Method of processing fluid products of low-temperature carbonization of hydrocarbon-containing raw m
专利摘要:
In a process for further treatment of carbonisation products, which are obtained in the carbonisation of waste materials, by liquid-phase hydrogenation in the presence of a disposable catalyst and/or disposable catalyst support, problematic wastes such as plastic wastes, hydrocarbon-contaminated residues, contaminated soils, biomasses and waste sludges, which preclude disposal in a landfill, are to be treated by a suitable process in such a way that no pollution of the environment by polycyclic hydrocarbons and/or chlorinated hydrocarbons is to be feared. The treatment of the problematic wastes is effected by carbonisation and subsequent further processing of the carbonisation products by liquid-phase hydrogenation. …<??>The disposable catalyst and/or disposable catalyst support or additive used is an internally or externally arising carbonisation coke or lignite coke which can have been impregnated with catalytically active metals or salts thereof. …<??>The process is suitable for the treatment of problematic hydrocarbon-containing wastes. Furthermore, the products obtained can, as products of value, be further utilised. 公开号:SU1766265A3 申请号:SU894613534 申请日:1989-02-24 公开日:1992-09-30 发明作者:Мерц Лудвиг;Ниманн Клаус;Веннинг Ханс-Петер 申请人:Феба Ель Энтвиклюнгс-Гезельшафт, Гмбх (Фирма); IPC主号:
专利说明:
The invention relates to a method for processing liquid semi-coking products of oil-contaminated bottom sediments, hydrocarbon sludges. Depending on the type and origin of the waste products subject to coking, various harmful substances are contained in the products of coking. Along with the so-called harmful substances inherent in the system, which are contained in waste products even before the semi-coking process, special attention should be paid to harmful substances specific to the process. Under reducing conditions of the semi-coking process, along with the main components, hydrogen, carbon monoxide, carbon dioxide, methane and water, hydrogen compounds such as ammonia, hydrogen sulfide, hydrogen cyanide compounds, hydrochloride compounds and hydrogen fluoride, as well as among other NOX and vuokis sulfur. A known patent which relates to a method for producing petrochemical products by hydrodisintegrating heavy liquids from hydrocarbon pyrolysis. In contrast to the claimed method, the patent concerns, therefore, other starting materials, i.e. pyrolysis vat residue, also used in furnaces to generate energy. Together with the semi-coke, used as a disposable catalyst and, accordingly, with the added substance, or with brown coal, other ma-VIs are also used. ten oh oh SP Igj materials as catalysts for hydrolysis. Depending on the type and composition of the waste materials subject to coking, the pyrolysis process has different requirements. The economics of these processes should always be considered in conjunction with their environmental impact. Minimizing the release of heavy metals, acid gases and polycyclic chlorinated hydrocarbons requires a large amount of technical effort. Pyrolysis products can most easily be used, especially with a heterogeneous composition of waste, only energetically. The aim of the invention is to increase the efficiency of the method, i.e. to be able to recycle certain wastes so that there is no need to fear any environmental impacts of polycyclic hydrocarbons or chlorohydrocarbons and that, in addition, a known portion of the products obtained as valuable products could be used again. c) this task is solved by the fact that in the method of processing liquid semi-coking products of hydrocarbon-containing raw materials obtained at a temperature of 500-550 ° C for an hour, by liquid-phase hydrogenation at a temperature of 450-470 ° C, hydrogen pressure of 220-280 bar in the presence of a catalyst in As the semi-coking liquid products, semi-coking tar of oil-contaminated bottom sediments, hydrocarbon-containing sludges is used, and semi-coke obtained in the process of semi-coking, taken in an amount of 1 wt.% liquid products, and the process is carried out at a hydrogen: feedstock ratio of 2000 l / kg and a specific feed rate of 1 kg / lh. The waste materials that are recycled after possible heating in the preheater are fed into the semi-coking drum. The latter, in the preferred form of the method, is heated indirectly through the walls of the drum. As a gas fuel, as a rule, flue gas is used, which is formed by combustion of semi-coking gas, which is produced in the semi-coking process. Already during loading, basic additives can be added, for example, lime, in order to bind acidic gases formed during semi-coking. The amount and genus of acid gases formed or released depends on the genus. applied materials. By the way in the processing of waste containing chlorine, CO2, NOx, and also HCI may occur. After partial condensation of the semi-coking vapors removed from the semi-coking drum, oil and semi-coking tar are obtained, as well as non-condensing semi-coking fractions, formed during the semi-coking process 0 polycyclic aromatic hydrocarbons and asphaltenes, as well as polychlorinated aromatic hydrocarbons formed in the presence of chlorine, are contained in the condensate. 5 Poluklks removed directly from the drum. It is highly free of organic material and is not leached with water. The obtained oil or tar of the semi-coke after heat exchange with the treated one, after extraction through the sluice device of the fraction containing residues, is placed in a downstream from the liquid-phase hydrogenation into the liquid-phase 5 reactor. The product remaining in the liquid-phase reactor is directed in a known manner through a thermal separator operating at a reaction pressure and at a temperature preferably lower relative to the reaction temperature from 20 to 50 ° C. Here, non-condensable hydrocarbons are discharged through the head and liquid-containing products containing fractions are discharged at the bottom. Distillable components of a heavy fraction of coal tar can be separated in a further stripping column and by combining with the head fraction 0 thermal separator summed up for further processing. The residue remaining behind the stripping column can be brought back to the semi-coking drum again for pyrolysis. five A device for gas-phase hydrogenation can be directly attached to the liquid phase hydrogenation device previously described for further processing of non-condensable reaction products, which have been removed in the upper part of the heat separator, without re-heating or pressure reduction. 5 A process gas containing hydrogen and / or fresh hydrogen is used as the hydrogenating gas. The catalyst for the gas phase is, for example, a standard, commercially available purification catalyst. After hydrogenation of the gas phase, the product streams are condensed by intensive heat exchange and separated into a liquid phase and a gas phase in a cold high-pressure separator. The part remaining from the gas is sent back as a circulating gas to a device for liquid-phase hydrogenation. Raffinate is distilled off by distillation. Waste water is discharged through a sluice device, reducing pressure. They are free of polycyclic aromatic hydrocarbons. Under the conditions of hydrogenation under pressure at temperatures between 250 and 500 ° C, usually also thermally relatively stable polycyclic partially chlorinated aromatic hydrocarbons are converted to saturated hydrogeons. Using the method according to. the invention is provided with the possibility of treating the problem / waste and, moreover, regenerating valuable waste. The method of the present invention is explained in more detail by the following examples. Example 1 Oil-deposited sediment from a reservoir refining oil reservoir (bottom sediment), which contains 12% of organic matter, undergoes pyrolysis in a rotating indirectly heated drum at 550 ° C. After 2 hours in the drum, it is obtained the solid residue of pyrolysis, which does not contain organic materials and does not leach with in water, In addition to semi-coking gas (about 1% relative to the load), semi-coking tar is also obtained stve 10 wt% which has the following sulfur contents March 2 yzota mass% - 0.8 mass% of carbon black dust - 12 mass% cheispar proxy component parts - 45 mass% The obtained semi-coking tar with a polychlorinated biphenol (PCB) content of 1000 ppm and a proportion of components of boiling poi more than 350 ° C is 88% hydrogenated at a temperature of 450 ° C, a pressure of 220 bar hydrogen / oil ratio of 2000 l / K and specific productivity 1 kg / lh in the semi-coking phase 1% finely ground semi-coke is added as an additive To neutralize the hydrochloric acid formed, a double stoichiometric amount of alkali is added to the feed product. Organically bound chlorine is converted to table salt and removed together with the additive through a gateway. However, also the amount of splinter to be administered can be injected in the form of water. solution into the downward reaction stream of the semi-coking phase after passing the so-called hot separator, for example, into the supply line of a cold high-pressure separator. About hydrocarbon gases is 4 wt.%, The consumption of hydrogen is 60 l / kg, 55% of the fractional sulfur boiling at a temperature of more than L5C ° C is converted into oil and middle distillate. Total amount g Uid: x0go product has the following contents. riA5 swords 0, ppm (detection limit), sulfur 01 May%, nitrogen - 0 1 May%; g heps, evens - less than 1 ppm (ibngo / ei / h border) Stekhnologi.eska water HUOTS & CSHs liquid g of drainage does not contain PCB goan: / cha oog a, 0 1 pp tO and m I llov (i ranitsa detection 1 ppm) PRI me R 2 Vysushenn.y purified 5 (, gluvodi-ny sludge) with the maintenance of 76% of organic components | eogas s and 1p; lysing in KOSVRI About heating i ikiv EC-ILJ e pg ° 6apa5shc ROI temgera-OLCC From 5a5s14e eieu.ie, solid ores of pyrolysis consisting of unsatisfactory and inorganic and xxo hours of purified sludge and image of the ja-i south according to ukosks and at 2 times the floor / train are obtained for an hour. L 22 las. , about the tar coking which is auger Ophe skarz ezizirovan following of azzo m tough + dust 60 May% aromatic Hsci e yi levodorsdy - 19 may%, aliphatic 21 May% 0 half of the tar gossip with content phenols of 15 mao% and a polycyclichexyl aomatic value of hydrocarbons () 10 to a c% in liquid phooE at a pressure of 280 bar iGi iepaiype 470 ° С 5 hydrogen / oil in 2000 l / kg and specific production of 1 kg / l h is subjected to liquid-phase hydrogenation At the end of the addition, 1% of thin box of motoxopsox (cooper at 0 to the floor of the furnace and the hot separator for the distillate distillates you of the hot section 11 were subjected to further processing in the hydrogenation directly connected to the gas in vcia-iOBxc Phase 5 on the accumulated prints in the trade of the purification catalyst under the pressure of liquid-phase hydrogenation at a temperature of 390 ° C and a reactor reactor output of 0.5 kg / kg / h. The remaining residue is hydrated by -1p in the liquid phase is fed again into the semi-coking drum for re-pyrolysis. The process water after hydrogenation in the gas phase does not contain phenols and polycyclic aromatic hydrocarbons. The overall product is characterized as follows: PAU less than 0.1 May.% Phenols less than 10 ppm More than 10 ppm Nitrogen 10 ppm The pyrolysis oil is subjected to co-liquid-phase gas-phase hydrogenation. Pyrolysis gas is fed directly to the gas phase reactor.
权利要求:
Claims (1) [1] The invention of the method of processing liquid hydrocarbon-containing semi-coking products raw materials obtained at a temperature of 500–550 ° C per hour by liquid phase hydrogenation at a temperature of 450–470 ° C and a hydrogen pressure of 220–280 bar in the presence of a catalyst, characterized in that, in order to increase the efficiency of the process, liquid semi-coking products use semi-coking tar of oil-contaminated bottom sediments, hydrocarbon-containing sludges, semi-coke obtained in the process of semi-coking, taken in an amount of 1 wt.% from the initial liquid products, and The process is carried out at a hydrogen: feedstock ratio of 2000 L / kg and a specific feed rate of 1 kg / L, h.
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同族专利:
公开号 | 公开日 NO890788D0|1989-02-24| DE3872869D1|1992-08-20| AT78286T|1992-08-15| ES2033409T3|1993-03-16| DE3806365C1|1989-07-20| CA1323319C|1993-10-19| GR3005868T3|1993-06-07| US4983782A|1991-01-08| NO890788L|1989-08-28| EP0330757A3|1990-03-07| DD279139A5|1990-05-23| EP0330757A2|1989-09-06| EP0330757B1|1992-07-15| JPH01263192A|1989-10-19|
引用文献:
公开号 | 申请日 | 公开日 | 申请人 | 专利标题 RU2470863C2|2008-01-05|2012-12-27|Био-Энерджи-Холдинг Аг|Method and apparatus for producing middle distillate from hydrocarbon-containing energy sources|BE533923A|1953-12-31| US3090820A|1960-11-21|1963-05-21|Monsanto Chemicals|Recovery of aromatic hydrocarbons| US3503867A|1968-03-04|1970-03-31|Atlantic Richfield Co|Process and system for producing synthetic crude from coal| DE2462495C2|1974-02-01|1982-10-14|Winfried 6234 Hattersheim Schäfer|Process for the production of gas and distillable oil components by heat treatment of automobile tires| US4204943A|1978-03-24|1980-05-27|Exxon Research & Engineering Co.|Combination hydroconversion, coking and gasification| US4266083A|1979-06-08|1981-05-05|The Rust Engineering Company|Biomass liquefaction process| US4303477A|1979-06-25|1981-12-01|Babcock Krauss-Maffei Industrieanlagen Gmbh|Process for the pyrolysis of waste materials| DE2935669C2|1979-09-04|1986-10-30|Herko Pyrolyse Gmbh & Co Recycling Kg, 6832 Hockenheim|Resistance heated crack reactor for waste pyrolysis| US4308411A|1980-08-28|1981-12-29|Occidental Research Corporation|Process for converting oxygenated hydrocarbons into hydrocarbons| DE3221411A1|1982-06-05|1983-12-08|Veba Oel Entwicklungsgesellschaft mbH, 4660 Gelsenkirchen-Buer|METHOD FOR HYDROGENATING HEAVY OIL, BITUMEN AND THE LIKE| DE3317977C2|1983-05-18|1988-10-06|Pka Pyrolyse Kraftanlagen Gmbh, 7080 Aalen, De| US4526675A|1983-05-26|1985-07-02|Standard Oil Company |Hydrocarbon conversion method| DE3412536A1|1984-04-04|1985-10-31|Fried. Krupp Gmbh, 4300 Essen|METHOD FOR PRODUCING HYDROCARBONS FROM CLEANING SLUDGE| DE3412582A1|1984-04-04|1985-10-24|KPA Kiener Pyrolyse Gesellschaft für thermische Abfallverwertung mbH, 7000 Stuttgart|GAS CONVERTER FOR SMOKE GASES FROM A PYROLYSIS OF WASTE| DE3605693A1|1986-02-21|1987-08-27|Kraftwerk Union Ag|WASTE REMOVAL DEVICE FOR PROBLEMS| DE3634275A1|1986-10-08|1988-04-28|Veba Oel Entwicklungs Gmbh|METHOD FOR HYDROGENATING CONVERSION OF HEAVY AND RESIDUAL OILS|DE3939745A1|1989-08-04|1991-02-07|Ruhrkohle Umwelttechnik Gmbh|Pyrolysis gas treatment - by indirectly heating contaminated soil and transferring to coking plant, etc.| US5707592A|1991-07-18|1998-01-13|Someus; Edward|Method and apparatus for treatment of waste materials including nuclear contaminated materials| AT158013T|1991-09-19|1997-09-15|Wolfdieter Klein|METHOD FOR SPLITTING CONTAMINATED PLASTICS.| US5389691A|1993-09-07|1995-02-14|Univ. Of Wyoming|Process for co-recycling tires and oils| DE19941497B4|1999-09-01|2009-01-29|Alphakat Gmbh|Process and apparatus for the production of liquid fuels from re-chargeable substances| US7344622B2|2003-04-08|2008-03-18|Grispin Charles W|Pyrolytic process and apparatus for producing enhanced amounts of aromatic compounds| EP1809721B1|2004-10-13|2012-12-05|Charlie Holding Intellectual Property, Inc.|Pyrolytic process for producing enhanced amounts of aromatic compounds| US7909895B2|2004-11-10|2011-03-22|Enertech Environmental, Inc.|Slurry dewatering and conversion of biosolids to a renewable fuel| EP1894893B1|2005-04-27|2014-09-24|Mitsubishi Kakoki Kaisha, Ltd|Organic waste disposal facility and method of disposal| WO2010118103A1|2009-04-07|2010-10-14|Enertech Environmental, Inc.|Method for converting organic material into a renewable fuel| US8690977B2|2009-06-25|2014-04-08|Sustainable Waste Power Systems, Inc.|Garbage in power outthermal conversion process| IN2012DN03077A|2009-10-14|2015-07-31|Reklaim Inc| US9061953B2|2013-11-19|2015-06-23|Uop Llc|Process for converting polycyclic aromatic compounds to monocyclic aromatic compounds|
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