| 序号 | 专利名 | 申请号 | 申请日 | 公开（公告）号 | 公开（公告）日 | 发明人 |
|---|---|---|---|---|---|---|
| 41 | Tetsukopurantohaikibutsunomudokukahoho | JP15662888 | 1988-06-24 | JPH0230753B2 | 1990-07-09 | JON KENISU PAAGETAA |
| 42 | Removal of pcb and other hologenated organic compound from organic liquid | JP18098983 | 1983-09-30 | JPS59131373A | 1984-07-28 | RUISU ERU PITOREUSUKII; FURANKU JIEI IAKONIAANI; KENESU KUREBUITSUTSU; AASAA BII SUMISU |
| 43 | 폐슬레이트의 석면 무해화 처리 방법, 및 이렇게 하여 얻은 무해화된 석면 | KR1020130072999 | 2013-06-25 | KR101326741B1 | 2013-11-08 | 장영남; 송경선; 이명규; 채수천; 조환주; 방준환; 유경원 |
| Disclosed is a method for detoxifying asbestos of waste slate. The method for detoxifying asbestos of waste slate comprises steps of: adding aqueous hydrochloric to waste slate powder and decomposing and removing limestone component contained in the waste slate powder in order to concentrate asbestos; and mixing the concentrated asbestos with oxalate and low heat treating the same. Here, the waste slate including asbestos is desirable to be smashed and ground, and the particle size of the smashed and ground waste slate powder is desirable to be 100-300 meshes. In the detoxified asbestos, recrystallized rhombohedral or amorphous magnesium oxalate is included. [Reference numerals] (S100) Pulverizing and crushing waste slate including asbestos;(S200) Adding aqueous hydrochloric to pulverized and crushed waste slate powder (remove limestone and concentrate asbestos);(S300) Low temperature heat treating the concentrated asbestos and organic acid mixture | ||||||
| 44 | 물질의 산화 방법 및 그 산화 장치 | KR1020067024131 | 2005-05-18 | KR1020070020037A | 2007-02-16 | 소토아카류지; 키무라요시야 |
| Disclosed are a method for oxidizing a substance in a liquid containing dinitrogen monoxide (N2O) and an oxidation apparatus. In this method, a substance is placed in a solution containing dinitrogen monoxide (N2O), and the solution is irradiated with light including at least a wavelength not more than 240 nm, thereby oxidizing the substance. ® KIPO & WIPO 2007 | ||||||
| 45 | 고체폐기물처리제및고체폐기물처리방법 | KR1019990004478 | 1999-02-09 | KR1019990072523A | 1999-09-27 | 가와시마마사따께; 오가와다까시; 데라다가즈히로; 오까야마히로유끼; 스기야마가쓰시; 호소다가즈오; 모리야마사후미 |
| 본발명에는아인산또는그의유도체및/또는차아인산또는그의유도체, 또는아인산또는그의유도체및/또는차아인산또는그의유도체, 및알루미늄및/또는티타늄화합물을포함하는고체폐기물처리제와, 디옥신및 PCB 와같은유해금속및/또는유기염소화화합물을함유하는고체폐기물에고체폐기물처리제를가하여, 고체폐기물을무해하도록만드는것을포함하는고체폐기물처리방법이개시되어있다. 아인산또는그의유도체및/또는차아인산또는그의유도체및 산화티타늄, 또는아인산또는그의유도체및/또는차아인산또는그의유도체, 산화티타늄및 알루미늄화합물을포함하는고체폐기물처리제가광 조사하에서고체폐기물처리를위한고체폐기물처리제로사용되는경우, 처리가상대적으로저온인경우에서도고체폐기물이효과적으로무해하게된다. | ||||||
| 46 | 중금속을 포함한 폐기물의 처리방법 및 처리장치 | KR1019960701953 | 1995-08-10 | KR100201520B1 | 1999-06-15 | 하야시요시히로; 야마네다케시; 간난마사키; 고지마아키라 |
| 중금속을 포함하는 폐기물을 무해화하기 위해 처리하는 방법 및 장치가 제공된다. 방법에 있어서, 폐기물에는 산화철 또는 산소의 존재하에서 가열에 의해 산화철을 생성하는 재료와 탄소등의 환원제가 첨가된다. 얻어진 혼합물은 건식법에 있어서 가열되며 페라이트를 생성한다. 중금속은 페라이트 중에 고정화되며 폐기물은 안전에서 또한 유용한 페라이트 재료로 변환된다. 처리 장치는 반응로(18), 원료 공급 장치(10, 12, 14, 16), 교반 장치(22), 복사 가열기(20), 휘발성 금속 회수 장치(26), 및 집진기(28)를 구비한다. | ||||||
| 47 | 불소계 유기 화합물의 분해 방법 및, 불소계 유기 화합물의 분해 장치 | KR1020150046831 | 2015-04-02 | KR1020150118532A | 2015-10-22 | 호리히사오; 가토마사아키 |
| (과제) 새롭고효율이좋은불소계유기화합물의분해방법및 그러한방법을실시하는데에유용한불소계유기화합물의분해장치를제공하는것이다. (해결수단) 본발명은, 분해대상인불소계유기화합물에대하여, 전해황산의존재하에서광조사하는것을특징으로하는불소계유기화합물의분해방법이다. 즉, 황산수용액을전기분해했을때에양극측에서얻어지는전해황산에, 분해대상이되는불소계유기화합물을더하여광조사를행함으로써, 그불소계유기화합물을불소이온이나이산화탄소까지분해시키는것을특징으로한다. 이에따라, 종래와같이고온에서연소하여불소계유기화합물을분해할필요가없어져, 분해를위한에너지비용을삭감할수 있다. | ||||||
| 48 | 물질의 산화 방법 및 그 산화 장치 | KR1020067024131 | 2005-05-18 | KR101160373B1 | 2012-06-26 | 소토아카류지; 키무라요시야 |
| 본 발명은 아산화질소(N 2 0)를 포함한 액중에서 물질을 산화시키는 산화 방법 및 산화 장치를 제공하는 것이다. 아산화질소(N 2 0)를 포함한 용액중에 물질을 존재시키고, 상기 용액에 대해 적어도 240 nm 이하의 파장을 포함하는 빛을 조사함으로써 물질의 산화를 수행한다. | ||||||
| 49 | 오염된 퇴적물 및 토양의 열화학적 개질 및 정화 방법 | KR1019997005702 | 1997-12-23 | KR100449553B1 | 2004-09-21 | 카오리차드엘; 랜드하바사라브예이트에스; 랜드하바수르예이트에스; 멘싱거마이클씨; 레호맷아미레일지; 리안쏘니엘 |
| This invention relates to thermo-chemical remediation and decontamination of sediments and soils contaminated with organic contaminants as well as inorganic materials with subsequent beneficial reuse. Novel environmentally stable products of commercial value are produced when certain additives such as calcium and metal oxides are mixed with the contaminated materials. In the process, the mixture is heated to 1150 DEG C. DIFFERENCE 1500 DEG C. to produce a molten reaction product with at least part of an excess amount of oxygen mixture or air is continuously bubbled through the melt in order to provide mixing and achieve high thermal destruction and removal efficiencies of the organic contaminants. The melt is then quickly quenched in moist air, steam, or water to avoid the transformation of the amorphous material into crystals. The inorganic contaminants such as chromium, nickel, zinc, etc. are incorporated and completely immobilized within the amorphous silicate network. The amorphous material can be pulverized to yield a powder which evinces cementitious properties either by reaction with alkali solution or by blending it with other materials to produce blended cements. The compressive strengths of the concretes made from the powder of the subject invention and blends thereof are comparable to, or greater than the ASTM requirements for general purpose concrete applications. The powder of the subject invention, blended cements, and concrete/mortar derived therefrom also easily pass the EPA TCLP leach test to achieve environmental acceptability. | ||||||
| 50 | 황산염환원균을 이용한 소각재 처리방법 | KR1019990034333 | 1999-08-19 | KR100283403B1 | 2001-02-15 | 정권 |
| 본발명은소각재황산염환원균을이용하기위하여, 기존의매립시설구조에매립물의상호보완적특성을고려하여합리적이며계획적으로매립하여소각재의중금속을불용화시키고유기물의안정화를유도하는소각재처리방법에관한것으로, 소각재에황산염환원균을포함하는유기성폐기물을함께매립하여상기황산염황원균이상기소각재내의황산염을환원시켜그 결과로생성된황화물을상기소각재내의중금속과결합시켜불용성금속황화물로침전시키도록구성되는소각재처리방법과소각재내의중금속을황산염환원균이불용성금속황화물로침전시키도록소각재및 황산염환원균을포함하는유기성폐기물을함께매립하고복토를덮어매립물을형성하는소각재처리방법을제공하며, 황산염환원균에의하여소각재의중금속을안전한금속황화물로침전시켜고형화시킬수 있으며, 그결과로소각재를처리함에있어서중금속의용출로인한주변의토양및 수질오염의가능성을획기적으로줄일수 있다. | ||||||
| 51 | Method for processing peroxygen solutions | US13038171 | 2011-03-01 | US09254400B2 | 2016-02-09 | John D. Hilgren; Jelte Lanting; Roger John Arthur Tippett |
| The present disclosure relates to a multi-step method for processing peroxygen solutions for reuse or disposal. The method uses an enzyme and a reducing agent. | ||||||
| 52 | METHOD AND APPARATUS OF DECOMPOSING FLUORINATED ORGANIC COMPOUND | US14682018 | 2015-04-08 | US20150290484A1 | 2015-10-15 | Hisao Hori; Masaaki Kato |
| A method of decomposing a fluorinated organic compound involves irradiating a target fluorinated organic compound with light in the presence of electrolyzed sulfuric acid. In detail, the inventive method involves adding electrolyzed sulfuric acid prepared by electrolysis of an aqueous sulfuric acid solution at an anode to a solution containing the target fluorinated organic compound and irradiating the solution with light to decompose the fluorinated organic compound into fluoride ions and carbon dioxide. The method can decompose fluorinated organic compounds at reduced decomposition energy, without high-temperature incineration that has been conventionally required. An apparatus for decomposing a fluorinated organic compound is also provided that is utilizable in practicing the method. | ||||||
| 53 | Degradation of nanomaterials | US12603104 | 2009-10-21 | US08530227B2 | 2013-09-10 | Alexander Star; Valerian E. Kagan; Brett Lee Allen |
| A method of degrading carbon nanomaterials includes mixing the carbon nanomaterials with a composition comprising a peroxide substrate and at least one catalyst selected from the group of an enzyme and an enzyme analog. The peroxide substrate undergoes a reaction in the presence of the catalyst to produce an agent interactive with the nanotubes to degrade the carbon nanomaterials. The peroxide substrate can, for example, be hydrogen peroxide or an organic peroxide. | ||||||
| 54 | Process for the destruction of sulfur and nitrogen mustards, lewisite, and their homologous/analogues in deep eutectic solvents | US12078012 | 2008-03-26 | US20120149964A1 | 2012-06-14 | Inas Muen Al Nashef; Saeed M. Al Zahrani |
| The subject invention provides a potentially economically viable process for the destruction of small to large quantities of sulfur and nitrogen mustards and lewisite, their homologous/analogues, and similar chemical warfare agents at ambient conditions without producing any toxic by-products. The process uses the superoxide ion that is either electrochemically generated by the reduction of oxygen in deep eutectic solvents or chemically by dissolving Group 1 (alkali metals) or Group 2 (alkaline earth metals) superoxides, e.g. potassium superoxide, in deep eutectic solvents. | ||||||
| 55 | PROCESS FOR THE DESTRUCTION OF TOXIC RESIDUES VIA OXIDATION IN PRESENCE OF WATER AND OXYGEN AND CONTINUOUS MOBILE UNIT TO TREAT HAZARDOUS COMPOUNDS | US13133195 | 2009-12-17 | US20110237857A1 | 2011-09-29 | Gustavo Eduardo Bolanos Barrera; Victor Fernando Marulanda Cardona |
| Process for the destruction of toxic residues via oxidation in the presence of water and oxygen developed in homogenous phase at temperatures over 374° C. and pressure of at least 220 atmospheres and a continuous mobile unit easily transferred to treat effluents or contaminated media. This mobile unit is composed of a reactor, which includes pressurization, reaction, cooling, depressurization and sampling zones for the destruction of toxic residues like polychloride biphenyls (PCBs), pyridines, and other hazardous compounds. | ||||||
| 56 | METHOD OF DETOXIFYING A METHYL COMPOUND | US12309992 | 2007-11-28 | US20100228073A1 | 2010-09-09 | Koichiro Nakamura; Akihiro Hishinuma; Shinji Kamiya |
| It is an object of the present invention to provide a method of detoxifying a methyl compound comprising arsenic etc., effectively and systematically. The method of detoxifying a methyl compound according to the present invention is characterized in that an organic halogenated compound is reacted with a methyl compound comprising at least one element selected from the groups comprising arsenic, antimony and selenium to convert the methyl compound into more harmless substances. Furthermore, in a preferred embodiment of the method of detoxifying a methyl compound according to the present invention, the method is characterized in that the element is arsenic. | ||||||
| 57 | DEGRADATION OF NANOMATERIALS | US12603104 | 2009-10-21 | US20100190239A1 | 2010-07-29 | ALEXANDER STAR; VALERIAN E. KAGAN; BRETT LEE ALLEN |
| A method of degrading carbon nanomaterials includes mixing the carbon nanomaterials with a composition comprising a peroxide substrate and at least one catalyst selected from the group of an enzyme and an enzyme analog. The peroxide substrate undergoes a reaction in the presence of the catalyst to produce an agent interactive with the nanotubes to degrade the carbon nanomaterials. The peroxide substrate can, for example, be hydrogen peroxide or an organic peroxide. | ||||||
| 58 | Large-volume elimination of airborne chemical and biological warfare agents by making use of a microwave plasma burner | US11409011 | 2006-04-24 | US20100048975A1 | 2010-02-25 | Han Sup Uhm; Dong H. Shin; Yong C. Hong |
| The invention is related to an apparatus made of microwave plasma burner for a large-volume elimination of toxic airborne chemical and biological warfare agents. The apparatus can purify the interior air of large volume in an isolated space such as buildings, public transportation systems, and military vehicles contaminated with chemical and biological warfare agents. The apparatus consists of a microwave plasma torch connected in series to a fuel injector and a reaction chamber for elimination and burnout of toxic airborne warfare agents in large quantities. Hydrocarbon fuel in gaseous or liquid state injected into the microwave plasma torch evaporates instantaneously, generating a large volume of plasma flame in the reaction chamber where the oxidation mechanism eliminates the chemical and biological warfare agents that pass through the reaction chamber. The apparatus can also purify air contaminated with volatile organic compounds and eliminate soot from diesel engines. | ||||||
| 59 | ACYL Transferase Useful for Decontamination | US12085721 | 2006-12-08 | US20090311395A1 | 2009-12-17 | Marguerite A. Cervin; Gregg Whited |
| The present invention provides an enzyme system that efficiently generates peracetic acid for use in decontamination applications. In preferred embodiments, the present invention provides a system that comprises an ester substrate, a hydrogen peroxide, and at least one acyl transferase. In some particularly preferred embodiments, the system further comprises at least one surfactant. In alternatively preferred embodiments, the present invention provides at least one wild-type and/or variant acyl transferase. The present invention finds particular use in decontamination involving a wide variety of chemical and biological warfare materials, as well as for general surface cleaning and decontamination. | ||||||
| 60 | Detoxification of chemical agents | US11981079 | 2007-10-31 | US20090112044A1 | 2009-04-30 | Ravi Jain; Abhinav Jain |
| This invention provides a process for the detoxification of chemical agents including chemical warfare agents such as sulfur mustards, nitrogen mustards, nerve agents of G and V type, lewisite and adamsite by reacting the chemical agents with hydroxyl radicals at a pH greater than 7.0 to detoxify the agents and to render them suitable for disposal. The process can be used on-site and can be easily scaled to fairly large sizes. | ||||||
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