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    • 35. 发明授权
    • Recovery of sulfur dioxide from sulfuric acid containing ferrous sulfate
    • 从含硫酸亚铁的硫酸中回收二氧化硫
    • US3906039A
    • 1975-09-16
    • US33841673
    • 1973-03-06
    • ZIEREN CHEMIEBAU GMBH DR A
    • FURKERT HERBERT
    • C01B17/50C01B17/58
    • C01B17/58Y10S423/02
    • In a process for the production of a gas containing sulfur dioxide from a dilute aqueous sulfuric acid stream containing iron (II) sulfate and approximately 10-40% by weight H2SO4, e.g. pickle liquor or waste H2SO4 from TiO2 production, comprising concentrating the acid in an evaporation stage, and reductively cracking the concentrating acid in a cracking stage at temperatures of between 850* and 1,100* C. to a hot cracked gas containing SO2 and metallic oxides, THE IMPROVEMENT COMPRISING EVAPORATING THE 10-40% STRENGTH SULFURIC ACID TO 55-70% STRENGTH SULFURIC ACID BY DIRECT HEAT EXCHANGE WITH THE HOT CRACKED GAS; SIMULTANEOUSLY FORMING PRECIPITATE CONTAINING IRON (II) sulfate; and passing resultant evaporated sulfuric acid to the cracking stage. The resultant cracked gas containing metallic oxides, aluminum and magnesium oxides in particular, is purified by the direct heat exchange treatment insofar as the metallic oxides are scrubbed out and become enmeshed in the sulfate precipitate.
    • 在从含硫酸铁(II)和约10-40重量%H 2 SO 4的稀硫酸水流中生产含二氧化硫的气体的方法中, 酸洗液或废H2SO4,包括在蒸发阶段浓缩酸,并将浓缩酸在850-1100℃的温度下,在含有SO 2和金属氧化物的热裂解气中进行还原性裂化, 包括将10-40%强酸性硫酸蒸发至具有热裂解气体的直接热交换的55-70%强酸性硫酸的改进; 同时形成含硫酸铁(II)的预硫化物; 并将所得蒸发的硫酸通入裂化阶段。 所形成的含金属氧化物,特别是铝和镁的氧化物的裂化气体,通过直接热交换处理进行纯化,只要金属氧化物被洗去并变成含硫酸盐沉淀物。
    • 40. 发明授权
    • Reduction of pyrosulfite
    • 减少磷灰石
    • US3649182A
    • 1972-03-14
    • US3649182D
    • 1968-12-24
    • WELLMAN LORD INC
    • MILLER LEO ATAYLOR JAMES AWILLARD THOMAS M
    • C01B17/24C01B17/50C01B17/28
    • C01B17/24C01B17/501
    • A process for treating metal pyrosulfites such as potassium, cesium, and rubidium pyrosulfites to obtain SO2 therefrom is disclosed. The pyrosulfite is reduced with a reducing agent such as hydrogen while in physical admixture with an inert, inorganic, refractory, particulate solid, a eutectic mixture of which with the desired metal sulfide has a melting point greater than the reduction zone temperatures, preferably greater than 1,650* F. Advantageously, the refractory solid for the reduction zone mixture is provided by introducing to the zone a pelletized admixture of the metal pyrosulfite with a hydrate of the refractory solid which, upon being heated to the reduction zone temperatures, will release water of hydration and be converted in situ to the refractory solid. Especially preferred is the use of pelletized admixtures of hydrous aluminum oxide and the metal pyrosulfite, the hydrous aluminum oxide being converted to alumina with the release of water when subjected to the reduction zone temperatures. The process can be employed with particular advantage where the pyrosulfite is obtained as a result of reacting SO2-containing gases with an aqueous absorbing solution of the corresponding metal sulfite to produce a spent absorbing solution containing dissolved metal bisulfite, and then recovering the metal bisulfite therefrom in the form of the corresponding metal pyrosulfite (e.g., by cooling the spent absorbing solution to crystallize out the pyrosulfite). The metal sulfide product obtained can be dissolved in water and the resulting solution treated with CO2 to provide hydrogen sulfide and the corresponding metal carbonate (which can be recycled to the SO2 absorption reaction). The H2S from the latter step may be mixed with the SO2 obtained from the reducing step and the mixture subjected to the Claus reaction to produce elemental sulfur and water.
    • 公开了一种处理金属焦亚硫酸盐如钾,铯和焦亚硫酸铷以获得SO 2的方法。 焦亚硫酸盐与还原剂如氢气还原,同时与惰性,无机,耐火的颗粒固体物理混合,其中所需金属硫化物的共晶混合物具有大于还原区温度的熔点,优选大于 有利的是,用于还原区混合物的耐火固体是通过向该区域引入焦亚硫酸金属盐与耐火固体的水合物的造粒混合物来提供的,当被加热到还原区时,温度将释放 水化并原位转化成难熔固体。 特别优选的是使用水合氧化铝和焦亚硫酸金属的颗粒化混合物,当经受还原区温度时,水合氧化铝被转化成氧化铝并释放水。 该方法可以具有特别的优点,其中由于使含SO 2的气体与相应的金属亚硫酸盐的吸收水溶液反应而获得焦亚硫酸盐,以产生含有溶解的亚硫酸氢盐的废吸收溶液,然后从其中回收金属亚硫酸氢盐 以相应的金属焦亚硫酸盐的形式(例如,通过冷却废吸收溶液以结晶出焦亚硫酸盐)。 获得的金属硫化物产物可以溶于水,所得溶液用二氧化碳处理,提供硫化氢和相应的金属碳酸盐(可以再循环到SO2吸收反应中)。 来自后一步骤的H 2 S可以与从还原步骤获得的SO 2混合,并进行克劳斯反应的混合物以产生元素硫和水。