子分类：
| 序号 | 专利名 | 申请号 | 申请日 | 公开（公告）号 | 公开（公告）日 | 发明人 |
|---|---|---|---|---|---|---|
| 1 | 农药组合物及残留农药分解剂 | CN200710128481.4 | 2002-06-25 | CN101147481A | 2008-03-26 | 若村正人 |
| 一种农药组合物，其特征在于，包括：农药活性成分；粉末状的金属改性磷灰石，其磷灰石结晶结构中所包含的金属原子的一部分为光催化性金属原子。最好金属改性磷灰石在实质上被透光性的有机膜覆盖。 | ||||||
| 2 | 生物化学—热化学多点交联处理生物质废物的方法及系统 | CN201510366911.0 | 2015-06-29 | CN104958865A | 2015-10-07 | 吕凡; 何品晶; 邵立明; 章骅 |
| 本发明一种生物化学—热化学多点交联处理生物质废物的方法及系统。本发明将热化学处理子系统的固、气、液产物应用至生物化学处理子系统，将生物化学处理子系统产生的热量应用至热化学处理子系统，形成生物化学处理子系统和热化处理子系统的多点双向交互连接，从而分别提高生物化学处理子系统的能源气体产率和稳定性，降低热化学处理子系统的污染和能耗。本发明适合于同时处理高含水率和低含水率的生物质废物，产生土壤改良剂、液体燃料和生物燃气，具有二次污染低、温室气体减排效益显著的特点。其固态产物作为土壤改良剂的生物稳定性、腐殖质含量以及含氮量都较高，便于贮存和运输。 | ||||||
| 3 | 有害废料的封固 | CN98805559.7 | 1998-05-29 | CN1105693C | 2003-04-16 | D·雷奇奇 |
| 一种封固有害废物(包括重金属，如砷、汞、镍和铬残余物以及放射性物质)的方法。该方法包括将有害废物加入可固化的组合物中，形成淤浆，使淤浆固化以封固废物。可固化组合物是粉末状可流动的胶粘组合物，含有碳酸钙和苛性氧化镁。封固材料的试验表明事实上没有有害废物从混凝土状外观的固化组合物中被浸提出来。 | ||||||
| 4 | 有害废料的封固 | CN98805559.7 | 1998-05-29 | CN1258269A | 2000-06-28 | D·雷奇奇 |
| 一种封固有害废物(包括重金属,如砷、汞、镍和铬残余物以及放射性物质)的方法。该方法包括将有害废物加入可固化的组合物中,形成淤浆,使淤浆固化以封固废物。可固化组合物是粉末状可流动的胶粘组合物,含有碳酸钙和苛性氧化镁。封固材料的试验表明事实上没有有害废物从混凝土状外观的固化组合物中被浸提出来。 | ||||||
| 5 | Self-disintegrating transdermal therapeutic system with improved functionality and efficacy | JP2011502263 | 2009-03-26 | JP5444325B2 | 2014-03-19 | シュテファン・マイアー; マールギト・ヴィルツ |
| 6 | Encapsulation method of hazardous waste materials | JP50002299 | 1998-05-29 | JP4307566B2 | 2009-08-05 | レチチ，ディノ |
| 7 | Decrease of abuse potential in the dosage form of abuse materials capable | JP2006551380 | 2005-01-20 | JP2007518819A | 2007-07-12 | アンダーソン、カーター、アール．; モリス、ラッセル、エル． |
| 使用済み皮膚貼付パッチに残る乱用可能物質の残量に関係する物質乱用の可能性は、除去又は処理方法の一部として乱用可能物質と分離された抗乱用物質を結合させるシステム又は方法の提供により減少させられる。 | ||||||
| 8 | PROCEDE ET DISPOSITIF DE TRAITEMENT DE POUSSIERES DE PURGE D'USINE CIMENTIERE | EP99938069.4 | 1999-08-04 | EP1207943B1 | 2004-11-03 | FERAUGE, Hubert; COLLEE, Jean-Benoît |
| The invention relates to a method and a device for treating the purge dust (2) which is produced during a manufacturing process, especially a clinker production process, and which contains i.a. chlorinated compounds and calcic compounds. The inventive method comprises the following steps: mixing the purge dust (2) with water (4); separating the mixture (7) into a liquid phase (8) comprising the water and i.a. the soluble chlorinated compounds, and a solid phase (9) consisting of the non-water soluble substances, including the rehydrated calcic compounds; and neutralising the liquid phase (8) until it reaches the desired pH. | ||||||
| 9 | PROCEDE ET DISPOSITIF DE TRAITEMENT DE POUSSIERES DE PURGE | EP99938069.4 | 1999-08-04 | EP1207943A1 | 2002-05-29 | FERAUGE, Hubert; COLLEE, Jean-Benoît |
| The invention relates to a method and a device for treating the purge dust (2) which is produced during a manufacturing process, especially a clinker production process, and which contains i.a. chlorinated compounds and calcic compounds. The inventive method comprises the following steps: mixing the purge dust (2) with water (4); separating the mixture (7) into a liquid phase (8) comprising the water and i.a. the soluble chlorinated compounds, and a solid phase (9) consisting of the non-water soluble substances, including the rehydrated calcic compounds; and neutralising the liquid phase (8) until it reaches the desired pH. | ||||||
| 10 | Treatment of hazardous materials with aqueous air foam of polyhydroxy polymer | EP89305261.3 | 1989-05-24 | EP0345967A3 | 1990-08-08 | Stern, Richard M. c/o Minnesota Mining and |
A method of treating hazardous material or other substrate with an aqueous air foam, comprising the steps of (1) preparing an aqueous solution or dispersion comprising (a) water-soluble polyhydroxy polymer capable of complexation with the borate anion (b) polyvalent ionic complexing agent, (c) foaming agent (d) a pH modifier, and (e) water as the major component of said aqueous solution or dispersion by weight; (2) aerating said aqueous solution or dispersion to form therefrom a fluid, aqueous, aerated or air-entrained, low density foam (or air foam) which is gelable or becomes viscous, generally at least 5 seconds after its formation; and (3) spraying, contacting or otherwise applying said fluid, aqueous air foam to exposed surface of said hazardous material or other substrate. |
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| 11 | Abuse Potential Reduction in Abusable Substance Dosage Form | US15907059 | 2018-02-27 | US20180185686A1 | 2018-07-05 | Carter R. Anderson; Russell L. Morris |
| The potential for substance abuse involving residual amounts of abusable substances remaining in used skin-worn patches is reduced by the provision of a system and method for combining the abusable substance with a separate anti-abuse substance agent as part of a removal or disposal procedure. | ||||||
| 12 | SYSTEM FOR SAMPLING SEDIMENT ON A BOTTOM OF A LIQUID MEDIUM | US15537048 | 2015-12-18 | US20180002890A1 | 2018-01-04 | Guylène LE GUEN; Philippe PETARD |
| System for removing sediments from a bed of a liquid environment such as a harbor or a pond, characterized in that it comprises a conduit (30), the lower extremity of which forms a moving suction mouth (31) that is to be placed substantially at the level of the bed, and the upper extremity of which leads into the open air so that said mouth (31) is under atmospheric pressure, said system comprising means for carrying out a local stirring operation (41, 42, 43, 44, 53) within said mouth and discharging means (50, 51, 52) connecting said mouth (31) to the surface of said liquid environment, in which these sediments circulate. | ||||||
| 13 | Method for reducing contamination | US13916988 | 2013-06-13 | US08858806B1 | 2014-10-14 | Henry Wilmore Cox, Jr. |
| Certain exemplary embodiments provide methods for reducing a concentration of a contaminant associated with a medium, which can be any substance or material, such as soil, water, air, and/or fluid. In one exemplary method, the medium is treated with a ferric chelate and an oxidizing agent in amounts effective to oxidize at least a portion of the contaminant. | ||||||
| 14 | PROCESSING OF ELECTRONIC WASTE WITH SUPERCRITICAL NOBLE GASES | US13964840 | 2013-08-12 | US20140128657A1 | 2014-05-08 | William B. CARLSON; Gregory D. PHELAN |
| A method of processing a material, the method including infiltrating a first disintegration fluid into a material at a first pressure, the first disintegration fluid including at least one supercritical noble gas, the first pressure being higher than a critical pressure of the first disintegration fluid, and disintegrating the material into particles by depressurizing the material from the first pressure to a second pressure, the second pressure being lower than the critical pressure of the first disintegration fluid. | ||||||
| 15 | Self-destructing transdermal therapeutic system having improved functionality and efficacy | US13851575 | 2013-03-27 | US20130226108A1 | 2013-08-29 | Stefan MAIER; Margit Wirz |
| The invention relates to a self-destructing transdermal therapeutic system (TTS), preferably in the form of a transdermal patch, that includes an active ingredient, an agent rendering the active ingredient useless, and a perforation mechanism. The perforation mechanism allows a mobile phase to reach the agent that is capable of rendering the active ingredient useless after removing the TTS after use. The agent then comes into contact with the active ingredient and destroys the active ingredient in the presence of the mobile phase. | ||||||
| 16 | Compositions, methods, and systems for reducing contamination | US12616436 | 2009-11-11 | US08480924B1 | 2013-07-09 | Henry Wilmore Cox, Jr. |
| Certain exemplary embodiments provide methods for reducing a concentration of a contaminant associated with a medium, which can be any substance or material, such as soil, water, air, and/or fluid. In one exemplary method, the medium is treated with a ferric chelate and an oxidizing agent in amounts effective to oxidize at least a portion of the contaminant. | ||||||
| 17 | Abuse potential reduction in abusable substance dosage form | US12952516 | 2010-11-23 | US08475837B2 | 2013-07-02 | Carter R. Anderson; Russell L. Morris |
| The potential for substance abuse involving residual amounts of abusable substances remaining in used skin-worn patches is reduced by the provision of a system and method for combining the abusable substance with a separate anti-abuse substance agent as part of a removal or disposal procedure. | ||||||
| 18 | Method for removing a halogen series gas | US09986587 | 2001-11-09 | US06685901B2 | 2004-02-03 | Hachiro Hirano; Yoichi Mori; Yoshikatsu Kawabe |
| A method is provided for removing a halogen series gas, by bringing a halogen series gas into contact with a granulated product, the granulated product being obtainable by granulating, employing various methods including compression molding, extrusion molding, rotating granulation and agitation granulation, a powder of hydrogencarbonate having a mean particle diameter of primary particles 10-500 &mgr;m, wherein the granulated product has a mean particle diameter of 0.5-20 mm and a minimum average hardness that is dependent on the mean particle diameter. | ||||||
| 19 | Preparation of enzymatically active sponges or foams for detoxification of hazardous compounds | US09558512 | 2000-04-26 | US06642037B2 | 2003-11-04 | Richard K. Gordon; Bhupendra P. Doctor; Ashima Saxena; Shawn R. Feaster; Donald Maxwell; Michelle Ross; David Lenz; Keith Lejeune; Alan Russell |
| An enzymatically active reusable sponge or foam, capable of regeneration with oximes, made of a polymer such as polyurethane is prepared for detoxification of hazardous compounds such as organophosphorus and organosulfur compounds. The foam or sponge contains a plurality of enzymes including enzymes selected from acetylcholinesterase, butyrylcholinesterase, triesterase, pseudocholinesterase, organophosphate hydrase, phosphotriesterase, paraoxonase and organophosphorus and organosulfur hydrolyzing enzymes. The sponge or foam may additionally contain activated carbon and an enzyme reactivation compound. A kit can be formed containing the sponge or foam and the compound for enzyme reactivation. The enzymatically active foam or sponge may be prepared using a two chamber device where enzymes and prepolymer are passed from separate chambers into a static mixing stator and are subjected to low shear mixing and extrusion to form by the sponge or foam. | ||||||
| 20 | Method for removing a halogen series gas | US09986587 | 2001-11-09 | US20020068032A1 | 2002-06-06 | Hachiro Hirano; Yoichi Mori; Yoshikatsu Kawabe |
| A method for removing a halogen series gas, which comprises bringing a halogen series gas comprising a halogen element or a halogen compound into contact with a granulated product, wherein the granulated product is obtained by granulating a powder of a hydrogencarbonate having a mean particle diameter of primary particles of from 10 to 500 nullm, and has a mean particle diameter of from 0.5 to 20 mm and an average hardness as defined below: in a case where the granulated product has a mean particle diameter of at least 0.5 mm and less than 1.0 mm, the average hardness of granulated product particles having particle diameters of at least 0.5 mm and less than 1.0 mm is at least 1 N; in a case where the granulated product has a mean particle diameter of at least 1.0 mm and less than 1.5 mm, the average hardness of granulated product particles having particle diameters of at least 1.0 mm and less than 1.5 mm is at least 4 N; in a case where the granulated product has a mean particle diameter of at least 1.5 mm and less than 2.0 mm, the average hardness of granulated product particles having particle diameters of at least 1.5 mm and less than 2.0 mm is at least 10 N; and in a case where the granulated product has a mean particle diameter of from 2.0 mm to 20 mm, the average hardness of granulated product particles having particle diameters of at least 2.0 mm is at least 30 N. | ||||||
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