RESUMEN
Di(2-ethylhexyl) phthalate (DEHP) is a widely used plasticizer, which is considered an endocrine disrupting pollutant. Growth kinetics and esterases activity by biochemical tests and polyacrylamide gel electrophoresis were characterized for Fusarium culmorum grown in DEHP-supplemented (1000â¯mg/L) medium as the only carbon source and in control medium with glucose. Intermediate compounds of biodegraded DEHP were identified by GC-MS. F. culmorum degraded 92% of DEHP within 36â¯h. DEHP was degraded to butanol, hexanal, catechol and acetic acid. It is suggested that the first two compounds would transform into butanediol and the last two would enter into the Krebs cycle and would be mineralized to CO2 and H2O. DEHP induced eight esterase isoforms, which were different to those constitutive isoforms produced in the control medium. It is suggested that five enzymes (25.7, 29.5, 31.8, 97.6 and 144.5â¯kDa) detected during the first 36â¯h be involved in the primary biodegradation of DEHP. The rest of the enzymes (45.9, 66.6 and 202.9â¯kDa) might be involved in the final steps for DEHP metabolism. F. culmorum has a promising practical application in the treatment of DEHP-contaminated environments because it can secrete specific esterase to breakdown high concentrations of DEHP in a short period of time. This research represents the first approach for the study of esterase involved in the DEHP degradation by fungi using this phthalate as the sole source of carbon and energy.
Asunto(s)
Dietilhexil Ftalato/análisis , Disruptores Endocrinos/análisis , Contaminantes Ambientales/análisis , Fusarium/crecimiento & desarrollo , Plastificantes/análisis , Biodegradación Ambiental , Esterasas/metabolismo , Fusarium/enzimología , CinéticaRESUMEN
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 (t1/2) 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. t1/2 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.
Asunto(s)
Dibutil Ftalato/metabolismo , Contaminantes Ambientales/metabolismo , Pleurotus/metabolismo , Biodegradación Ambiental , Pleurotus/crecimiento & desarrolloRESUMEN
Dibutyl phthalate (DBP) is a widely used plasticizer, whose presence in the environment as a pollutant raises concern because of its endocrine-disrupting toxicity. Growth kinetics, glucose uptake, biodegradation constant of DBP (k), half-life of DBP biodegradation (t1/2) and percentage of removal efficiency (%E) were evaluated for Fusarium culmorum grown on media containing glucose and different concentrations of DBP (500 and 1000 mg/l). Intermediate compounds of biodegraded DBP were identified by GC-MS and a novel DBP biodegradation pathway was proposed on the basis of the intermolecular flow of electrons of the intermediates identified using quantum chemical modeling. F. culmorum degraded 99% of both 1000 and 500 mg of DBP/l after an incubation period of 168 and 228 h, respectively. %E was 99.5 and 99.3 for 1000 and 500 mg of DBP/l, respectively. The k was 0.0164 and 0.0231 h-1 for 500 and 1000 mg of DBP/l, respectively. DBP was fully metabolized to fumaric and malic acids, which are compounds that enter into the Krebs cycle. F. culmorum has a promising ability for bioremediation of environments polluted with DBP because it efficiently degrades DBP and uses high concentrations of this compound as carbon and energy source.
RESUMEN
Di(2-ethyl hexyl) phthalate (DEHP) is a plasticizer that interfere with endocrine systems in mammals. Growth parameters for Pleurotus ostreatus grown on media containing glucose and different concentrations of DEHP (0, 500 and 1000mg/L) were evaluated. The highest biomass production was observed in medium supplemented with 1000mg of DEHP/L. Half-life of DEHP biodegradation, biodegradation constant of DEHP, and percentage of removal efficiency (%E) were also determined. P. ostreatus degraded 100% of DEHP after 504h. %E was 99.3% and 98.4% for 500 and 1000mg of DEHP/L, respectively. Intermediate compounds of biodegraded DEHP were identified by GC-MS and a DEHP biodegradation pathway was proposed using quantum chemical investigation. DEHP might be metabolized through three pathways; a de-esterification pathway, an oxidation pathway and an oxidation-hydrolysis pathway, forming phthalic acid, acetic acid and butanediol, respectively. P. ostreatus degrades and uses (as carbon and energy source) high concentrations of DEHP.
Asunto(s)
Dietilhexil Ftalato/análisis , Disruptores Endocrinos/análisis , Plastificantes/análisis , Pleurotus/metabolismo , Animales , Biodegradación Ambiental , Biomasa , Biotransformación , Dietilhexil Ftalato/metabolismo , Disruptores Endocrinos/metabolismo , Cromatografía de Gases y Espectrometría de Masas , Semivida , Plastificantes/metabolismo , Pleurotus/crecimiento & desarrolloRESUMEN
Di(2-ethylhexyl) phthalate (DEHP) is a plasticizer widely used in the manufacture of plastics, and it is an environmental contaminant. The specific growth rate (µ), maximum biomass (Xmax), biodegradation constant of DEHP (k), half-life (t1/2) of DEHP biodegradation and removal efficiency of DEHP, esterase and laccase specific activities, and enzymatic yield parameters were evaluated for Fusarium culmorum grown on media containing glucose and different concentrations of DEHP (0, 500 and 1000mg/L). The greatest µ and the largest Xmax occurred in media supplemented with 1000mg of DEHP/L. F. culmorum degraded 95% of the highest amount of DEHP tested (1000mg/L) within 60h of growth. The k and t1/2 were 0.024h(-1) and 28h, respectively, for both DEHP concentrations. The removal efficiency of DEHP was 99.8% and 99.9% for 1000 and 500mg/L, respectively. Much higher specific esterase activity than specific laccase activity was observed in all media tested. The compounds of biodegradation of DEHP were identified by GC-MS. A DEHP biodegradation pathway by F. culmorum was proposed on the basis of the intermolecular flow of electrons of the identified intermediate compounds using quantum chemical modeling. DEHP was fully metabolized by F. culmorum with butanediol as the final product. This fungus offers great potential in bioremediation of environments polluted with DEHP.
Asunto(s)
Dietilhexil Ftalato/metabolismo , Fusarium/metabolismo , Contaminantes del Suelo/metabolismo , Biodegradación Ambiental , Fusarium/enzimología , Fusarium/crecimiento & desarrollo , Cinética , Modelos QuímicosRESUMEN
Mycoinsecticides application within Integral Pest Management requires high quantities of conidia, with the proper quality and resistance against environmental conditions. Metarhizium anisopliae var. lepidiotum conidia were produced in normal atmospheric conditions (21 % O2) and different concentrations of oxygen pulses (16, 26, 30, and 40 %); conidia obtained under hypoxic conditions showed significantly lower viability, hydrophobicity, and virulence against Tenebrio molitor larvae or mealworm, compared with those obtained under normal atmospheric conditions. Higher concentrations of oxygen (26 and 30 %) improved conidial production. However, when a 30 % oxygen concentration was applied, maximal conidial yields were obtained at earlier times (132 h) relative to 26 % oxygen pulses (156 h); additionally, with 30 % oxygen pulses, conidia thermotolerance was improved, maintaining viability, hydrophobicity, and virulence. Although conidial production was not affected when 40 % oxygen pulses were applied, viability and virulence were diminished in those conidia. In order to find a critical time for mycelia competence to respond to these oxidant conditions, oxygen pulses were first applied either at 36, 48, 60, and 72 h. A critical time of 60 h was determined to be the best time for the M. anisopliae var. lepidiotum mycelia to respond to oxygen pulses in order to increase conidial production and also to maintain the quality features. Therefore, oxygen-enriched (30 %) pulses starting at 60 h are recommended for a high production without the impairment of quality of M. anisopliae var. lepidiotum conidia.
Asunto(s)
Metarhizium/crecimiento & desarrollo , Micelio/metabolismo , Oxígeno/metabolismo , Esporas Fúngicas/crecimiento & desarrollo , Animales , Bioensayo , Interacciones Hidrofóbicas e Hidrofílicas , Metarhizium/patogenicidad , Control Biológico de Vectores , Tenebrio/microbiología , VirulenciaRESUMEN
Rice and oat flours were analyzed as media for the production of conidia by M. anisopliae var. lepidiotum. The presence of peptone increased conidia yield regardless of the substrate used; however, the highest yield was achieved on oat flour media. The effect of oxygen on conidia production using oat-peptone medium was also studied at two levels: Normal atmosphere (21% O(2)) and Oxygen-rich pulses (26% O(2)). Maximum conidia production (4.25 x 10(7) conidia cm(-2)) was achieved using 26% O(2) pulses after 156 h of culture, which was higher than 100% relative to conidial levels under normal atmosphere. Conidia yield per gram of biomass was 2.6 times higher with 26% O(2) (1.12 x 10(7) conidia mg(-1)). Conidia quality parameters, such as germination and hydrophobicity, did not show significant differences (P < 0.05) between those treatments. Bioassays parameters, using Tenebrio molitor adults, were analyzed for conidia obtained in both atmospheres and data were fitted to an exponential model. The specific mortality rates were 2.22 and 1.26 days(-1), whereas lethal times for 50% mortality were 3.90 and 4.31 days, for 26% O(2) pulses and 21% O(2) atmosphere, respectively. These results are relevant for production processes since an oxygen increase allowed superior levels of conidia by M. anisopliae without altering quality parameters and virulence toward Tenebrio molitor adults.
Asunto(s)
Medios de Cultivo/farmacología , Metarhizium/efectos de los fármacos , Metarhizium/aislamiento & purificación , Oxígeno/farmacología , Control Biológico de Vectores , Animales , Avena/química , Técnicas de Cultivo de Célula , Medios de Cultivo/química , Metarhizium/crecimiento & desarrollo , Oryza/química , Esporas Fúngicas/efectos de los fármacos , Esporas Fúngicas/crecimiento & desarrollo , Esporas Fúngicas/aislamiento & purificación , Tenebrio/microbiologíaRESUMEN
The production of laccases during the lag, exponential and stationary phases of growth of Pleurotus ostreatus in submerged fermentation was evaluated. Laccase activity was positively correlated to the growth of the fungus. The specific growth rate was 0.02 h(-1) and the highest amount of dry biomass (7.8 gl(-1)) was obtained after 480 h of growth. Four laccase isoforms were secreted by the fungus, and tentatively named L(I)1, L(I)2, L(I)3 and L(I)4. L(I)2, L(I)3 and L(I)4 were produced during the stationary phase (between 408 and 456 h approximately) while L(I)1 was produced during the lag, exponential and stationary phases of growth. Maximal laccase activity (12 200 Ul(-1)) was observed at the beginning of the stationary phase (at 432 h of growth). L(I)1 was purified by preparative isoelectric focusing and partially characterized. L(I)1 had a molecular mass of 43.7 kDa as determined by SDS PAGE, a Km and Vmax of 90 microM and 1.18 DeltaAbs min(-1) respectively and an isoelectric point of 2.3. L(I)1 showed activity over a broad range of pH and temperature, which may make it useful in the biodegradation of phenolic compounds present in wastewater from several industrial processes.