydrogen peroxide (H₂O₂), an active oxygen species, is widely generated in many biological systems. The present study demonstrates that H₂O₂ was generated in seedling explants after the primary roots were removed, and it mediates the auxin response prior to adventitious root formation in cucumber (Cucumis sativus L. Ganfeng 8). When compared with the controls, treatment of cucumber seedling explants after primary roots removal with either 20–40 mM H₂O₂ or 10 μM IAA significantly increased the number of adventitious roots, and treatment with 10–50 mM H₂O₂ significantly increased the fresh weight of adventitious roots. The effects of H₂O₂ on promoting the formation and growth of adventitious roots were eliminated by 2 mM ascorbic acid, 100 U CAT or 1 μM DPI, and the effects of IAA were eliminated by 4 mM ascorbic acid, 100 U CAT or 5 μM DPI. Treatment with either 4 mM ascorbic acid or 1–5 μM DPI inhibited the formation and growth of adventitious roots, and these inhibitory effects were partly reversed by exogenous H₂O₂.Furthermore, a higher concentration of endogenous H₂O₂ was detected in seedling explants 3 h after the primary roots were removed. However, in 10 μM DPI-treated seedling explants, the concentration of endogenous H₂O₂ was markedly reduced by DPI. Results obtained suggest that H₂O₂ may function as a signaling molecule, involved in the formation and development of adventitious roots in cucumber.     

Aquopentacyanoferrate (II): an effective probing electron donor in the conversion of oxyhemoglobin to methemoglobin and peroxide.

HbA O₂ reacts readily with Fe^II(CN)₅H₂O^3? to form aquometHb and peroxide via a second order process: rate=k[HbO₂][Fe^II(CN)₅H₂O^3?]. A slight enchancement in the rate of metHb formation due to the H₂O₂ produced can be prevented by addition of catalase. The reaction is free from complications exhibited by other reductants. The hexacyanide, ferrocyanide, reacts with HbA O₂ but at only ca. 0.02% the rate and with formation of cyanometHb. Reductants such as phenols and sulfa drugs may produce radicals that can enter into side reactions. Fe^II(CN)₅H₂O^3? shows promise as an effective probing reagent for the characterization of H₂O₂ production from oxygenated heme and other proteins.     

Mutagenicity of non-K-region diols and diol-epoxides of benz(a)anthracene and benzo(a)pyrene in S. typhimurium TA 100

When incubated with a 9,000 x g rat-liver supernatant, benzo(a)pyrene 7,8-diol and benz(a)anthracene 8,9-diol were more active than the parent hydrocarbons in inducing his⁺ revertant colonies of S. typhimurium TA 100. Benzo(a) pyrene 9,10-diol was less active than benzo(a)pyrene; the K-region diols, benz(a)anthracene 5,6-diol and benzo(a)pyrene 4,5-diol, were inactive. None of the diols was active when the cofactors for the microsomal mono-oxygenase were omitted. The diol-epoxides benzo(a)pyrene 7,8-diol 9,10-oxide, benz(a)anthracene 8,9-diol 10,11-oxide and 7-methylbenz(a)anthracene 8,9-diol 10,11-oxide and the K-region epoxides, benzo(a)pyrene 4,5-oxide and benz(a)anthracene 5,6-oxide, were mutagenic without further metabolism.     

Oligonucleotides are potent antioxidants acting primarily through metal ion chelation

We report on a rather unknown feature of oligonucleotides, namely, their potent antioxidant activity. Previously, we showed that nucleotides are potent antioxidants in Fe^II/Cu^I/II–H₂O₂ systems. Here, we explored the potential of 2′-deoxyoligonucleotides as inhibitors of the Fe^II/Cu^I/II-induced ·OH formation from H₂O₂. The oligonucleotides [d(A)_5,7,20; d(T)₂₀; (2′-OMe-A)₅] proved to be highly potent antioxidants with IC₅₀ values of 5–17 or 48–85 μM in inhibiting Fe^II/Cu^I- or Cu^II-induced H₂O₂ decomposition, respectively, thus representing a 40–215-fold increase in potency as compared with Trolox, a standard antioxidant. The antioxidant activity is only weakly dependent on the oligonucleotides’ length or base identity. We analyzed by matrix-assisted laser desorption/ionization time of flight mass spectrometry and ¹H-NMR spectroscopy the composition of the d(A)₅ solution exposed to the aforementioned oxidative conditions for 4 min or 24 h. We concluded that the primary (rapid) inhibition mechanism by oligonucleotides is metal ion chelation and the secondary (slow) mechanism is radical scavenging. We characterized the Cu^I–d(A)₅ and Cu^II–d(A)₇ complexes by ¹H-NMR and ³¹P-NMR or frozen-solution ESR spectroscopy, respectively. Cu^I is probably coordinated to d(A)₅ via N1 and N7 of two adenine residues and possibly also via two phosphate/bridging water molecules. The ESR data suggest Cu^II chelation through two nitrogen atoms of the adenine bases and two oxygen atoms (phosphates or water molecules). We conclude that oligonucleotides at micromolar concentrations prevent Fe^II/Cu^I/II-induced oxidative damage, primarily through metal ion chelation. Furthermore, we propose the use of a short, metabolically stable oligonucleotide, (2′-OMe-A)₅, as a highly potent and relatively long lived (t _1/2 ~ 20 h) antioxidant.     

Mechanism of dithionite reduction of the R2 protein of E. coli and mouse ribonucleotide reductase: evidence for reduction of FeIII 2 prior to the tyrosyl radical

 Dithionite has been found to reduce directly (without mediators) the Escherichia coli R2 subunit of ribonucleotide reductase. With dithionite (∼10 mM) in large excess, the reaction at 25  °C is complete in ∼10 h. Preparations of E. coli R2 have an Fe^III ₂ (met-R2) component in this work at ∼40% levels, alongside the fully active enzyme Fe^III ₂ . . . Tyr*, which has a tyrosyl radical at Tyr-122. In the pH range studied (7–8) the kinetics are biphasic. Rate laws for both phases give [S₂O₄ ^2–] and not [S₂O₄ ^2–]^1/2 dependencies, and saturation kinetics are observed for the first time in R2 studies. No dependence on pH was detected. The kinetics (25  °C) of the first phase are reproduced in separate experiments using only met-R2, with association of S₂O₄ ^2– to met-R2, K=330 M^–1, occurring prior to electron transfer, k _et=4.8×10^–4 s^–1, I=0.100 M (NaCl). The second phase assigned to the reaction of Fe^III ₂ . . . Tyr* with S₂O₄ ^2– gives K=800 M^–1 and k _et=5.6×10^–5 s^–1. Bearing in mind the substantially smaller reduction potential for Fe^III ₂ compared to Tyr*, this is a quite remarkable finding, with implications similar to those already reported for the reaction of R2 with hydrazine, but with additional information provided by the saturation kinetics. The similarity in rates for the two phases (∼fourfold difference) suggests that reduction of Fe^III ₂ is occurring in both cases, and since S₂O₄ ^2– is involved a two-equivalent change is proposed with the formation of Fe^II ₂ . . . Tyr* in the case of active R2. As a sequel to the second phase, intramolecular reduction of the strongly oxidising Tyr* by the Fe^II ₂ is rapid, and further decay of Fe^IIFe^III is also fast. There is no stable mouse met-R2 form, and the single-phase reaction with dithionite gives saturation kinetics with K=208 M^–1 and k _et=1.7±10^–3 s^–1. Mechanistic implications, including the applicability of a pathway for electron transfer via Fe_A, are considered. Received: 25 February 1998 / Received: 20 August 1998     

Reversible sporicidal action of cuprous ions

At 10 mM, Cu⁺ was highly protective against killing of spores of Bacillus megaterium ATCC 19213 by H₂O₂, while at higher concentrations, from 15–100 mM, killing was augmented. In contrast, Cu²⁺, Fe²⁺, Fe³⁺, Co²⁺ or Co³⁺ ions acted only protectively. Cu⁺ itself was sporicidal in the absence of H₂O₂ or ascorbate, and its sporicidal action did not depend on generation of highly reactive oxygen species. It appeared that killing involved either inhibition of germination or copper toxicity to germinated cells in that Cu⁺-inactivated spores did not germinate readily but chemical decoating of the cells prior to plating on a solid medium resulted in reversal of the sporicidal effect. Received 12 July 1996/ Accepted in revised form 03 November 1996     

Ferroglobus placidus gen. nov., sp. nov., a novel hyperthermophilic archaeum that oxidizes Fe2+ at neutral pH under anoxic conditions

A novel coccoid, anaerobic, Fe²⁺-oxidizing archaeum was isolated from a shallow submarine hydrothermal system at Vulcano, Italy. In addition to ferrous iron, H₂ and sulfide served as electron donors. NO₃ ^– was used as electron acceptor. In the presence of H₂, also S₂O₃ ^2– could serve as electron acceptor. The isolate was a neutrophilic hyperthermophile that grew between 65° C and 95° C. It represents a novel genus among the Archaeoglobales that we name Ferroglobus. The type species is Ferroglobus placidus (DSM 10642). Received: 7 March 1996 / Accepted: 4 September 1996     

Purification of polyhydroxybutyrate produced by <Emphasis Type="Italic">Burkholderia cepacia</Emphasis> IPT64 through a chemical and enzymatic route

This work aimed at the study of purification of biopolymers produced by Burkholderia cepacia IPT64, through a chemical attack like an adjuvant procedure through chemical and enzymatic route. Enzymatic lysis using protease was run on an enzyme/cell ratio of 0.02. Chemical attacks were performed as pre or post-treatment for enzymatic attacks, using sodium dodecyl sulphate or hydrogen peroxide. The same chemicals and procedures were used alone as a control. Fenton’s reagent was also tested as a chemical treatment. Using only one of the chemicals H₂O₂, Fenton’s reagent or SDS, the purity increase achieved values of 14%, 16% or 23%, respectively. When H₂O₂ or SDS were used as pre-treatment for the enzymatic attack, the results of purity increase achieved values of 58% for H₂O₂/cell ratio between 0.60 and 1.20, and 57% when SDS/cell ratio at 0.56 was used. In the case when H₂O₂ or SDS were used as post-treatment for the enzymatic attack, results of purity increase achieved 60% when the H₂O₂ was used at H₂O₂/cell ratio ranging between 0.30 and 0.60 and 71% when SDS was used at a ratio SDS/cell of 0.56.     

Degradation of polycyclic aromatic hydrocarbons in soil by a two-step sequential treatment

The objectives of this work were to isolate the microorganisms responsible for a previously observed degradation of polycyclic aromatic hydrocarbons (PAH) in soil and to test a method for cleaning a PAH-contaminated soil. An efficient PAH degrader was isolated from an agricultural soil and designated as Mycobacterium LP1. In liquid culture, it degraded phenanthrene (58%), pyrene (24%), anthracene (21%) and benzo(a)pyrene (10%) present in mixture (initial concentration 50 μg ml⁻¹ each) and phenanthrene (92%) and pyrene (94%) as sole carbon sources after 14 days of incubation at 30°C. In soil, Mycobacterium LP1 mineralised ¹⁴C-phenanthrene (45%) and ¹⁴C-pyrene (65%) after 10 days. The good ability of this Mycobacterium was combined with the benzo(a)pyrene oxidation effect obtained by 1% w/w rapeseed oil in a sequential treatment of a PAH-spiked soil (total PAH concentration 200 mg kg⁻¹). The first step was incubation with the bacterium for 12 days and the second step was the addition of the rapeseed oil after this time and a further incubation of 22 days. Phenanthrene (99%), pyrene (95%) and anthracene (99%) were mainly degraded in the first 12 days and a total of 85% of benzo(a)pyrene was transformed during the whole process. The feasibility of the method is discussed.