367,414 research outputs found

    Process of treating cellulosic membrane and alkaline with membrane separator

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    The improvement of water-soluble cellulose ether membranes for use as separators in concentrated alkaline battery cells is discussed. The process of contacting membranes with an aqueous alkali solution of concentration less than that of the alkali solution to be used in the battery but above that at which the membrane is soluble is described

    Device separates hydrogen from solution in water at ambient temperatures

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    Separator decreases the partial pressure of hydrogen gas dissolved in the water produced by fuel cells containing an alkaline electrolyte. The unit eliminates the hazards associated with the release of hydrogen from water solution when the hydrostatic pressure is rapidly decreased

    Manganese pigmented anodized copper as solar selective absorber

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    The study concerns the optical and structural properties of layers obtained by a new efficient surface treatment totally free of chromium species. The process is made up of an anodic oxidation of copper in an alkaline solution followed by an alkaline potassium permanganate dipping post-treatment. Coatings, obtained at the lab and pilot scales, are stable up to 220 °C in air and vacuum, present low emissivity (0.14 at 70 °C) and high solar absorptivity (0.96), i.e. a suitable thermal efficiency (0.84 at 70 °C)

    Studies in fundamental chemistry of fuel cell reactions Quarterly report, 1 Jul. - 30 Sep. 1969

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    Electrocatalysts, dendritic deposition of zinc from alkaline solution, reversibility of organic reactions with platinum and gold electrodes, ion adsorption, and related studies on fuel cell

    In Vitro Dry Matter Digestibility of Cocoa Pods Immersed in Different Alkaline Solution

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    The aim of this study was to determine in vitro dry matter digestibility (IVDMD) of cocoa pods following treatment of immersing the cocoa pods into different alkaline solution at different length of immersion time. The experiment was carried out in a 5 x 3 factorial arrangement according to completely randomized design. The replication for each treatment combination was three giving the total number of experimental units was 45. The first factor was different alkaline solutions, namely P1: water, P2: rice husk ash solution 10%, P3: coconut shell ash solution 10%, P4: cocoa pod ash solution 10% and P5: NaOH 6%. The second factor was immersion time, i.e. T1: immersion time for 8 hours, T2: immersion time for 16 hours, and T3: immersion for 24 hours. Analysis of variance indicated that alkaline solution, immersion time, and interaction between alkaline solution and immersion time affected (P<0.05) IVDMD of cocoa pods. In conclusion, the IVDMD decreased as the length of immersion time increased. Moreover, the best alkaline solution giving similar result to that NaOH 6% solution was alkaline solution made from cocoa pods ash

    Electrochemical removal of phenol in alkaline solution. Contribution of the anodic polymerization on different electrode materials

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    The removal of organic pollutants based on electropolymerization on an anode was performed in the case of phenol in alkaline solution. The polymer formed by a process involving less than two electrons per molecule of phenol, is then precipitated by decreasing the pH and finally filtered and disposed. The electrochemical polymerization of phenol (C0 = 0.105M) in alkaline solution (pH = 13) at 86 ◦C has been studied by galvanostatic electrolysis, using a range of anode materials characterized by different O2-overpotentials (IrO2, Pt and B-PbO2). Measurements of total organic carbon and HPLC have been used to follow phenol oxidation; the morphology of the polymer deposited on the electrode surface has been examined by SEM. Experimental data indicate that phenol concentration decreases by oxidation according to a first order reaction suggesting a mass transport limitation process. Polymeric films formed in alkaline solution did not cause the complete deactivation of the anodes. SEM results show that the polymeric films formed on Ti/IrO2 and Pt anodes cannot be mineralized. On the other hand, complex oxidation reactions leading to the partial incineration of polymeric materials can take place on the Ta/B-PbO2 surface due to electrogenerated HO• radicals which have an oxidizing power much higher than that of intermediaries formed respectively on IrO2 and Pt. It is assumed that the polymer films formed on these anodes have different permeability characteristics which determine the rate of mass transfer of the phenol. The fractions of phenol converted in polymers were 25, 32 and 39% respectively with Ti/IrO2, Pt and Ta/B-PbO2, a series of materials in which the O2-overvoltage increases

    Electrochemical polymerisation of phenol in aqueous solution on a Ta/PbO2 anode

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    This paper deals with the treatment of aqueous phenol solutions using an electrochemical technique. Phenol can be partly eliminated from aqueous solution by electrochemically initiated polymerisation. Galvanostatic electrolyses of phenol solutions at concentration up to 0.1 mol dm−3 were carried out on a Ta/PbO2 anode. The polymers formed are insoluble in acidic medium but soluble in alkaline. These polymers were filtered and then dissolved in aqueous solution of sodium hydroxide (1 mol dm−3). The polymers formed were quantified by total organic carbon (TOC) measurement. It was found that the conversion of phenol into polymers increases as a function of initial concentration, anodic current density, temperature, and solution pH. The percentage of phenol polymerised can reach 15%

    Geopolymer lightweight bricks manufactured from fly ash and foaming agent

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    This paper deals with the development of lightweight geopolymer bricks by using foaming agent and fly ash. The mix parameters analysed through a laboratory experiment with fix ratio of sodium silicate/sodium hydroxide solution mass ratio 2.5, fly ash/alkaline activator solution mass ratio 2.0, foaming agent/paste mass ratio 1:2 and molarity of sodium hydroxide solution used was 12M. Different curing temperature (Room Temperature, 60, 80) and foaming agent/water mass ratio (1:10 and 1:20) were studied. Compressive strength, density analysis, and water absorption has been investigated. The results show that the foamed geopolymer bricks with a lower foam/water mass ratio (1:10)and high curing temperature (80°C) leading to a better properties. Mixtures with a low density of around 1420 kg/m3 and a compressive strength of around 10 MPa were achieved
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