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    • 131. 发明申请
    • CATALYTIC-HYDROTHERMAL DISPOSAL PROCESS OF CHEMICAL MILITARY MATERIALS
    • 用于催化水处置武器的化学物质
    • WO1996034662A1
    • 1996-11-07
    • PCT/EP1995001710
    • 1995-05-05
    • UHDE GMBHHEDERER, HartmutTHIAGARAJAN, NatarajanANDERSEN, Kjeld
    • UHDE GMBH
    • A62D03/00
    • A62D3/20A62D3/35A62D2101/02A62D2101/22A62D2101/24A62D2101/26
    • The chemical military materials include both the group of chemical agents used in chemical weapons and the group of fuels used in military aircraft. Chemical military materials must be disposed of at the end of their storage life. A continuous process is disclosed for that purpose. The chemical military materials are first suspended and/or dissolved in water and an alkaline catalyst is added to the aqueous mixture. A reaction mixture is thus obtained. The reaction mixture is brought to the reaction pressure by liquid feeding means, for example a high pressure pump. The reaction pressure lies between 100 bars and 1000 bars. The reaction mixture is heated up to a reaction temperature lower than the critical temperature of pure water. The usual reaction temperature is 350 DEG C. The reaction mixture heated up to the reaction temperature then flows over a catalyst bed that contains a catalytic zirconium dioxide. The catalysed reactions produce a hot mixture of converted materials that is substantially free of chemical military materials. The hot mixture of converted materials is cooled down and expanded in a separator, producing a gaseous phase with CO2, CH4 and H2, an oily phase and an aqueous phase with dissolved salts that may all be dumped.
    • 武器的化学物质包括该组的可作为化学武器的化学战剂,以及在军用飞机使用的组的燃料。 武器的化学物质必须在其保质期后丢弃。 这是在一个连续的过程中完成的。 在此,化学武器材料首先悬浮在水和/或溶解的和水的混合物中加入碱性催化活性添加剂。 使得进料混合物生产的。 然后,与这样的液体资金进料混合物。 带来作为高压泵向反应压力。 反应压力为100巴和1000巴之间。 将进料混合物被加热到低于纯水的临界温度的反应温度。 典型的反应温度为350℃。加热到反应温度进料混合物通过催化剂床有催化作用的二氧化锆,其中所述热产生Konvertgemisch在催化的反应,这是无化学物质臂基本上通过。 热Konvertgemisch被冷却并在分离器放松。 被填埋在此,气相与CO 2,CH 4和H 2,油相和水相含有溶解的盐出现。
    • 139. 发明申请
    • COMPOSITION AND PROCESS FOR REDUCING OR PREVENTING METAL AND ACID CONTAMINATION IN ROCK DRAINAGE
    • 用于减少或防止岩石渗漏中的金属和酸污染的组合物和方法
    • WO1995017927A1
    • 1995-07-06
    • PCT/US1994014565
    • 1994-12-16
    • BUCKMAN LABORATORIES INTERNATIONAL, INC.
    • BUCKMAN LABORATORIES INTERNATIONAL, INC.KRAVETZ, Mark, E.McNEEL, Thomas, E.
    • A62D03/00
    • A62D3/33A62D2101/43B09C1/08C02F2103/06
    • The formation of contaminants in drainage from waste rock or tailings is reduced or prevented by contacting the waste rock or tailings with an organic or inorganic sulfur compound in combination with a neutralizing agent, a fixating agent or a neutralizing agent and a fixating agent. When an organic or inorganic sulfur compound is used with the neutralizing agent or fixating agent, the amount of neutralizing agent and/or the amount of fixating agent required to reduce or prevent the formation of contaminants in drainage from waste rock or tailings is substantially reduced. The amount of sulfur compound applied to the waste rock or tailings can be about 1 % to 5 % by weight and the amount of neutralizing agent and/or fixating agent applied to the waste rock or tailings can be about 1 % to about 15 % by weight, based on the weight of the waste rock or tailings. The organic or inorganic sulfur compounds are those having a sulfhydryl group or an ionized sulfhydryl group or a sulfur compound which is capable of producing a sulfhydryl group or an ionized sulfhydryl group.
    • 通过将废石或尾矿与有机或无机硫化合物与中和剂,固定剂或中和剂和固定剂组合使其接触,减少或防止从废石或尾矿排出的污染物的形成。 当有机或无机硫化合物与中和剂或固定剂一起使用时,中和剂的量和/或减少或防止从废石或尾矿排水中形成污染物所需的固着剂的量大大减少。 施加到废石或尾矿的硫化合物的量可以为约1重量%至5重量%,并且施用于废石或尾矿的中和剂和/或固化剂的量可以为约1%至约15%,通过 重量,基于废石或尾矿的重量。 有机或无机硫化合物是具有巯基或离子化巯基的化合物或能够产生巯基或电离巯基的硫化合物。
    • 140. 发明申请
    • SELECTIVE OXIDATION CATALYSTS FOR HALOGENATED ORGANICS
    • 选择性氧化催化剂用于氢化有机物
    • WO1995011726A1
    • 1995-05-04
    • PCT/US1994012244
    • 1994-10-26
    • THE UNIVERSITY OF AKRON
    • THE UNIVERSITY OF AKRONGREENE, Howard, L.RAMACHANDRAN, BalachandranCHATTERJEE, Sougato
    • A62D03/00
    • A62D3/38A62D2101/22A62D2101/28B01D53/8662B01J29/061
    • The invention relates to a process and a catalyst composition for the destruction of volatile organic compounds (VOCs). The process includes the step of contacting the VOCs with an oxygen-containing gas in the presence of a catalyst which is a metal-exchanged, metal-impregnated aluminosilicate zeolite with at least one exchanged metal in the zeolite being selected from the group consisting of Ti, V, Cr, Co, Ni, Cu, Fe, Mo, Mn, Pd, and Pt, and at least one impregnated metal in the zeolite being selected from the group consisting of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd and Pt, and wherein the difference between the exchanged metal and the impregnated metal varies the temperature necessary to promote oxidation of the compounds and for a contact time sufficient to oxidize the compounds. The process reaction temperature can vary from about 100 DEG C to about 650 DEG C and the contact time can vary from about 0.01 to 20 seconds. Preferably, the reaction temperature is from about 150 DEG C to about 450 DEG C and the contact time is from about 0.1 to 1.0 seconds. The CO/CO2 ratio and the Cl2/HCl ratio in the gaseous effluent can be varied through selection of at least two impregnating metals with at least one exchanged metal in the aluminosilicate zeolite or by the use of at least one impregnating metal with at least two exchanged metals in the aluminosilicate zeolite.
    • 本发明涉及用于破坏挥发性有机化合物(VOC)的方法和催化剂组合物。 该方法包括在催化剂存在下使VOC与含氧气体接触的步骤,催化剂是金属交换的金属浸渍的硅铝酸盐沸石,沸石中的至少一种交换金属选自Ti ,V,Cr,Co,Ni,Cu,Fe,Mo,Mn,Pd和Pt,沸石中的至少一种浸渍金属选自Ti,V,Cr,Mn,Fe,Co, Ni,Cu,Mo,Pd和Pt,并且其中交换的金属和浸渍金属之间的差异改变促进化合物氧化所需的温度和足以氧化化合物的接触时间。 工艺反应温度可以在约100℃至约650℃之间变化,接触时间可以在约0.01至20秒之间变化。 优选地,反应温度为约150℃至约450℃,接触时间为约0.1至1.0秒。 气态流出物中的CO / CO 2比和Cl 2 / HCl比可以通过在铝硅酸盐沸石中选择至少两种浸渍金属与至少一种交换的金属或通过使用至少一种浸渍金属至少两种来改变 在铝硅酸盐沸石中交换金属。