156 research outputs found

    E. coli metabolic protein aldehydealcohol dehydrogenase-E binds to the ribosome: a unique moonlighting action revealed

    Get PDF
    It is becoming increasingly evident that a high degree of regulation is involved in the protein synthesis machinery entailing more interacting regulatory factors. A multitude of proteins have been identified recently which show regulatory function upon binding to the ribosome. Here, we identify tight association of a metabolic protein aldehyde-alcohol dehydrogenase E (AdhE) with the E. coli 70S ribosome isolated from cell extract under low salt wash conditions. Cryo-EM reconstruction of the ribosome sample allows us to localize its position on the head of the small subunit, near the mRNA entrance. Our study demonstrates substantial RNA unwinding activity of AdhE which can account for the ability of ribosome to translate through downstream of at least certain mRNA helices. Thus far, in E. coli, no ribosome-associated factor has been identified that shows downstream mRNA helicase activity. Additionally, the cryo-EM map reveals interaction of another extracellular protein, outer membrane protein C (OmpC), with the ribosome at the peripheral solvent side of the 50S subunit. Our result also provides important insight into plausible functional role of OmpC upon ribosome binding. Visualization of the ribosome purified directly from the cell lysate unveils for the first time interactions of additional regulatory proteins with the ribosom

    A Computational Investigation on the Connection between Dynamics Properties of Ribosomal Proteins and Ribosome Assembly

    Get PDF
    Assembly of the ribosome from its protein and RNA constituents has been studied extensively over the past 50 years, and experimental evidence suggests that prokaryotic ribosomal proteins undergo conformational changes during assembly. However, to date, no studies have attempted to elucidate these conformational changes. The present work utilizes computational methods to analyze protein dynamics and to investigate the linkage between dynamics and binding of these proteins during the assembly of the ribosome. Ribosomal proteins are known to be positively charged and we find the percentage of positive residues in r-proteins to be about twice that of the average protein: Lys+Arg is 18.7% for E. coli and 21.2% for T. thermophilus. Also, positive residues constitute a large proportion of RNA contacting residues: 39% for E. coli and 46% for T. thermophilus. This affirms the known importance of charge-charge interactions in the assembly of the ribosome. We studied the dynamics of three primary proteins from E. coli and T. thermophilus 30S subunits that bind early in the assembly (S15, S17, and S20) with atomic molecular dynamic simulations, followed by a study of all r-proteins using elastic network models. Molecular dynamics simulations show that solvent-exposed proteins (S15 and S17) tend to adopt more stable solution conformations than an RNA-embedded protein (S20). We also find protein residues that contact the 16S rRNA are generally more mobile in comparison with the other residues. This is because there is a larger proportion of contacting residues located in flexible loop regions. By the use of elastic network models, which are computationally more efficient, we show that this trend holds for most of the 30S r-proteins

    Lateral opening in the intact β-barrel assembly machinery captured by cryo-EM

    Get PDF
    The β-barrel assembly machinery (BAM) is a ~203 kDa complex of five proteins (BamA-E) which is essential for viability in E. coli. BAM promotes the folding and insertion of β-barrel proteins into the outer membrane via a poorly understood mechanism. Several current models suggest that BAM functions through a ‘lateral gating’ motion of the β-barrel of BamA. Here we present a cryo-EM structure of the BamABCDE complex, at 4.9 Å resolution. The structure is in a laterally open conformation showing that gating is independent of BamB binding. We describe conformational changes throughout the complex, and interactions between BamA, B, D, and E and the detergent micelle that suggest communication between BAM and the lipid bilayer. Finally, using an enhanced reconstitution protocol and functional assays, we show that for the outer membrane protein OmpT, efficient folding in vitro requires lateral gating in BAM

    Tratamiento de efluentes acuosos contaminados con compuestos organoclorados

    Get PDF
    [ES] Los compuestos organoclorados son un tipo de residuos que han adquirido especial relevancia en los últimos tiempos, debido a sus características tóxicas y peligrosas, tanto para el medio ambiente como para los seres humanos. Su especial peligrosidad ha potenciado la búsqueda de alternativas para su tratamiento en las distintas corrientes donde se presentan. En este artículo se describe la problemática real de este tipo de compuestos, se exponen los principales contaminantes y se muestra una visión general de las alternativas para la eliminación de estos organoclorados de corrientes acuosas, detallándose en profundidad una de las alternativas de eliminación consideradas: la hidrodecloración catalítica en fase acuosa.Padilla Vivas, B.; Díez Sanz, FV.; Ordóñez García, S. (2005). Tratamiento de efluentes acuosos contaminados con compuestos organoclorados. Ingeniería del agua. 12(4):361-375. https://doi.org/10.4995/ia.2005.2571OJS361375124Alejandre A., Medina F., Rodríguez X., Salagre P., Cesteros Y., Sueiras J. E. (2000). Cu/Ni/Al layered double hydroxides as precursors of catalysts for the wet air oxidation of phenol aqueous solutions. Appl. Catal. B. 30:195-207Ali M., Sreekrishnan T. R. (2001). Aquatic toxicity from pulp and paper mill effluents: a reviewAdvances in Environmental Research. 5:175-196Aramendia M. A., Boráu V., García I. M., Jiménez C., Marinas A., Marinas J. M., Urbano F. J. (2002). Liquid-phase hydrodehalogenation of substituted chlorobenzenes over palladium supported catalysts. Appl. Catal. B.43:71-79Araujo J. (1993). Naturaleza y Ecología en España. La Muerte Silenciosa. Ed. Círculo de LectoresATSDR. Agency for Toxic Substances and Disease Registry (2002). ToxFAQs™. EEUU.Brauer H. (1985). Biotechnology Fundamentals of Biochemical Engineering. Volumen 2.Buitrón G., González A., López-Martín L. M. (1998). Biodegradation of phenolic compounds by an acclimated activated sludge and isolated bacteria. Water Science and Technology. 37:371-378Cuevas M. A. (1998). Jornadas sobre la contaminación de las aguas subterráneas: un problema pendiente. Valencia.Cybulski, Trawczynski J. (2004). Catalytic wet air oxidation of phenol over platinum and ruthenium catalysts. Appl. Catal. B. 47:1-13Debellefontaine H., Foussard J. (1999). Wet air oxidation for the treatment of industrial wastes. Chemical aspects, reactor design and industrial applications in Europe. Waste management. 20:15Energy Research Group (2003). Centre for Ecological Sciences, Bangalore, India.EPA (1998). The inventory sources of chlorinated pollutants in the United States (EPA/600/P-98/002Aa).EPA (1999). Integrated Risk Information System on 1,2,4-Trichlorobenzene.EPA (2003). Ground water primer, EPA region 5 and Agricultural & Biological Engineering. Purdue UniversityEuro Chlor (2002). Chloroform in the environment; Marine Risk Assessments (www.eurochlor.org)Felis V., Bellefon C., Fouilloux P., Schweich D. (1998). Hydrodechlorination and hydrodearomatisation of monoaromatic chlorophenols into cyclohexanol on Ru/C catalysts applied to water depollution: influence of basic solvent and kinetics of the reactions. Appl. Catal. B: Environ. 20:91-100Fernández J., Maruthamuthu P., Kiwi J. (2004). Photobleaching and mineralization of Orange II by oxone and metal-ions involving Fenton-like chemistry under visible light. Journal of Photochemistry and Photobiology A: Chemistry. 161:185-192Fortuny A., Bengoa C., Font J., Castells F., Fabregat A. (1999). Water pollution abatement by catalytic wet air oxidation in a trickle bed reactor. Catalysis Today. 53:107-114Fritsch D., Kuhr K., Mackenzie K., Kopinke F. (2003). Hydrodechlorination of chloroorganics compounds in groundwater by Pd catalysts. Part 1. Development of polymer-based catalysts and membrane reactor tests. Catalysis Today. 82:105-118García Ara L. J. (2002). Actuaciones para la minimización del impacto del vertido de sustancias peligrosas en la industria química. (www.eic.es)Glaze W., Kenneke J., Ferry J. (1993). Chlorinated by-products from the TiO2-mediated photodegradation of trichloroethylene and tetrachloroethylene in water. Environ. Sci. Technol. 27:177-184Heinrichts B., Schoebrechts J. P., Pirard J. P. (2001). Palladium-silver sol-gel catalysts for selective hydrodechlorination of 1,2-dichloroethane into ethylene. Part III. Kinetics and reaction mechanism. Part IV. Deactivation mechanism and regeneration. Journal of Catalysis. 200:309-320Hoke J. B., Gramiccioni G. A., Balko E. N. (1992). Catalytic hydrodechlorination of chlorophenols. Appl. Catal. B: Environ. 1:285-296Janssen D. B., Oppentocht J. E., Poelarends G. J. (2001). Microbial dehalogenation. Environmental Biotechnology. 12:254-258Jechorek M., Wendlandt K. D., Beck M. (2003). Cometabolic degradation of chlorinated aromatic compounds. Journal of Biotechnology. 102:93-98Kargi F., Eker S. (2004, in press, corrected proof). Removal of 2,4-dichlorophenol and toxicity from synthetic wastewater in a rotating perforated tube biofilm reactor. Process BiochemistryKim Y. H., Carraway E. R. (2000). Dechlorination of pentachlorophenol by zero valent iron and modified zero valent irons. Environ. Sci. Tec. 34:2014-2017Kopinke F., Mackenzie K., Köhler R. (2002). Catalytic hydrodechlorination of groundwater contaminants in water and in the gas phase using Pd/Al2O3. Appl. Catal B: Environ. 1349:1-10Kovenklioglu S., Cao Z., Farrauto R. J., Balko E. N. (1992). Direct catalytic hydrodechlorination of toxic organics in wastewater. AIChE J. 38:1003-1012Lin S. S., Chen C. L., Chang D. J., Chen C. & C. (2001). Catalytic wet air oxidation of phenol by various CeO2catalysts. Water research. 36:3009-3014Lomnicki S., Lichtenberger J., Xu Z., Waters M., Kosman J., Amiridis M. D. (2003). Catalytic oxidation of 2,4,6-trichlorophenol over vanadia/titania-based catalysts. Appl. Catal. B: Environ. 46:105-119López E., Ordóñez S., Díez F. V. (2003). Inhibition effects of organosulphur compounds on the hydrodechlorination of tetrachloroethylene. Catalysis Today. 84:121-127Lowry G. V., Reinhard M. (1999). Hydrodehalogenation of 1- to 3- carbon halogenated organic compounds in water using a palladium catalyst and hydrogen gas. Environ. Sci. Technology.33:1905-1910Lowry G. V., Reinhard M. (2000). Pd-catalyzed TCE dechlorination in groundwater: solute effects, biological control and oxidative catalyst regeneration. Environ. Sci. Technology. 34:3217-3223Malato S., Blanco J., Vidal A., Richter C. (2002). Photocatalysis with solar energy at a pilot-plant scale: an overview. Appl. Catal. B: Environ. 37:1-15Matatov-Meytal Y. I., Sheintuch M. (1998). Catalytic abatement of water pollutants. Ind. Eng. Chem. Res. 37:309-326Matatov-Meytal Y. I., Sheintuch M. (2000). Catalytic regeneration of chloroorganics-saturated activated carbon using hydrodechlorination. Ind. Eng. Chem.Res. 39:18-23Matatov-Meytal Y. I., Sheintuch M. (2002). Hydrotreating processes for catalytic abatement of water pollutants. Catalysis Today. 75:63-67Matheson L. J., Tratnyek P. G. (1994). Reductive dehalogenation of chlorinated methanes by iron metal. Environ. Sci. Technology. 28:2045-2053McNab W. W., Ruiz R., Reinhard M. (2000). In-situ destruction of chlorinated hydrocarbons in groundwater using catalytic reductive dehalogenation in a reactive well: testing and operational experiences. Environ. Sci. Technol. 34:149-153Ministerio de Medio Ambiente (2001). Medio Ambiente en España 2000. Ed. Direc. Gral. de Medio Ambiente.Muftikian R., Fernando Q., Korte N. (1995). A method for the rapid dechlorination of low molecular weight chlorinated hydrocarbons in water. Water Research. 29:2434-2439Ordóñez S., Díez F. V., Sastre H. (2003). Hydrodechlorination of tetrachloroethylene over Pd catalysts: influence of process conditions on catalyst performance and stability. Appl. Catal. B. 40:119-130Peres, J. A., Beltrán de Heredia J. (2004). Integrated Fenton's reagent coagulation/flocculation process for the treatment of cork processing wastewaters. Journal of Hazardous Materials. 107:115-121Perrone L., Prati L., Rossi M. (1997). Removal of chlorinated organic compounds from water by catalytic dehydrohalogenation. Appl. Catal. B: Environ. 15:241-246Portela J. R., Bernal J. L., Sanz E. N., Martínez de la Ossa E. (1997). Kinetics of wet air oxidation of phenol. Chem. Eng. J. 67:115-121Rivas F. J., Kolaczkowski S. T., Beltrán F. J., McLurgh D. (1998). Development of a model for the wet air oxidation of phenol based on a free radical mechanism. Chemical Engineering Science. 53:2575-2586Schmidt L. M., Delfino J. J., Preston J. F., St. Laurent G. (1999). Biodegradation of low aqueous concentration pentachlorophenol (PCP) contaminated groundwater. Chemosphere. 38:2897Schreier C. G., Reinhard M. (1995). Catalytic hydrodehalogenation of chlorinated ethylenes using palladium and hydrogen for the treatment of contaminated water. Chemosphere. 31:3475-3487Schüth C., Disser S., Schüth F., Reinhard M. (2000). Tailoring catalysts for hydrodechlorinating chlorinated hydrocarbon contaminants in groundwater. Appl. Catal. B: Environ. 28:147-152Schüth C., Reinhard M. (1998). Hydrodechlorination and hydrogenation of aromatic compounds over palladium on alumina in hydrogen-saturated water. Appl. Catal. B: Environ. 18:215-221Shindler Y., Matatov-Meytal Y. I., Sheintuch M. (2001). Wet hydrodechlorination of p-chlorophenol using Pd supported on an activated carbon cloth. Ind. Eng. Chem.Res. 40:3301-3308Sweeny K. H. (1981). The reductive treatment of industrial wastewaters. AIChE Symp.Series. 77:67-78Torrades F., Pérez M., Mansilla H. D., Peral J. (2003). Experimental design of Fenton and photo-Fenton reactions for the treatment of cellulose bleaching effluents. Chemosphere. 53:1211-1220Trabuco E., Ford P.C. (1999). Hydrodechlorination of 1,2-dichloroethane by rhodium catalysts under water gas shift reaction conditions. Journal of Molecular Catalysis A: Chemical. 148:1-7Young K., Daniel J., Lewis S. (2002). Kinetic and inhibition studies for the aerobic cometabolism of 1,1,1-trichloroethane, 1,1-dichloroethylene and 1,1-dichloroethane by a butane-grown mixed culture. Biotechnology and Bioengineering. 80:498-508Yuan G., Keane M.A. (2003a). Liquid phase catalytic hydrodechlorination of 2,4-dichlorophenol over carbon supported Pd: an evaluation of transport limitations Chemical Engineering Science. 58:257-267Yuan G., Keane M.A. (2003b). Liquid phase catalytic hydrodechlorination of chlorophenols at 273 K. Catalysis Communications. 4:195-201Yuan G., Keane M.A. (2003c). Catalyst deactivation during the liquid phase hydrodechlorination of 2,4-dichlorophenol over supported Pd: influence of the support. Catalysis Today. 88:27-3

    Mechanism of eIF6 release from the nascent 60S ribosomal subunit.

    Get PDF
    SBDS protein (deficient in the inherited leukemia-predisposition disorder Shwachman-Diamond syndrome) and the GTPase EFL1 (an EF-G homolog) activate nascent 60S ribosomal subunits for translation by catalyzing eviction of the antiassociation factor eIF6 from nascent 60S ribosomal subunits. However, the mechanism is completely unknown. Here, we present cryo-EM structures of human SBDS and SBDS-EFL1 bound to Dictyostelium discoideum 60S ribosomal subunits with and without endogenous eIF6. SBDS assesses the integrity of the peptidyl (P) site, bridging uL16 (mutated in T-cell acute lymphoblastic leukemia) with uL11 at the P-stalk base and the sarcin-ricin loop. Upon EFL1 binding, SBDS is repositioned around helix 69, thus facilitating a conformational switch in EFL1 that displaces eIF6 by competing for an overlapping binding site on the 60S ribosomal subunit. Our data reveal the conserved mechanism of eIF6 release, which is corrupted in both inherited and sporadic leukemias.Supported by a Federation of European Biochemical Societies Long term Fellowship (to FW), Specialist Programme from Bloodwise [12048] (AJW), the Medical Research Council [MC_U105161083] (AJW) and [U105115237] (RRK), Wellcome Trust strategic award to the Cambridge Institute for Medal Research [100140], Tesni Parry Trust (AJW), Ted’s Gang (AJW) and the Cambridge NIHR Biomedical Research Centre.This is the author accepted manuscript. The final version is available from Nature Publishing Group via http://dx.doi.org/10.1038/nsmb.311

    A highly potent human antibody neutralizes dengue virus serotype 3 by binding across three surface proteins

    Get PDF
    Dengue virus (DENV) infects ~400 million people annually. There is no licensed vaccine or therapeutic drug. Only a small fraction of the total DENV-specific antibodies in a naturally occurring dengue infection consists of highly neutralizing antibodies. Here we show that the DENV-specific human monoclonal antibody 5J7 is exceptionally potent, neutralizing 50% of virus at nanogram-range antibody concentration. The 9 Å resolution cryo-electron microscopy structure of the Fab 5J7–DENV complex shows that a single Fab molecule binds across three envelope proteins and engages three functionally important domains, each from a different envelope protein. These domains are critical for receptor binding and fusion to the endosomal membrane. The ability to bind to multiple domains allows the antibody to fully coat the virus surface with only 60 copies of Fab, that is, half the amount compared with other potent antibodies. Our study reveals a highly efficient and unusual mechanism of molecular recognition by an antibody. There is no licensed vaccine or therapeutic for dengue virus (DENV) infection. Here, the authors show that a highly potent human monoclonal antibody binds to DENV particles in an unusual and very effective way by interacting with three viral envelope proteins

    Refined physical parameters for Chariklo’s body and rings from stellar occultations observed between 2013 and 2020

    Get PDF
    Context. The Centaur (10199) Chariklo has the first ring system discovered around a small object. It was first observed using stellar occultation in 2013. Stellar occultations allow sizes and shapes to be determined with kilometre accuracy, and provide the characteristics of the occulting object and its vicinity. Aims. Using stellar occultations observed between 2017 and 2020, our aim is to constrain the physical parameters of Chariklo and its rings. We also determine the structure of the rings, and obtain precise astrometrical positions of Chariklo. Methods. We predicted and organised several observational campaigns of stellar occultations by Chariklo. Occultation light curves were measured from the datasets, from which ingress and egress times, and the ring widths and opacity values were obtained. These measurements, combined with results from previous works, allow us to obtain significant constraints on Chariklo's shape and ring structure. Results. We characterise Chariklo's ring system (C1R and C2R), and obtain radii and pole orientations that are consistent with, but more accurate than, results from previous occultations. We confirm the detection of W-shaped structures within C1R and an evident variation in radial width. The observed width ranges between 4.8 and 9.1 km with a mean value of 6.5 km. One dual observation (visible and red) does not reveal any differences in the C1R opacity profiles, indicating a ring particle size larger than a few microns. The C1R ring eccentricity is found to be smaller than 0.022 (3σ), and its width variations may indicate an eccentricity higher than ~0.005. We fit a tri-axial shape to Chariklo's detections over 11 occultations, and determine that Chariklo is consistent with an ellipsoid with semi-axes of 143.8-1.5+1.4, 135.2-2.8+1.4, and 99.1-2.7+5.4 km. Ultimately, we provided seven astrometric positions at a milliarcsecond accuracy level, based on Gaia EDR3, and use it to improve Chariklo's ephemeris

    Experimental detection of short regulatory motifs in eukaryotic proteins: tips for good practice as well as for bad

    Full text link
    It has become clear in outline though not yet in detail how cellular regulatory and signalling systems are constructed. The essential machines are protein complexes that effect regulatory decisions by undergoing internal changes of state. Subcomponents of these cellular complexes are assembled into molecular switches. Many of these switches employ one or more short peptide motifs as toggles that can move between one or more sites within the switch system, the simplest being on-off switches. Paradoxically, these motif modules (termed short linear motifs or SLiMs) are both hugely abundant but difficult to research. So despite the many successes in identifying short regulatory protein motifs, it is thought that only the “tip of the iceberg” has been exposed. Experimental and bioinformatic motif discovery remain challenging and error prone. The advice presented in this article is aimed at helping researchers to uncover genuine protein motifs, whilst avoiding the pitfalls that lead to reports of false discovery. ELECTRONIC SUPPLEMENTARY MATERIAL: The online version of this article (doi:10.1186/s12964-015-0121-y) contains supplementary material, which is available to authorized users
    corecore