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    • 91. 发明授权
    • Compacting method and apparatus, particularly adapted to compacting
hazardous materials
    • 压实方法和装置,特别适用于压实危险材料
    • US5613433A
    • 1997-03-25
    • US464868
    • 1995-06-28
    • Daniel TucoulatPatrick JacqPhilippe KerrienDaniel Kerlau
    • Daniel TucoulatPatrick JacqPhilippe KerrienDaniel Kerlau
    • G21F9/30B30B9/30B30B9/32G21F9/36
    • B30B9/3042B30B9/30B30B9/327G21F9/36Y10S100/902
    • A compacting method and apparatus particularly adapted to compacting hazardous materials, and in particular radioactive waste, in which a container (1, 1', 1", 1"') is compacted inside a compacting skirt (20) by cooperation between a support surface (7) on which the compacting skirt (20) with the container (1') is placed and a compactor (9) disposed faing the support surface (7) and displaceable along a vertical axis inside the compacting skirt (20). According to the compacting method the compacting skirt (20) containing the container (1, 1', 1", 1"') is moved in translation, in particular between a loading station (I) for loading the container (1), a compacting station (II) where the container (1') is compacted, and an unmolding station (III) for unmolding the compacted container (1") and for evacuating the compacted container (1"') downwards.
    • PCT No.PCT / FR94 / 00040 Sec。 371日期:1995年6月28日 102(e)日期1995年6月28日PCT 1994年1月13日PCT PCT。 公开号WO94 / 16449 日期1994年7月21日一种特别适用于压实危险材料,特别是放射性废物的压实方法和装置,其中容器(1,1',1“,1”)在压实裙部(20 )通过其上放置有压实裙部(20)的支撑表面(7)与设置在支撑表面(7)之间的压实机(9)之间的协作,并且可沿着压实中的竖直轴线移位 裙子(20)。 根据压实方法,容纳容器(1,1',1“,1”)的压实裙部(20)平移地移动,特别是在用于装载容器(1)的装载站(I) ,其中容器(1')被压实的压实站(II)和用于将压实的容器(1“)解模并用于将压实的容器(1”)向下抽空的非模制工位(III)。
    • 95. 发明授权
    • Method and apparatus for waste vitrification
    • 废玻璃化的方法和设备
    • US5550857A
    • 1996-08-27
    • US485625
    • 1995-06-07
    • Ray S. Richards
    • Ray S. Richards
    • C03B5/00C03B5/027C03B5/033C03B5/187G21F9/30C03B5/02
    • G21F9/305C03B5/005C03B5/027C03B5/033C03B5/1875C03B5/26Y02P40/52Y02P40/57Y10S422/903
    • A waste vitrification apparatus (10) having rotatable mixer impeller (16) functioning as a shaft electrode (60) and metallic vessel (14) functioning as a vessel electrode (62). A stream (12) of waste material and vitrifiable material are mixed and melted in the vessel (14) for vitrification. The waste vitrification method converts a feed stream (12) by mixing the feed stream into a glass melt (13) and melting glass batch of the feed stream (12) to form a foamy mass. The stream is dispersed by the impeller (16) to form a foam which is then densified in a settling zone (22), recovered through a spout (24) and solidified in storage containers. An adjuster adjusts the location of the mixing impeller (16) in the vessel (14) to change the depth of the settling zone (22). The impeller (16) is mounted on a drive shaft (18) having a recirculating coolant flow.
    • 一种具有用作轴电极(60)的旋转混合器叶轮(16)和用作容器电极(62)的金属容器(14)的废玻璃化装置(10)。 将废物和玻璃化物质的料流(12)混合并熔化在容器(14)中用于玻璃化。 废玻璃化方法通过将进料流混合到玻璃熔体(13)中并将进料流(12)的熔融玻璃批料混合以形成泡沫体来转化进料流(12)。 流由叶轮(16)分散以形成泡沫,然后在沉降区(22)中致密化,通过喷口(24)回收并固化在储存容器中。 调节器调节容器(14)中的混合叶轮(16)的位置以改变沉降区(22)的深度。 叶轮(16)安装在具有循环冷却剂流的驱动轴(18)上。
    • 96. 发明授权
    • Method of vitrifying high-level radioactive liquid waste
    • 玻璃化高放射性废液的方法
    • US5530174A
    • 1996-06-25
    • US520786
    • 1995-08-30
    • Kazuhiro KawamuraMasayuki YoneyaKenichi Sasage
    • Kazuhiro KawamuraMasayuki YoneyaKenichi Sasage
    • G21F9/16G21F9/30G21F9/00
    • G21F9/305
    • A method of vitrifying a high-level radioactive liquid waste comprising removing a precipitate composed mainly of Mo and Zr from the high-level liquid waste, mixing the resulting high-level liquid waste with a raw glass material having a chemical composition wherein the B.sub.2 O.sub.3 /SiO.sub.2, ZnO/Li.sub.2 O and Al.sub.2 O.sub.3 /Li.sub.2 O ratios are at least 0.41, at least 1.00 and at least 2.58, respectively, and melt-solidifying the mixture to thereby form a vitrified waste. By using such a raw glass material, there can be obtained a vitrifled waste having the waste content of about 45% by oxide weight in which the same leaching rate as that of a conventional vitrified waste having the waste content of 25% by oxide weight is ensured without suffering from yellow phase separation.
    • 一种对高级放射性废液进行玻璃化的方法,包括从高级废液中除去主要由Mo和Zr组成的沉淀物,将所得高级废液与具有化学组成的原料玻璃材料混合,其中B 2 O 3 / SiO 2,ZnO / Li 2 O和Al 2 O 3 / Li 2 O比分别为至少0.41,至少1.00和至少2.58,并将混合物熔融固化,从而形成玻璃化废物。 通过使用原料玻璃材料,可以得到废氧含量为约45%的玻璃化废物,其氧化物重量与通过氧化物重量为25%的废物含量相同的常规玻璃化废物的浸出率相同 确保没有黄相分离。
    • 97. 发明授权
    • Methods of decontaminating mercury-containing soils
    • 去除含汞土壤的方法
    • US5516968A
    • 1996-05-14
    • US472505
    • 1995-06-07
    • Albert E. Abel
    • Albert E. Abel
    • A62D3/34A62D3/36A62D101/22A62D101/24A62D101/26A62D101/28A62D101/43B09C1/00B09C1/02B09C1/08C22B7/00C22B43/00C22B60/02G21F9/00G21F9/08G21F9/12G21F9/28G21F9/30
    • C22B60/0247B09C1/02C22B17/04C22B43/00C22B7/008G21F9/002G21F9/30Y02P10/122Y02P10/126Y02P10/234
    • Soil including sand and clays contaminated with elemental mercury are decontaminated by forming slurries with anhydrous liquid ammonia. An ammoniacal liquid, such as anhydrous liquid ammonia facilitates decontamination by breaking up soil into fine slurries for releasing droplets of mercury metal. The high density of the mercury metal permits precipitation with larger soil particles and for recovery from soil particulates. Contaminated soils having mixed wastes comprising metallic mercury with organic compounds like PCBs are decontaminated first by slurring with anhydrous liquid ammonia to release droplets of mercury for coalescing and recovery. Solvated electrons are formed in the slurry in-situ by treating the slurry with an alkali metal or alkaline earth metal to reduce or degrade toxic organic compounds to more environmentally benign substances. Mixed waste comprising elemental mercury and nuclear waste, such as radionuclides like plutonium and uranium in the fines of soil and clay can also be concentrated to yield residual soil products which are sufficiently free of contaminants to allow reclamation. Economics are improved over aqueous systems since ammonia can be recovered and recycled. By concentrating nuclear wastes in soil fines space requirements ordinarily needed for storage of untreated soil and handling costs can be significantly reduced.
    • 包括用元素汞污染的沙子和粘土的土壤通过用无水液氨形成浆料来净化。 氨水液体如无水液氨通过将土壤分解成细小的浆液来释放汞金属液滴,有助于净化。 汞金属的高密度允许用较大的土壤颗粒沉淀并从土壤颗粒中回收。 含有金属汞和有机化合物如PCBs的混合废物的污染土壤首先通过用无水液态氨进行去污去除,以释放出汞的液滴以进行聚结和回收。 通过用碱金属或碱土金属处理浆料以原位形成溶液中的电子,以将有毒有机化合物降解或降解为更环境友好的物质。 包括元素汞和核废料在内的混合废物,如土壤和粘土细粉中的钚和铀等放射性核素也可以被浓缩,产生残留的土壤产物,这些残留的土壤产品不含污染物以允许回收。 由于氨可以回收和再循环,因此经济性比水系统得到改善。 通过将核废料集中在土壤细粉中,通常需要通常用于储存未处理土壤和处理成本的空间要求可以大大降低。