1,204 research outputs found

    Dengue disease, basic reproduction number and control

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    Dengue is one of the major international public health concerns. Although progress is underway, developing a vaccine against the disease is challenging. Thus, the main approach to fight the disease is vector control. A model for the transmission of Dengue disease is presented. It consists of eight mutually exclusive compartments representing the human and vector dynamics. It also includes a control parameter (insecticide) in order to fight the mosquito. The model presents three possible equilibria: two disease-free equilibria (DFE) and another endemic equilibrium. It has been proved that a DFE is locally asymptotically stable, whenever a certain epidemiological threshold, known as the basic reproduction number, is less than one. We show that if we apply a minimum level of insecticide, it is possible to maintain the basic reproduction number below unity. A case study, using data of the outbreak that occurred in 2009 in Cape Verde, is presented.Comment: This is a preprint of a paper whose final and definitive form has appeared in International Journal of Computer Mathematics (2011), DOI: 10.1080/00207160.2011.55454

    Is the technical performance of young soccer players influenced by hormonal status, sexual maturity, anthropometric profile, and physical performance?

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    The aim of this study was to examine the influence of hormonal status, anthropometric profile, sexual maturity level, and physical performance on the technical abilities of 40 young male soccer players during small-sided games (SSGs). Anthropometric profiling, saliva sampling, sexual maturity assessment (Tanner scale), and physical performance tests (Yo-Yo and vertical jumps) were conducted two weeks prior to the SSGs. Salivary testosterone was determined by the enzyme-linked immunosorbent assay method. Technical performance was determined by the frequency of actions during SSGs. Principal component analyses identified four technical actions of importance: total number of passes, effectiveness, goal attempts, and total tackles. A multivariate canonical correlation analysis was then employed to verify the prediction of a multiple dependent variables set (composed of four technical actions) from an independent set of variables, composed of testosterone concentration, stage of pubic hair and genitalia development, vertical jumps and Yo-Yo performance. A moderate-to-large relationship between the technical performance set and the independent set was observed. The canonical correlation was 0.75 with a canonical R2 of 0.45. The highest structure coefficient in the technical performance set was observed for tackles (0.77), while testosterone presented the highest structure coefficient (0.75) for the variables of the independent set. The current data suggest that the selected independent set of variables might be useful in predicting SSG performance in young soccer players. Coaches should be aware that physical development plays a key role in technical performance to avoid decision-making mistakes during the selection of young players

    Two-plane automatic balancing:a symmetry breaking analysis

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    International audienceWe present an analysis of a two-plane automatic balancing device for rotating machinery. The mechanism consists of a pair of races that contain balancing balls which move to eliminate imbalance due to rotor eccentricity or principal axis misalignment. A model is developed that includes the effect of support anisotropy and rotor acceleration. The symmetry of the imbalance is considered, and techniques from equivariant bifurcation theory are used to derive a necessary condition for the stability of balanced operation. The unfolding of the solution structure is explored and we investigate mechanical systems in which either the supports or the automatic ball balancer is asymmetric. Here it is shown that, provided the imbalance is small, the balanced state is robust to the considered asymmetries

    Temporal Changes in Technical and Physical Performances During a Small-Sided Game in Elite Youth Soccer Players

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    Background: There have been claims that small-sided games (SSG) may generate an appropriate environment to develop youth players’ technical performance associated to game-related problem solving. However, the temporal change in technical performance parameters of youth players during SSG is still unknown.. Objectives: The aim of this study was to examine temporal changes in technical and physical performances during a small-sided game (SSG) in elite soccer players.. Methods: Sixty elite youth players (age 14.8 ± 0.2 yr; stature 177 ± 5 cm; body mass 66.2 ± 4.7 kg) completed a 5 v 5 SSG using two repetitions of 8 minutes interspersed by 3 minutes of passive recovery. To evaluate temporal changes in performance, the data were analysed across 4 minutes quarters. Physical performance parameters included the total distance covered (TDC), the frequency of sprints (>18 km‱h-1), accelerations and decelerations (> 2.0 m‱s-2 and - 2.0 m‱s-2), metabolic power (W‱kg-1), training impulse (TRIMP), TDC: TRIMP, number of impacts, and body load. Technical performance parameters included goal attempts, total number of tackles, tackles and interceptions, total number of passes, and passes effectiveness.. Results: All physical performance parameters decreased from the first to the last quarter with notable declines in TDC, metabolic power and the frequency of sprints, accelerations and decelerations (P 0.05; trivial ES for 1st v 4th quarters: 0.15 - 0.33).. Conclusions: The data demonstrate that technical performance is maintained despite substantial declines in physical performance during a SSG in elite youth players. This finding may have implications for designing SSG’s for elite youth players to ensure physical, technical and tactical capabilities are optimized. Modifications in player number, pitch dimensions, rules, coach encouragement, for instance, should be included taking into account the main aim of a given session and then focused on overloading physical or technical elements.

    Antibiotics mineralization by electrochemical and UV-based hybrid processes: evaluation of the synergistic effect

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    [EN] Antibiotics are not efficiently removed in conventional wastewater treatments. In fact, different advanced oxidation process (AOPs), including ozone, peroxide, UV radiation, among others, are being investigated in the elimination of microcontaminants. Most of AOPs proved to be efficient on the degradation of antibiotics, but the mineralization is on the one hand not evaluated or on the other hand not high. At this work, the UV-based hybrid process, namely Photo-assisted electrochemical oxidation (PEO), was applied, aiming the mineralization of microcontaminants such as the antibiotics Amoxicillin (AMX), Norfloxacin (NOR) and Azithromycin (AZI). The influence of the individual contributions of electrochemical oxidation (EO) and the UV-base processes on the hybrid process (PEO) was analysed. Results showed that AMX and NOR presented higher mineralization rate under direct photolysis than AZI due to the high absorption of UV radiation. For the EO processes, a low mineralization was found for all antibiotics, what was associated to a mass-transport limitation related to the low concentration of contaminants (200 Âżg/L). Besides that, an increase in mineralization was found, when heterogeneous photocatalysis and EO are compared, due to the influence of UV radiation, which overcomes the mass-transport limitations. Although the UV-based processes control the reaction pathway that leads to mineralization, the best results to mineralize the antibiotics were achieved by PEO hybrid process. This can be explained by the synergistic effect of the processes that constitute them. A higher mineralization was achieved, which is an important and useful finding to avoid the discharge of microcontaminants in the environment.The authors thank CAPES project number DGPU-2015/7595/14-0, CNPq, FAPERGS, Cyted and FINEP for the financial support.Da Silva, SW.; Heberle, AN.; Santos, AP.; Rodrigues, M.; ValentĂ­n PĂ©rez-Herranz; Bernardes, A. (2018). Antibiotics mineralization by electrochemical and UV-based hybrid processes: evaluation of the synergistic effect. Environmental Technology. https://doi.org/10.1080/09593330.2018.1478453SKummerer, K. (2003). Significance of antibiotics in the environment. Journal of Antimicrobial Chemotherapy, 52(1), 5-7. doi:10.1093/jac/dkg293Dı́az-Cruz, M. S., LĂłpez de Alda, M. J., & BarcelĂł, D. (2003). Environmental behavior and analysis of veterinary and human drugs in soils, sediments and sludge. TrAC Trends in Analytical Chemistry, 22(6), 340-351. doi:10.1016/s0165-9936(03)00603-4De Carvalho RN, Ceriani L, Ippolito A, et al. Development of the first Watch List under the Environmental Quality Standards Directive, in, European Commission, 2015.Riaz, L., Mahmood, T., Khalid, A., Rashid, A., Ahmed Siddique, M. B., Kamal, A., & Coyne, M. S. (2018). Fluoroquinolones (FQs) in the environment: A review on their abundance, sorption and toxicity in soil. Chemosphere, 191, 704-720. doi:10.1016/j.chemosphere.2017.10.092Hirte, K., Seiwert, B., SchĂŒĂŒrmann, G., & Reemtsma, T. (2016). New hydrolysis products of the beta-lactam antibiotic amoxicillin, their pH-dependent formation and search in municipal wastewater. Water Research, 88, 880-888. doi:10.1016/j.watres.2015.11.028D. Barcelo, J. Bennett, editors. Antibiotic Resistance in the Environment. Sci Total Environ; 2015.Larsen, T. A., Lienert, J., Joss, A., & Siegrist, H. (2004). How to avoid pharmaceuticals in the aquatic environment. Journal of Biotechnology, 113(1-3), 295-304. doi:10.1016/j.jbiotec.2004.03.033Barbosa, M. O., Moreira, N. F. F., Ribeiro, A. R., Pereira, M. F. R., & Silva, A. M. T. (2016). Occurrence and removal of organic micropollutants: An overview of the watch list of EU Decision 2015/495. Water Research, 94, 257-279. doi:10.1016/j.watres.2016.02.047Niu, J., Zhang, L., Li, Y., Zhao, J., Lv, S., & Xiao, K. (2013). Effects of environmental factors on sulfamethoxazole photodegradation under simulated sunlight irradiation: Kinetics and mechanism. Journal of Environmental Sciences, 25(6), 1098-1106. doi:10.1016/s1001-0742(12)60167-3Wan, Z., Hu, J., & Wang, J. (2016). Removal of sulfamethazine antibiotics using Ce Fe-graphene nanocomposite as catalyst by Fenton-like process. Journal of Environmental Management, 182, 284-291. doi:10.1016/j.jenvman.2016.07.088Marcelino, R. B. P., LeĂŁo, M. M. D., Lago, R. M., & Amorim, C. C. (2017). Multistage ozone and biological treatment system for real wastewater containing antibiotics. Journal of Environmental Management, 195, 110-116. doi:10.1016/j.jenvman.2016.04.041Zhu, L., Santiago-SchĂŒbel, B., Xiao, H., Hollert, H., & Kueppers, S. (2016). Electrochemical oxidation of fluoroquinolone antibiotics: Mechanism, residual antibacterial activity and toxicity change. Water Research, 102, 52-62. doi:10.1016/j.watres.2016.06.005Choudhry, G. G., & Webster, G. R. B. (1987). Environmental photochemistry of polychlorinated dibenzofurans (PCDFs) and dibenzo‐p‐dioxins (PCDDs): A review. Toxicological & Environmental Chemistry, 14(1-2), 43-61. doi:10.1080/02772248709357193Juretic, D., Kusic, H., Koprivanac, N., & Loncaric Bozic, A. (2012). Photooxidation of benzene-structured compounds: Influence of substituent type on degradation kinetic and sum water parameters. Water Research, 46(9), 3074-3084. doi:10.1016/j.watres.2012.03.014Yuan, F., Hu, C., Hu, X., Qu, J., & Yang, M. (2009). Degradation of selected pharmaceuticals in aqueous solution with UV and UV/H2O2. Water Research, 43(6), 1766-1774. doi:10.1016/j.watres.2009.01.008Kim, I., Yamashita, N., & Tanaka, H. (2009). Performance of UV and UV/H2O2 processes for the removal of pharmaceuticals detected in secondary effluent of a sewage treatment plant in Japan. Journal of Hazardous Materials, 166(2-3), 1134-1140. doi:10.1016/j.jhazmat.2008.12.020Da Silva, S. W., Viegas, C., Ferreira, J. Z., Rodrigues, M. A. S., & Bernardes, A. M. (2016). The effect of the UV photon flux on the photoelectrocatalytic degradation of endocrine-disrupting alkylphenolic chemicals. Environmental Science and Pollution Research, 23(19), 19237-19245. doi:10.1007/s11356-016-7121-3Konstantinou, I. K., & Albanis, T. A. (2004). TiO2-assisted photocatalytic degradation of azo dyes in aqueous solution: kinetic and mechanistic investigations. Applied Catalysis B: Environmental, 49(1), 1-14. doi:10.1016/j.apcatb.2003.11.010Rivera-Utrilla, J., SĂĄnchez-Polo, M., Ferro-GarcĂ­a, M. Á., Prados-Joya, G., & Ocampo-PĂ©rez, R. (2013). Pharmaceuticals as emerging contaminants and their removal from water. A review. Chemosphere, 93(7), 1268-1287. doi:10.1016/j.chemosphere.2013.07.059KapaƂka, A., FĂłti, G., & Comninellis, C. (2009). The importance of electrode material in environmental electrochemistry. Electrochimica Acta, 54(7), 2018-2023. doi:10.1016/j.electacta.2008.06.045KapaƂka, A., Lanova, B., Baltruschat, H., FĂłti, G., & Comninellis, C. (2008). Electrochemically induced mineralization of organics by molecular oxygen on boron-doped diamond electrode. Electrochemistry Communications, 10(9), 1215-1218. doi:10.1016/j.elecom.2008.06.005Einaga, Y., Foord, J. S., & Swain, G. M. (2014). Diamond electrodes: Diversity and maturity. MRS Bulletin, 39(6), 525-532. doi:10.1557/mrs.2014.94FĂłti, G., Mousty, C., Reid, V., & Comninellis, C. (1998). Characterization of DSA type electrodes prepared by rapid thermal decomposition of the metal precursor. Electrochimica Acta, 44(5), 813-818. doi:10.1016/s0013-4686(98)00240-0Trasatti, S. (2000). Electrocatalysis: understanding the success of DSAÂź. Electrochimica Acta, 45(15-16), 2377-2385. doi:10.1016/s0013-4686(00)00338-8Pelegrini, R., Peralta-Zamora, P., de Andrade, A. R., Reyes, J., & DurĂĄn, N. (1999). Electrochemically assisted photocatalytic degradation of reactive dyes. Applied Catalysis B: Environmental, 22(2), 83-90. doi:10.1016/s0926-3373(99)00037-5Pinhedo, L., Pelegrini, R., Bertazzoli, R., & Motheo, A. J. (2005). Photoelectrochemical degradation of humic acid on a (TiO2)0.7(RuO2)0.3 dimensionally stable anode. Applied Catalysis B: Environmental, 57(2), 75-81. doi:10.1016/j.apcatb.2004.10.006Batchu, S. R., Panditi, V. R., O’Shea, K. E., & Gardinali, P. R. (2014). Photodegradation of antibiotics under simulated solar radiation: Implications for their environmental fate. Science of The Total Environment, 470-471, 299-310. doi:10.1016/j.scitotenv.2013.09.057Gonçalves, A. G., ÓrfĂŁo, J. J. M., & Pereira, M. F. R. (2014). Ozonation of erythromycin over carbon materials and ceria dispersed on carbon materials. Chemical Engineering Journal, 250, 366-376. doi:10.1016/j.cej.2014.04.012Liu, P., Zhang, H., Feng, Y., Yang, F., & Zhang, J. (2014). Removal of trace antibiotics from wastewater: A systematic study of nanofiltration combined with ozone-based advanced oxidation processes. Chemical Engineering Journal, 240, 211-220. doi:10.1016/j.cej.2013.11.057Bolton, J. R., Bircher, K. G., Tumas, W., & Tolman, C. A. (2001). Figures-of-merit for the technical development and application of advanced oxidation technologies for both electric- and solar-driven systems (IUPAC Technical Report). Pure and Applied Chemistry, 73(4), 627-637. doi:10.1351/pac200173040627Li, G., Zhu, M., Chen, J., Li, Y., & Zhang, X. (2011). Production and contribution of hydroxyl radicals between the DSA anode and water interface. Journal of Environmental Sciences, 23(5), 744-748. doi:10.1016/s1001-0742(10)60470-6Panizza, M., & Cerisola, G. (2009). Direct And Mediated Anodic Oxidation of Organic Pollutants. Chemical Reviews, 109(12), 6541-6569. doi:10.1021/cr9001319Niu, X.-Z., Busetti, F., Langsa, M., & CrouĂ©, J.-P. (2016). Roles of singlet oxygen and dissolved organic matter in self-sensitized photo-oxidation of antibiotic norfloxacin under sunlight irradiation. Water Research, 106, 214-222. doi:10.1016/j.watres.2016.10.002Hartmann, J., Bartels, P., Mau, U., Witter, M., TĂŒmpling, W. v., Hofmann, J., & Nietzschmann, E. (2008). Degradation of the drug diclofenac in water by sonolysis in presence of catalysts. Chemosphere, 70(3), 453-461. doi:10.1016/j.chemosphere.2007.06.063MartĂ­nez-Huitle, C. A., Rodrigo, M. A., SirĂ©s, I., & Scialdone, O. (2015). Single and Coupled Electrochemical Processes and Reactors for the Abatement of Organic Water Pollutants: A Critical Review. Chemical Reviews, 115(24), 13362-13407. doi:10.1021/acs.chemrev.5b00361Ohtani, B. (2010). Photocatalysis A to Z—What we know and what we do not know in a scientific sense. Journal of Photochemistry and Photobiology C: Photochemistry Reviews, 11(4), 157-178. doi:10.1016/j.jphotochemrev.2011.02.001Chong, M. N., Jin, B., Chow, C. W. K., & Saint, C. (2010). Recent developments in photocatalytic water treatment technology: A review. Water Research, 44(10), 2997-3027. doi:10.1016/j.watres.2010.02.039Li, G., Zhu, W., Chai, X., Zhu, L., & Zhang, X. (2015). Partial oxidation of polyvinyl alcohol using a commercially available DSA anode. Journal of Industrial and Engineering Chemistry, 31, 55-60. doi:10.1016/j.jiec.2015.05.042Montgomery DC. Introduction to statistical quality control, 2009.Montgomery DC. Design and analysis of experiments, 2012.Kumar, K. V., Porkodi, K., & Rocha, F. (2008). Langmuir–Hinshelwood kinetics – A theoretical study. Catalysis Communications, 9(1), 82-84. doi:10.1016/j.catcom.2007.05.019Daneshvar, N., Rasoulifard, M. H., Khataee, A. R., & Hosseinzadeh, F. (2007). Removal of C.I. Acid Orange 7 from aqueous solution by UV irradiation in the presence of ZnO nanopowder. Journal of Hazardous Materials, 143(1-2), 95-101. doi:10.1016/j.jhazmat.2006.08.072Hussain, S., Steter, J. R., Gul, S., & Motheo, A. J. (2017). Photo-assisted electrochemical degradation of sulfamethoxazole using a Ti/Ru 0.3 Ti 0.7 O 2 anode: Mechanistic and kinetic features of the process. Journal of Environmental Management, 201, 153-162. doi:10.1016/j.jenvman.2017.06.043Heberle, A. N. A., da Silva, S. W., Klauck, C. R., Ferreira, J. Z., Rodrigues, M. A. S., & Bernardes, A. M. (2017). Electrochemical enhanced photocatalysis to the 2,4,6 Tribromophenol flame retardant degradation. Journal of Catalysis, 351, 136-145. doi:10.1016/j.jcat.2017.04.011Da Silva, S. W., Bordignon, G. L., Viegas, C., Rodrigues, M. A. S., Arenzon, A., & Bernardes, A. M. (2015). Treatment of solutions containing nonylphenol ethoxylate by photoelectrooxidation. Chemosphere, 119, S101-S108. doi:10.1016/j.chemosphere.2014.03.134Xin, Y., Gao, M., Wang, Y., & Ma, D. (2014). Photoelectrocatalytic degradation of 4-nonylphenol in water with WO3/TiO2 nanotube array photoelectrodes. Chemical Engineering Journal, 242, 162-169. doi:10.1016/j.cej.2013.12.068Hurwitz, G., Hoek, E. M. V., Liu, K., Fan, L., & Roddick, F. A. (2014). Photo-assisted electrochemical treatment of municipal wastewater reverse osmosis concentrate. Chemical Engineering Journal, 249, 180-188. doi:10.1016/j.cej.2014.03.08

    Biochemical analysis of TssK, a core component of the bacterial Type VI secretion system, reveals distinct oligomeric states of TssK and identifies a TssK–TssFG subcomplex

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    Gram-negative bacteria use the Type VI secretion system (T6SS) to inject toxic proteins into rival bacteria or eukaryotic cells. However, the mechanism of the T6SS is incompletely understood. In the present study, we investigated a conserved component of the T6SS, TssK, using the antibacterial T6SS of Serratia marcescens as a model system. TssK was confirmed to be essential for effector secretion by the T6SS. The native protein, although not an integral membrane protein, appeared to localize to the inner membrane, consistent with its presence within a membrane-anchored assembly. Recombinant TssK purified from S. marcescens was found to exist in several stable oligomeric forms, namely trimer, hexamer and higher-order species. Native-level purification of TssK identified TssF and TssG as interacting proteins. TssF and TssG, conserved T6SS components of unknown function, were required for T6SS activity, but not for correct localization of TssK. A complex containing TssK, TssF and TssG was subsequently purified in vitro, confirming that these three proteins form a new subcomplex within the T6SS. Our findings provide new insight into the T6SS assembly, allowing us to propose a model whereby TssK recruits TssFG into the membrane-associated T6SS complex and different oligomeric states of TssK may contribute to the dynamic mechanism of the system

    Construction of effective disposable biosensors for point of care testing of nitrite

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    © 2015. This manuscript version is made available under the CC-BY-NC-ND 4.0 license http://creativecommons.org/licenses/by-nc-nd/4.0/"In this paper we aim to demonstrate, as a proof-of-concept, the feasibility of the mass production of effective point of care tests for nitrite quantification in environmental, food and clinical samples. Following our previous work on the development of third generation electrochemical biosensors based on the ammonia forming nitrite reductase (ccNiR), herein we reduced the size of the electrodes’ system to a miniaturized format, solved the problem of oxygen interference and performed simple quantification assays in real samples. In particular, carbon paste screen printed electrodes (SPE) were coated with a ccNiR/carbon ink composite homogenized in organic solvents and cured at low temperatures. The biocompatibility of these chemical and thermal treatments was evaluated by cyclic voltammetry showing that the catalytic performance was higher with the combination acetone and a 40 °C curing temperature. The successful incorporation of the protein in the carbon ink/solvent composite, while remaining catalytically competent, attests for ccNiR’s robustness and suitability for application in screen printed based biosensors. Because the direct electrochemical reduction of molecular oxygen occurs when electroanalytical measurements are performed at the negative potentials required to activate ccNiR (ca. -0.4 V vs Ag/AgCl), an oxygen scavenging system based on the coupling of glucose oxidase and catalase activities was successfully used. This enabled the quantification of nitrite in different samples (milk, water, plasma and urine) in a straightforward way and with small error (1 – 6%). The sensitivity of the biosensor towards nitrite reduction under optimized conditions was 0.55 A M-1 cm-2 with a linear response range 0.7 – 370 ÎŒM.
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