WO2004090422A1 - Method and apparatus for treating medical materials - Google Patents

Method and apparatus for treating medical materials Download PDF

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Publication number
WO2004090422A1
WO2004090422A1 PCT/CN2003/000826 CN0300826W WO2004090422A1 WO 2004090422 A1 WO2004090422 A1 WO 2004090422A1 CN 0300826 W CN0300826 W CN 0300826W WO 2004090422 A1 WO2004090422 A1 WO 2004090422A1
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shell
gas
thermal cracking
combustion
cracking
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PCT/CN2003/000826
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French (fr)
Chinese (zh)
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Dingli Zhou
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Dingli Zhou
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Priority to AU2003271035A priority Critical patent/AU2003271035A1/en
Publication of WO2004090422A1 publication Critical patent/WO2004090422A1/en

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    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/30Pyrolysing
    • F23G2201/304Burning pyrosolids
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2209/00Specific waste
    • F23G2209/20Medical materials
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00Special features of, or arrangements for incinerators
    • F23G2900/50204Waste pre-treatment by pyrolysis, gasification or cracking
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00Special features of, or arrangements for incinerators
    • F23G2900/70Incinerating particular products or waste
    • F23G2900/7009Incinerating human or animal corpses or remains

Abstract

The present invention discloses a method and apparatus for treating medical materials. Typically, firstly the medical materials are cracked in a sealed furnace in a temperature range of 300-450° C. Hydrocarbon from cracking is recovered. Further, the organic residua produced by cracking process are combusted in a higher range temperature of 850-1300° C into ash. Futhermore the present invention also discloses the treating apparatus including a housing for gathering medical materials, the sealed furnace, a combustion furnace, a jar for storing residua, a collector for hydrocarbon and etc. The present invention makes the medical materials harmless and makes a great deal of medical materials to a kind of resource.

Description

一种处理医疗废弃物的方法和设备 技术领域  Method and equipment for treating medical waste
本发明涉及处理医疗废弃物的方法和设备, 具体地说, 涉及一种采 用裂解和焚烧的方式处理医疗废弃物的方法和设备。 背景技术  The present invention relates to a method and equipment for treating medical waste, and in particular, to a method and equipment for treating medical waste by means of cracking and incineration. Background technique
随着社会的发展和人们健康水平的提高, 医疗废弃物在社会垃圾总 量中的百分比含量不断上升。 因医疗废弃物可能含有具有病菌、 病毒, 因而具有毒性和传染性, 还有恶臭, 它们对人群和环境的危害性远远大 于普通的日常生活垃圾。 有效地处理这些医疗废弃物、 使其无害化、 减 容化, 已成为全球普遍重视和研究的课题。  With the development of society and the improvement of people's health, the percentage of medical waste in the total amount of social waste has continued to rise. Because medical waste may contain germs and viruses, it is toxic and infectious, as well as foul odors. They are far more harmful to people and the environment than ordinary daily garbage. Effectively disposing of these medical wastes, making them harmless, and reducing their volume has become a topic that is widely valued and researched worldwide.
医疗废弃物成份复杂, 主要包含有机高分子聚合物类, 如橡胶手套, 床垫、 塑料输液管、 血浆袋等; 有机纤维类, 如纱布、 绷带、 口罩、 药 用棉花棉球、 衣物等; 碳水化合物类, 如人体内脏器官、 肢体、 发毛、 血液及残余物; 以及固体废弃物类, 如玻璃瓶、 金属针头、 破损的手术 器 、 刀械, 等等。 医疗废弃物必须经过高温处理才能彻底无害化, 达 到环境保护要求。 目前, 分解和销毁医疗废弃物的常见方法就是采用各 式各样的焚烧法,如旋转筒式焚烧法、卧式排炉燃烧法,立式筒体焚烧法, 例如在 USP 6 , 352 , 040中采用二步焚烧法, 等等。 焚烧垃圾后排出的 尾气严重污染大气环境、 每天焚烧的垃圾越多 , 产生的尾气也越多, 对 环境的污染也就越大; 焚烧垃圾需要大量燃料油, 能耗大、 处理成本高; 焚烧中产生大量过剩的高温烟气或热量难以储蓄和综合利用, 特别是医 疗废弃物中含有大量可以转化成高价值燃料油的废塑料、 廈橡胶物品被 烧掉, 造成能量资源的严重浪费; 未被高温处理的原始医疗废弃物带有 易传染的有毒和有害性物质, 必须在密封环境条件下进行无毒化处理和 彻底销毁; 而焚烧法通常是在鼓吹空气的条件下进行的, 一般很难形成 到密闭环境, 导致操作工人和周围环境被有害物质传染。 Medical waste has complex components, mainly including organic high molecular polymers, such as rubber gloves, mattresses, plastic infusion tubes, plasma bags, etc .; organic fibers, such as gauze, bandages, masks, medicinal cotton balls, clothing, etc .; Carbohydrates, such as internal organs, limbs, hair, blood, and residues; and solid waste, such as glass bottles, metal needles, broken surgical instruments, knives, and so on. Medical waste must be treated at high temperature to be completely harmless and meet environmental protection requirements. At present, the common methods of decomposing and destroying medical waste are various incineration methods, such as rotary barrel incineration method, horizontal exhaust furnace combustion method, and vertical barrel incineration method, for example, in USP 6, 352, 040. In the two-step incineration method, etc. The exhaust gas discharged after incineration of garbage seriously pollutes the atmospheric environment. The more waste incinerated every day, the more exhaust gas is generated, and the greater the pollution to the environment; the incineration of garbage requires a large amount of fuel oil, which consumes a large amount of energy and has a high processing cost; A large amount of excess high-temperature flue gas or heat generated during incineration is difficult to save and comprehensively use, especially medical waste containing a large amount of waste plastic and rubber articles that can be converted into high-value fuel oil is burned, causing serious waste of energy resources; The raw medical waste that has not been processed at high temperature carries infectious toxic and harmful substances, and must be detoxified and completely destroyed in a sealed environment. The incineration method is usually carried out under the condition of air blowing. It is difficult to form a confined environment, causing the operator and the surrounding environment to be infected by harmful substances.
综上所述,将医疗废弃物进行一次性焚烧处理的方法存在着大量的 尾气污染环境、 能耗和处理成本高, 过剩的热能难以储蓄利用以及无法 进行医疗废弃物的资源化等严重的弊病。 '  In summary, the method of one-time incineration of medical waste has serious ills such as polluting the environment with a large amount of exhaust gas, high energy consumption and treatment costs, difficulty in saving and utilizing excess thermal energy, and inability to recycle medical waste. . '
现有技术已公开了一些取代和改进上述焚烧法的新技术方案, 例如 采用热裂解方法。 在 USP 6, 139 , 793中, 医疗废弃物在带有搅拌装置 的密闭容器中进行间歇式无害化处理; 但由于搅拌轴长时间在高温条件 下旋转易变形和弯曲, 转轴与容器之间的密封系统易被破坏, 致使容器 内的高温气体易向外泄露, 故只能采用较低温度来处理医疗废弃物, 但 其中使用的 121- 171 °C低温范围只能起到杀菌消毒作用, 根本不能将有 机废弃物彻底分解和裂解;  The prior art has disclosed some new technical solutions to replace and improve the above-mentioned incineration method, such as using a thermal cracking method. In USP 6, 139, 793, medical waste is intermittently harmlessly treated in a closed container with a stirring device; however, because the stirring shaft is easily deformed and bent when it is rotated under high temperature for a long time, between the shaft and the container The sealing system is easy to be damaged, so that the high-temperature gas in the container is easy to leak to the outside. Therefore, the lower temperature can only be used to treat medical waste, but the low temperature range of 121-171 ° C used in it can only sterilize and disinfect. The organic waste cannot be completely decomposed and cracked at all;
USP 6 , 524 , 539中公开了用电磁微波作为热源、 在无氧的密闭容 器中将医疗废弃物进行传统的间歇式干馏方法, 使排放的尾气中不含二 恶英等有毒物质; 由于是间歇式操作, 加料和排灰清渣必须在常压常温 条件下进行, 以致每次装料后需要很长时间去升温, 卸渣排灰前需要很 长时间去降温, 升温和降温二个过程消耗了大量的时间, 导致设备的单 位处理量降低; 大量的热能在升温和降温过程中损失掉, 必须额外增加 和补充大量的电耗; 废弃物中本身含的有机物不能被燃烧利用, 处理成 本高; 另外, 废弃物中的金属物质对电磁微波有反射作用, 导致电磁微 波设备受到坏的影响, 不能正常运行。 USP 6, 524, 539 discloses the use of electromagnetic microwaves as a heat source and traditional batch retorting methods of medical waste in oxygen-free closed containers, so that the exhaust gas does not contain toxic substances such as dioxins; because Intermittent operation, feeding and ash removal and slag removal must be carried out at normal pressure and temperature, so that it takes a long time to heat up after each loading, and it takes a long time to cool down before slag discharge and ash discharge. A large amount of time is consumed, resulting in a reduction in the unit processing capacity of the equipment; a large amount of heat energy is lost during the heating and cooling processes, which must be additionally increased And replenish a large amount of electricity consumption; the organic substances contained in the waste cannot be burned and used, and the treatment cost is high; in addition, the metal substances in the waste have a reflection effect on the electromagnetic microwave, causing the electromagnetic microwave equipment to be adversely affected and unable to operate normally .
特别是, 医疗废弃物中含有大量的碳水化合物, 如人体的内脏等等, 必须要在 850°C以上的高温下处理才能使其彻底分解和无害化。 当今, 市场上或工业上常用的耐高温钢即不锈钢或钛合金钢也很难长时间耐受 850°C以上的高温条件, 且价格昂贵; 所以, 在实际工业化处理医疗废弃 物的过程中, 裂解设备的材质的使用温度一般在 500-700 °C。 裂解设备 材质的耐温能力限制了裂解设备内的医疗废弃物的热裂解温度难以达到 850°C , 也就是说, 在 500-700°C的温度条件所发生的热裂解不能使医疗 废弃物完全彻底地分解, 裂解后的残渣中还含有相当多未被分解的有机 物质, 还必须进一步处理使其彻底分解或无害化, 才能符合环境保护的 要求。  In particular, medical waste contains a large amount of carbohydrates, such as the internal organs of the human body, and must be treated at a high temperature of 850 ° C or higher to completely decompose and harmless it. Today, high temperature resistant steels commonly used in the market or industry, such as stainless steel or titanium alloy steel, are difficult to withstand high temperature conditions above 850 ° C for a long time and are expensive; therefore, in the actual industrialized process of medical waste treatment, The operating temperature of the material of the cracking equipment is generally 500-700 ° C. The temperature resistance of the material of the cracking equipment limits the thermal cracking temperature of the medical waste in the cracking equipment, which is difficult to reach 850 ° C, that is, the thermal cracking that occurs at a temperature of 500-700 ° C cannot make the medical waste completely It is completely decomposed. The residue after cracking also contains quite a lot of undecomposed organic substances, which must be further processed to completely decompose or harmless to meet the requirements of environmental protection.
综上所述, 单纯采用焚烧法和传统的热解法处理医疗廈弃物 ,.. 已经 不能满足高效、 环保、 节能等多方面的要求。  To sum up, simply adopting the incineration method and the traditional pyrolysis method to treat medical building wastes can no longer meet the requirements of high efficiency, environmental protection and energy saving.
本发明的目的就是要克服上述焚烧法和热解法处理医疗废弃物的缺 点, 提供一种先低温裂解后高温焚烧、 能满足高效、 环保、 节能等多方 面要求的处理医疗廈弃物的方法和设备。 发明内容  The purpose of the present invention is to overcome the shortcomings of the above-mentioned incineration method and pyrolysis method for treating medical waste, and provide a method for treating medical waste, which can meet the requirements of high efficiency, environmental protection, energy saving and other aspects, such as low-temperature cracking and high-temperature incineration. And equipment. Summary of the Invention
按本发明的一个方面, 提供了一种处理医疗废弃物的方法, 更具体 地说, 本发明涉及一种先将医疗废弃物进行有限热裂解、 然后将裂解反 应产生的残渣进行高温焚烧的方法。 According to one aspect of the present invention, a method for treating medical waste is provided, and more particularly, the present invention relates to a method for firstly performing limited thermal cracking of medical waste, and then The method of high temperature incineration of the generated residue.
按本发明的另一方面, 提供了一种处理医疗废弃物的设备, 它主要 包括将医疗废弃物进行有限热裂解的装置和将裂解反应产生的残渣进行 高温焚烧的装置。  According to another aspect of the present invention, a device for treating medical waste is provided, which mainly includes a device for performing limited thermal cracking of medical waste and a device for incineration of residues generated by the cracking reaction.
按本发明的方法包括以下步骤:  The method according to the invention comprises the following steps:
i ) 将所述的医疗废弃物装入裂解设备内并密闭该设备; ii ) 加热该裂解设备, 使物料在 300-450°C保持 0. 2-4小时, 进 行热裂解反应, 收集并利用热裂解反应的气相产物; iii ) 将裂解反应残渣排出裂解设备, 送到燃烧炉中焚烧至烬; iv ) 从燃烧炉中排出并处置焚烧后的灰渣。  i) loading the medical waste into a cracking device and sealing the device; ii) heating the cracking device to keep the material at 300-450 ° C for 0. 2-4 hours, performing a thermal cracking reaction, collecting and using The gas phase product of the thermal cracking reaction; iii) The cracking reaction residue is discharged from the cracking equipment and sent to a burner for incineration to embers; iv) the burned ash is discharged and disposed of.
所说的医疗废弃物包含一种或多种下列废弃的物质: 有机聚合物、 有机纤维物质、 碳水化合物、 人体组织器官或其它有机残余物、 无机 - 及金属材料、 器械等。  The medical waste includes one or more of the following waste substances: organic polymers, organic fiber substances, carbohydrates, human tissues or other organic residues, inorganic-and metallic materials, equipment, etc.
在装料前, 所述的医疗废弃物经过粉碎或不粉碎, 要求废弃物的尺 寸不大于 35厘米。在装料过程中应尽量避免裂解设备中存留的裂解反应 气体产物不外泄。  Before loading, the medical waste is pulverized or not, and the size of the waste is required to be no more than 35 cm. During the charging process, the cracking reaction gas products remaining in the cracking equipment should be avoided as far as possible.
热裂解反应和焚烧所需的热源可以由燃油、 燃气、 煤、 电能或 /和裂 解反应残渣的燃烧来提供, 所说的燃油和燃气可以是从热裂解反应产生 的气体产物中获得的。  The heat source required for the pyrolysis reaction and incineration can be provided by the combustion of fuel oil, gas, coal, electricity or / and the residue of the cracking reaction, said fuel oil and gas can be obtained from the gas products produced by the thermal cracking reaction.
所述'的热裂解残渣在燃烧炉内在 850-1300°C下经焚烧, 使其中的可 燃物燃烧干净, 也使其它物质彻底无害化; 裂解和焚烧操作的压力各为 常压或稍微加压。 将裂解反应残渣排出裂解设备的步骤可分两步进行, 即先将残渣排 放到一个残渣收集容器中、 待积累到一定量时才一并送到燃烧炉中; 将 排出的残渣送到燃烧炉中的步驟可采用常用的方式进行, 例如采用链条 传送, 或在处理量不很大时用人力传送。 The thermal cracking residue is burned in a combustion furnace at 850-1300 ° C, so that the combustibles in it are burned cleanly, and other materials are completely harmless; the pressures of the cracking and incineration operations are normal pressure or slightly increased. Pressure. The step of discharging the cracking reaction residues into the cracking equipment can be performed in two steps. That is, the residues are first discharged into a residue collection container, and they are sent to the combustion furnace when they have accumulated to a certain amount. The steps in the process can be performed in common ways, such as chain transfer, or manual transfer when the processing capacity is not large.
经过焚烧后的灰渣排出燃烧炉, 冷却后经分筛, 将未被灰化的固体 物质如固体无机物和金属与灰分分开, 分别做进一步的处理。  The incinerated ash is discharged out of the combustion furnace. After cooling, it is sieved to separate unashed solid materials, such as solid inorganic matter and metals, from the ash for further processing.
按本发明的方法的一个优选的实施方案 , 将所述的热裂解反应分两 步进行,第一步为将医疗废弃物在裂解设备包含的一个储料 /气化单元中 升温至不超过 250°C, 维持 0. 2-2小时, 其间产生的气体产物送到燃烧 炉中燃烧并回收热量, 第二步再将剩余物 1入裂解设备包含的一个热裂 解单元中, 使其在 300- 450°C保持 0. 2-4小时, 以完成热裂解反应。  According to a preferred embodiment of the method of the present invention, the thermal cracking reaction is performed in two steps. The first step is to raise the temperature of the medical waste to not more than 250 in a storage / gasification unit included in the cracking equipment. ° C, maintaining for 0.2-2 hours, the gas products produced in the meantime are sent to a combustion furnace for combustion and heat recovery, the second step is to put the remainder 1 into a thermal cracking unit included in the cracking equipment, so that it is at 300- Hold at 450 ° C for 0. 2-4 hours to complete the thermal cracking reaction.
按本发明的方法的又一个优选的实施方案, 使裂解反应所生产的气 相产物经冷凝处理, 并收集冷凝下来的液相烃油, 将未凝结的气体引入 燃烧炉进行燃烧, 并利用燃烧放热来为热裂解反应过程供热。  According to another preferred embodiment of the method of the present invention, the gas-phase product produced by the cracking reaction is subjected to condensation treatment, and the condensed liquid hydrocarbon oil is collected, and the uncondensed gas is introduced into a combustion furnace for combustion, and the combustion gas is used for combustion. Heat is used to provide heat for the thermal cracking reaction process.
按本发明处理医疗废弃物的设备包括储料仓、 热裂解设备、 燃烧炉、 储渣罐、 余热锅炉和烃油收集装置;  The equipment for treating medical waste according to the present invention includes a storage silo, a thermal cracking equipment, a combustion furnace, a slag storage tank, a waste heat boiler and a hydrocarbon oil collection device;
所述的储料仓包括: 可为圆柱形或矩形的壳体, 壳体的外层是加热 用的烟道气通道层, 壳体的上部装有加料开孔, 并配备密封盖或阀门; 壳体的下部装有通向热裂解设备的卸料口 , 并配备阀门; 壳体上部装有 蒸汽进口和气体排放出口;  The storage bin includes: a cylindrical or rectangular shell, an outer layer of the shell is a flue gas channel layer for heating, an upper part of the shell is provided with a feeding opening, and is equipped with a sealing cover or a valve; The lower part of the shell is equipped with a discharge port leading to the thermal cracking equipment, and is equipped with a valve; the upper part of the shell is equipped with a steam inlet and a gas exhaust outlet;
所述的热裂解设备位于储料仓的下方, 包括: 可为圆柱形或矩形的 上部壳体、 与上部壳体形状匹配但逐渐收口的圆锥形或弧顶向上的圆形 封头状下部壳体, 上部和下部壳体紧密结合; 壳体的外层是加热用的烟 道气通道层; 壳体的上部有加料开孔, 开孔上配备阀门, 此阔门与储料 仓的卸料口相连接; 壳体下部或下部侧面安装有排渣口, 并配备阀门, 此阀门与储渣罐的残渣入口相连接;壳体上部装有通向烃油收集装置和 / 或燃烧炉的气相物排放口; The thermal cracking equipment is located below the storage silo and includes: a cylindrical or rectangular upper casing, a conical shape or a circular arc top upwardly matching the shape of the upper casing but gradually closing. The head-shaped lower casing is closely combined with the upper and lower casings; the outer layer of the casing is a flue gas channel layer for heating; the upper part of the casing has a feeding opening, and a valve is arranged on the opening. The discharge port of the silo is connected; a slag discharge port is installed at the lower or lower side of the casing and is equipped with a valve, which is connected to the residue inlet of the slag storage tank; the upper part of the casing is provided with a hydrocarbon oil collection device and / Or the gaseous matter discharge port of the combustion furnace;
所述的储渣罐包括: 圆柱形或矩形壳体, 壳体的上部有残渣进入开 口, 壳体下部有排渣口, 并配备排渣阀门; 壳体上部装有尾气出口; 所述的燃烧炉包括:供燃烧和焚烧的圆柱形或矩形壳体、 壳壁上有与 储料仓相连的气化物入口、 与烃油收集装置相连的未冷凝气化物入口、 液体烃油燃烧喷嘴、 燃烧获得的高温烟气出口、 来自储渣罐的残渣焚烧 入口以及壳内供固体物质焚烧用的炉排。  The slag storage tank includes: a cylindrical or rectangular shell, the upper part of the shell has a residue entry opening, the lower part of the shell has a slag discharge port, and is equipped with a slag discharge valve; the upper part of the shell is equipped with an exhaust gas outlet; the combustion The furnace includes: a cylindrical or rectangular shell for combustion and incineration, a gas inlet connected to a storage bin on the shell wall, an uncondensed gas inlet connected to a hydrocarbon oil collection device, a liquid hydrocarbon oil combustion nozzle, and combustion obtained High temperature flue gas outlet, residue incineration inlet from slag storage tank, and grate in the shell for solid matter incineration.
所述的烃油收集装置包括: 冷凝装置和气液分离装置,冷凝装置可以 接受来自于裂解设备的气化产物, 使其冷凝后分离为气液两种产物, 储 存于气液分离器或烃油储罐中, 可用室温空气或室温水给冷凝装置降温 换热, 换热后的热空气进入燃烧炉; 气液分离装置或烃油储罐收集来自 于冷凝装置的气液产物, 并有出口与燃烧炉相连。  The hydrocarbon oil collection device includes: a condensing device and a gas-liquid separation device. The condensing device can receive the gasification products from the cracking equipment, and after condensing, it can be separated into two products of gas and liquid, which are stored in the gas-liquid separator or the hydrocarbon oil In the storage tank, room temperature air or room temperature water can be used to cool and cool the condensing device, and the hot air after heat exchange enters the combustion furnace; the gas-liquid separation device or hydrocarbon oil storage tank collects gas-liquid products from the condensing device, and has an outlet and The burner is connected.
按本发明的设备的一个优选实施方案,  A preferred embodiment of the device according to the invention,
按本发明的设备的另一个优选实施方案, 所述的裂解设备可以是旋 转式反应器, 或是圆柱形壳体, 壳体的底部可以是弧顶向上的圆形封头, 排渣孔配置在壳体下部的侧面上, 或矩形壳体反应器; 壳体内可以安装 搅拌器。 在另一个优选实施方案中, 裂解设备壳体内部装有加热烟道管, 烟道管与壳体外层的烟道通道相连通。 附图的简要说明 According to another preferred embodiment of the device of the present invention, the cracking device may be a rotary reactor or a cylindrical shell, and the bottom of the shell may be a circular head with an arc top upward, and a slag hole configuration On the side of the lower part of the shell, or a rectangular shell reactor; a stirrer can be installed in the shell. In another preferred embodiment, a heating flue pipe is installed inside the shell of the cracking device, and the flue pipe is in communication with a flue channel on the outer layer of the shell. Brief description of the drawings
图 1 是用本发明方法和设备的筒易流程图;  Figure 1 is a simple flowchart of the method and equipment of the present invention;
图 2 是本发明中可采用的热裂解釜、 储料仓和储渣罐设备的配置 示意图。 具体的实施方案  FIG. 2 is a schematic configuration diagram of a thermal cracking kettle, a storage bin, and a slag storage tank device that can be used in the present invention. Specific implementation scheme
下面结合本发明的设备来描述本发明的方法。  The method of the invention is described below in conjunction with the device of the invention.
将医疗废弃物不粉碎和或粉碎成其尺寸在 35厘米以下。  The medical waste is not crushed or crushed to a size of less than 35 cm.
在将医疗废弃物加入储料仓之前, 先打开储料仓上的水蒸汽进口和 尾气出口, 将余热锅炉产生的水蒸汽通入密封的储料仓中, 用水蒸汽或 抽风机将储料仓内留存的烃类气体驱赶出去, 并输送到燃烧炉去燃烧; 然后再敞开储料仓, 给储料仓加料; 加料完毕, 将储料仓加盖密闭, 用 水蒸汽或抽风机把储料仓内的空气驱赶出去。  Before adding medical waste to the storage silo, first open the water vapor inlet and exhaust gas outlet on the storage silo, pass the water vapor generated by the waste heat boiler into the sealed storage silo, and use water vapor or an exhaust fan to connect the storage silo The remaining hydrocarbon gas is driven out and sent to the combustion furnace for combustion; then the storage bin is opened to feed the storage bin; after the filling is completed, the storage bin is covered and sealed, and the storage bin is closed with water vapor or a fan The air inside expelled.
在储料仓内不含空气的条件下, 打开储料仓和热裂解釜之间的连接 阀门, 医疗废弃物下落到热裂解釜内, 这避免了储料仓在装料时进入的 空气带进到热裂解釜, 以防止热裂解釜中因有空气而产生爆鸣气发生爆 炸; 然后, 关闭储料仓和热裂解釜之间的连接阀门; 重复上述操作方法, 能连续地给储料仓进行装料和卸料。  Under the condition that the storage silo does not contain air, open the connection valve between the storage silo and the thermal cracking kettle, and the medical waste falls into the thermal cracking kettle, which avoids the air zone that the storage silo enters during loading. Enter the thermal cracking kettle to prevent the explosion of detonation gas due to air in the thermal cracking kettle; then, close the connection valve between the storage silo and the thermal cracking kettle; repeat the above operation method to continuously feed the material The silo is loaded and unloaded.
用高温烟气给热裂解釜内的医疗废弃物加热 , 并使物料在 300-450 °C下维持 0. 2-4小时, 发生热裂解反应; 热裂解反应维持常压或高于常 压; 反应产生气相物和残渣, 将残渣排出热裂解釜, 将其送入燃烧炉进 行 850-1300°C的高温燃烧处理至烬, 达到无害化和减容化; 气相物不断 地被排出热裂解釜, 经冷凝器冷凝, 收集得到烃油, 不凝结气相物被引 入到燃烧炉进行燃烧, 将燃烧炉内产生的高温烟气返回到热裂解釜, 给 热裂解釜加热; 当燃烧炉内可燃性气体的供应量不足以产生足够的高温 烟气时, 用油泵将收集得到的烃油输入到燃烧炉进行燃烧; 热裂解反应 产生的残渣排入到储渣罐时, 储渣罐内的压力可以是常压, 也可以是负 压, 负压可以是用水蒸汽射流或用真空泵抽气产生。 Heat the medical waste in the pyrolysis kettle with high temperature flue gas, and keep the material at 300-450 ° C for 0. 2-4 hours, a thermal cracking reaction occurs; the thermal cracking reaction maintains normal pressure or higher than normal pressure; The gas phase and residue are produced by the reaction. The residue is discharged from the pyrolysis kettle and sent to the combustion furnace. 850-1300 ° C high-temperature combustion treatment to embers, to achieve harmlessness and volume reduction; gaseous materials are continuously discharged from the thermal cracker, condensed by condensers, collected to obtain hydrocarbon oil, non-condensable gaseous materials are introduced into the combustion The furnace performs combustion, returns the high temperature flue gas generated in the combustion furnace to the thermal cracking kettle, and heats the thermal cracking kettle; when the supply amount of combustible gas in the combustion furnace is insufficient to generate sufficient high temperature flue gas, it is collected by an oil pump The hydrocarbon oil is input to the combustion furnace for combustion; when the residue produced by the pyrolysis reaction is discharged into the slag storage tank, the pressure in the slag storage tank may be normal pressure or negative pressure, and the negative pressure may be a water vapor jet or a Vacuum pumping is generated.
排渣时, 打开热裂解釜的排渣口与储渣罐进料口相连接的阀门, 热 裂解釜中的残渣受储渣罐内的负压吸引和 /或向下重力作用,往下落入到 储渣罐内; 关闭热裂解釜与储渣罐相连接的阀门, 再打开储渣罐的排渣 阀门, 将残渣排出储渣罐, 然后, 关闭储渣罐的排渣阀门; 重复上述排 渣操作方法, 可方便地将热裂解釜中的残渣排出装置, 并将含有有机物 的反应残渣送入燃烧炉去焚烧, 进一步进行无害化、 减容化处理。  During the slag discharge, the valve connecting the slag discharge port of the thermal cracking kettle and the feed opening of the slag storage tank is opened. Into the slag storage tank; close the valve connecting the pyrolysis kettle and the slag storage tank, then open the slag discharge valve of the slag storage tank to discharge the residue out of the slag storage tank, and then close the slag discharge valve of the slag storage tank; repeat the above discharge The slag operation method can conveniently discharge the residues in the thermal cracking kettle and send the reaction residues containing organic matter to the combustion furnace for incineration, and further perform harmless and volume reduction treatment.
较优选的做法是, 将从热裂解釜外壳层排出的加热烟气引入储料仓 外壳层的加热烟气通道, 使医疗废弃物升温至不超过 250°C , 维持 0. 2-2 小时, 以便干燥、 预热物料并使易于挥发的有机组分预先挥发; 将气体 产物直接送到燃烧炉里去燃烧, 提供热能; 再将剩余物引入裂解釜中, 使其在 300- 450°C保持 0. 2—4小时, 以完成热裂解反应。  A more preferred approach is to introduce the heated flue gas discharged from the shell layer of the thermal cracking kettle into the heated flue gas passage of the shell layer of the storage bin, so that the medical waste is heated to not more than 250 ° C, and maintained for 0.2-2 hours, In order to dry, pre-heat the material and pre-volatile organic components that are easy to volatilize; send the gas product directly to the combustion furnace to burn to provide thermal energy; and then introduce the residue into the cracker to keep it at 300-450 ° C 0.2 to 4 hours to complete the thermal cracking reaction.
在上述方法步骤中, 所述的热裂解反应所需热量由热裂解反应产生 的烃类 (烃油和 /或低分子量可燃性气体, 如 H2、 CH4、 C2 ) 以及 裂解残渣中的有机物质经燃烧炉燃烧后产生的高温烟气供给; 热裂解温 度为 300— 450°C , 压力为常压或高于常压, 燃烧炉内的温度为 850-1300 。c ; 在通常的医疗废弃物中, 废塑料、 废橡胶和废纤维等有机高分子废 弃物品的重量百分比例比较高,但是,它们容易在很短时间内在 300-450In the above method step, the heat required for the thermal cracking reaction is generated from the hydrocarbons (hydrocarbon oil and / or low molecular weight flammable gas, such as H 2 , CH 4 , C 2 ) and the cracking residues generated from the thermal cracking reaction. The supply of high-temperature flue gas generated by the combustion of organic substances in a combustion furnace; the thermal cracking temperature is 300-450 ° C, the pressure is normal pressure or higher, and the temperature in the combustion furnace is 850-1300 . c; In general medical waste, the weight percentages of organic polymer waste products such as waste plastic, waste rubber, and waste fiber are relatively high, but they are easily within 300-450 in a short period of time.
IM氐温度范围内完全彻底地热裂解和分解, 只需要少量的热量; 同时, 热裂解反应后产生大量能燃烧的烃类物质(烃油和可燃性气体 ); 裂解反 应产生的这些烃类物质如果全部燃烧, 则燃烧后产生的总热量远远大于 热裂解反应所吸收的总热量, 热量或能量有剩余, 应该回收储备这部分 剩余的热量作为备用, 否则, 这部分多余的热量将被浪费和损失; 而碳 水化合物或纤维类废弃物 (如人的内脏器官、 血浆、 肢体、 皮肉等等) 的重量百分比含量虽然比较小, 但它们的物质组成中含有大量的氢键The IM 氐 temperature range is completely and completely thermally cracked and decomposed, requiring only a small amount of heat; at the same time, a large amount of combustible hydrocarbons (hydrocarbon oil and flammable gas) are generated after the thermal cracking reaction; if these hydrocarbons produced by the cracking reaction are If all combustion is performed, the total heat generated after combustion is far greater than the total heat absorbed by the thermal cracking reaction. There is a surplus of heat or energy. This surplus heat should be recovered and stored as a backup. Otherwise, this excess heat will be wasted and Loss; while the weight percentage content of carbohydrate or fiber waste (such as human internal organs, plasma, limbs, flesh, etc.) is relatively small, but their material composition contains a large number of hydrogen bonds
( Η ··· 0 )和大量的水分, 热裂解和分解它们需要大量的热量, 但它们反 应后产生的烃类物质 (烃油和可燃性气体) 的量^少, 这些烃类物质燃 烧后产生的热量远远小于或不能满足热裂解反应所吸收的热量, 热量亏 损; 由于许多碳水化合物废弃物需要在较高的高温条件下, 经过一个比 较长的时间才能慢慢地彻底地裂解和分解, 所以, 必须额外补充新的热 源(如燃料油、 燃料气 ), 并将其引入到燃烧炉进行燃烧, 产生高 温烟气, 以维持热裂解反应的正常进行, 这将会增加医疗废弃物处理的 运行成本; (Η ··· 0) and a large amount of water, thermal cracking and decomposing them require a lot of heat, but the amount of hydrocarbons (hydrocarbon oil and flammable gas) generated after their reaction is small, and after burning these hydrocarbons The heat generated is far less than or cannot meet the heat absorbed by the thermal cracking reaction, and the heat is lost; because many carbohydrate wastes need to be under high temperature conditions, it takes a relatively long time to slowly and completely crack and decompose. Therefore, a new heat source (such as fuel oil and fuel gas) must be supplemented and introduced into a combustion furnace for combustion to generate high-temperature flue gas to maintain the normal progress of the thermal cracking reaction, which will increase the treatment of medical waste. Operating costs
为了避免多余热量的浪费, 降低生产中的热消耗和能源成本, 平衡 热裂解反应全过程中的总热量, 本发明将热裂解反应在 300-450°C温度 范围收回到的多余的热能 一一 烃油,在必要时输入到燃烧炉进行燃烧, 以补充和维持热裂解反应所需的热量, 这样不需要额外购买燃料油, 降 低了运行成本, 作到了医疗垃圾处理的资源化; 如果医疗废弃物中可燃 烧的废物量很少时, 发热量也就小, 应额外补充燃料到燃烧炉, 此种情 况可以不冷凝裂解反应排出的气相烃, 即, 不收集烃油, 而是将气相烃 直接引入到燃烧炉进行燃烧, 以便获得足够量的高温烟道气和热量供裂 解反应所用; 由于 300- 450 °C的裂解温度不能将医疗废弃物彻底分解和 无害化, 须进一步将热裂解后剩余的有机残渣输送到燃烧炉, 经过 850- 130 (TC高温焚烧处理至烬 , 将燃烧后产生的高温烟气返回到热裂解 反应釜, 给反应釜供热, 热裂解反应所需的热源可以是燃油、 燃气、 煤、 电能或 /和裂解反应残渣, 裂解反应残渣如果全部变成无机物 , 则裂解反 应残渣也可以不再返到燃烧炉中焚烧处理; In order to avoid waste of excess heat, reduce heat consumption and energy cost in production, and balance the total heat in the whole process of thermal cracking reaction, the present invention recovers the excess thermal energy of the thermal cracking reaction in the temperature range of 300-450 ° C one by one. Hydrocarbon oil is input to the combustion furnace for combustion when necessary to supplement and maintain the heat required for the thermal cracking reaction. This eliminates the need to purchase additional fuel oil, reduces operating costs, and recycles medical waste. If medical waste is discarded, Flammable When the amount of waste burned is small, the calorific value is small, and additional fuel should be added to the combustion furnace. In this case, the gas phase hydrocarbons discharged from the cracking reaction may not be condensed, that is, the hydrocarbon oil is not collected, but the gas phase hydrocarbons are directly introduced into the The combustion furnace burns in order to obtain a sufficient amount of high-temperature flue gas and heat for the cracking reaction. Since the cracking temperature of 300-450 ° C cannot completely decompose and harmless medical waste, the remaining residual after thermal cracking must be further The organic residues are sent to the combustion furnace, and after 850-130 (TC high-temperature incineration treatment to embers, the high-temperature flue gas generated after combustion is returned to the thermal cracking reactor to heat the reactor. The heat source required for the thermal cracking reaction can be fuel oil , Gas, coal, electricity, and / or cracking reaction residues, if the cracking reaction residues all become inorganic, the cracking reaction residues may no longer be returned to the combustion furnace for incineration;
可用本发明方法处理的废弃物包括: 各类医疗废弃物、有机物废品、 废塑料、 废橡胶、 废纤维素制品、 碳水化合物、 渣油、 重油、 污油、 人 蓄粪便、 污泥、 木屑、 含油砂子以及其它高分子有机废弃物。  Wastes that can be treated by the method of the present invention include: various medical wastes, organic waste products, waste plastics, waste rubber, waste cellulose products, carbohydrates, residues, heavy oil, slop oil, human waste, sludge, wood chips, Oily sand and other high-molecular organic waste.
下面结合附图来说明本发明。  The invention is described below with reference to the drawings.
参见图 1, 本发明的设备包括; 储料仓(6)、 热裂解反应釜或裂解 设备 (13)、 储渣罐 ( 15 )、 燃烧炉 ( 27 )、 余热锅炉 ( 12 )、 冷凝器 ( 20 )、 烃油储罐或汽液分离器 (21)、 油泵(22)和鼓风机(23)等装置。  Referring to FIG. 1, the equipment of the present invention includes: a storage silo (6), a thermal cracking reactor or cracking equipment (13), a slag storage tank (15), a combustion furnace (27), a waste heat boiler (12), and a condenser ( 20), a hydrocarbon oil storage tank or a vapor-liquid separator (21), an oil pump (22), and a blower (23).
所述的储料仓(6) 包括: 圆柱形或矩形壳体(32), 壳体(32) 的 外层是加热烟道层( 5 ), 壳体( 32 )的上部装有加料开孔( 2 ), 开孔( 2 ) 配备密封盖或阀门 (1); 壳体(32) 的下部装有卸料口, 卸料口上装有 阀门 ( 7 ), 此阀门 (7)与壳体(32)下部的热裂解釜 (13)相连接; 壳 体 ( 32 ) 的上部装有蒸汽进口 ( 4 )和废气排放出口 (3);  The storage bin (6) includes: a cylindrical or rectangular shell (32), an outer layer of the shell (32) is a heating flue layer (5), and an upper part of the shell (32) is provided with a feeding opening. (2), the opening (2) is equipped with a sealing cover or a valve (1); the lower part of the housing (32) is equipped with a discharge port, and the valve (7) is installed on the discharge port, and the valve (7) and the housing ( 32) The lower thermal cracking kettle (13) is connected; the upper part of the casing (32) is equipped with a steam inlet (4) and an exhaust gas outlet (3);
所述的热裂解釜(13) 包括: 上部是圆柱形或矩形壳体(33), 下部 是圆锥形或梯形壳体( 34 ), 上部壳体( 33 )和下部壳体( 34 )相焊接; 壳体(33、 34) 的外层是加热烟道层 (30), 壳体(33、 34) 内部装有按 垂直方向或水平方向排列的加热烟道管 (9), 烟道管 (9)与壳体(33、 34 )外层的烟道 ( 30 )相连通; 壳体 ( 33 )的上部有加料开孔 (35), 开 孔( 35 )上配备阀门 ( 7 ), 此阀门 (7)与储料仓 ( 6 )的卸料口相连接; 壳体( 34 ) 下部有排渣口 ( 37), 并配备阀门 (14), 此阀门 (14) 与储 渣罐 ( 15 ) 的残渣进口 ( 35 )相接; 壳体(33)上部装有烃类气相物排 放口 (8); The thermal cracking kettle (13) includes: the upper part is a cylindrical or rectangular shell (33), and the lower part Is a conical or trapezoidal shell (34), the upper shell (33) and the lower shell (34) are welded; the outer layer of the shell (33, 34) is a heating flue layer (30), the shell (33) 34) The inside is equipped with a heating flue pipe (9) arranged in a vertical or horizontal direction, and the flue pipe (9) is in communication with the flue (30) on the outer layer of the casing (33, 34); the casing ( 33) is provided with a feeding opening (35) on the upper part, and a valve (7) is provided on the opening (35), and this valve (7) is connected with the discharge opening of the storage bin (6); the lower part of the housing (34) has The slag discharge port (37) is equipped with a valve (14). This valve (14) is connected to the slag inlet (35) of the slag storage tank (15); the upper part of the casing (33) is provided with a hydrocarbon gaseous gas discharge port ( 8);
所述的储渣罐 ( 15 ) 包括: 圆柱形或矩形壳体( 36 ), 壳体( 36 )的 上部有残渣进口 ( 35 ), 此进口 ( 35 )通过阀门 ( I4 )与壳体( 36 )上方 的热裂解釜(13)相接, 壳体(36)下部有排渣孔,并配备排渣阀门(16); 壳体( 36 )上部装有尾气出口 ( 18 ); The storage slag pot (15) comprising: a cylindrical or rectangular housing (36), the upper housing (36) has a residue inlet (35), this inlet (35) through the valve (I 4) and the housing (36) The upper thermal cracking kettle (13) is connected, the lower part of the shell (36) has a slag discharge hole, and is equipped with a slag discharge valve (16); the upper part of the shell (36) is equipped with an exhaust gas outlet (18);
结合附图 1和 1对本发明的方法进行进一步的说明。  The method of the present invention is further described with reference to FIGS. 1 and 1.
将医疗廈弃物不粉碎和或粉碎成其尺寸在 35厘米以下,通过储料仓 ( 6 )的加料口 ( 2 )进入到储料仓 (6) 中; 加料前, 先打开储料仓 ( 6 ) 上的水蒸汽进口 (4)的阀门 (41)和尾气出口 (3)的阀门 (40), 将水 蒸汽( 17 )通入密封的储料仓( 6 ) 中, 用水蒸汽( 17 )将储料仓( 6 ) 内的高温烃类气体经尾气出口 ( 3 )驱赶出储料仓 ( 6 ), 并将烃类气体输 送到燃烧炉 (27), 通过喷嘴(26)去燃烧; 然后, 关闭蒸汽阀门 (41) 和尾气出口阀门( 40 );打开或敞开储料仓( 6 )的加料口盖子或阀门( 1 ), 将医疗废弃物装入储料仓( 6 ) 中, 关闭或密封加料口 (2); 用盖子或阀 门 (1) 密封加料口 (2); 将水蒸汽(17)通入储料仓(6) 内, 把储料 仓( 6 ) 内的空气经储料仓 ( 6 )的尾气出口 (3)驱赶出储料仓 (6), 或 是将热裂解釜 ( 13 )排出的余热烟气引入储料仓 ( 6 )外层的加热烟道层 (5) 内, 给储料仓 (6) 内的医疗废弃物加热升温, 同时, 打开尾气出 口 (3)上的阀门 (40), 将储料仓(6) 内的水蒸汽、 易挥性物质和空气 排出储料仓 (6), 并引入到燃烧炉 (27), 经喷嘴 (26)进行燃烧处理; 或者也可以不给储料仓(6) 内的医疗废弃物加热; 打开储料仓(6)和 热裂解釜 (13)之间的连接阀门 (7), 医疗废弃物经裂解釜 (13)上部 的进料口 (35) 下落到热裂解釜(13) 内; 然后, 关闭裂解釜(13)上 部的进料阀门( 7 );循环地重复上述操作方法,既可以确保热裂解釜( 13) 时刻处在密闭条件下, 又可以自由地或连续地给储料仓 ( 6 )进行装料和 卸料, 达到生产的连续性; 将热裂解反应中产生的烃类(烃油( 38)和 / 或可燃性气体)返回到燃烧炉( 27 ),通过燃油喷嘴( 25 )和烃气喷嘴( 28 ) 进行燃烧, 将高温烟气引入到热裂解釜(13), 给热裂解釜(13)加热, 在 300- 450°C及常压或高于常压的条件下, 热裂解釜(13) 内的医疗废 弃物中的各种有机物 (纤维、 塑料、 橡胶、 碳水化合物及其它有机物) 发生热裂解反应, 分解成烃类气相物、 水和残渣, 不断地将气相物排出 热裂解釜(13), 经冷凝器(20)冷凝, 收集烃油 (38), 不凝结的低分 子烃气被引入到燃烧炉 (27)进行燃烧, 燃烧产生高温烟气, 将高温烟 气返回到热裂解釜 (13)给热裂解釜 (13)加热, 提供热裂解反应所需 热量; 在热裂解反应的中后期, 热裂解釜向外排放的烃类渐渐减少 , 用 泵( 22 )将烃油( 38 )输入到燃烧炉( 27 ), 经燃烧喷嘴( 25 )进行燃烧, 保持热裂解反应所需热量; 为了避免渐渐增多的残渣占用热裂解釜( 13 ) 内的原料空间和热裂解空间, 应该不断地将残渣排出热裂解釜(13), 以 维持高温条件下的连续化生产; 排渣时, 打开密闭储渣罐(15)上部的 尾气出口( 18 )管上的阀门( 39 ),按尾气出口向外的方向喷射水蒸汽( 17 ), 利用射流产生负压或真空的物理原理 5 储渣罐 (15) 内的空气随水蒸汽 (17)排出储渣罐(15), 储渣罐(15) 内形成真空或负压环境; 打开热 裂解釜 (13)下部的排渣口 ( 37) 阀门 (14), 热裂解釜 (13) 中的残渣 受储渣罐 (15) 内的负压吸引和重力作用, 经热裂解釜 (13) 的排渣阀 门( 14 )往下落入到储渣罐( 15 )内; 关闭热裂解釜( 13 )与储渣罐 ( 15 ) 相连接的排渣阀门 (14), 即关闭储渣罐(15)上部的进渣口 (42), 停 止喷射水蒸汽( Π ), 然后, 打开储渣罐 ( 15 )下部的排渣孔阔门 ( 16 ), 将残渣排出储渣罐(15), 再关闭排渣孔阀门 (16); 循环地重复上述排 渣操作方法, 既可以随意地或自由地将热裂解釜(13) 中的残渣排出装 置, 又维持了热裂解釜(13) 内的密封条件, 确保了热裂解反应在高温 条件下的连续化进行。 进一步将储渣灌 (i5) 中排出的有机残渣输送到 燃烧炉 ( 27) 内, 经 850- 1300 高温焚烧处理至烬, 燃烧后产生的高温 烟气返回到热裂解反应釜(13)给反应釜(13)供热。 根据医疗废弃物 中废弃物成份和 /或种类的变化, 如果热裂解反应在 300- 450°C温度下能 将医疗废弃物或原料彻底分解, 裂解残渣是无机物, 储渣罐内的灰渣不 需返到燃烧炉中进行焚烧处理。 The medical waste is not crushed or crushed to a size of less than 35 cm, and enters the storage silo (6) through the feeding port (2) of the storage silo (6); before charging, open the storage silo ( 6) The valve (41) of the water vapor inlet (4) and the valve (40) of the exhaust gas outlet (3) on the upper side, pass the water vapor (17) into the sealed storage bin (6), and use the water vapor (17) The high-temperature hydrocarbon gas in the storage silo (6) is driven out of the storage silo (6) through the tail gas outlet (3), and the hydrocarbon gas is sent to the combustion furnace (27), and is burned through the nozzle (26); , Close the steam valve (41) and the exhaust gas outlet valve (40); open or open the filler cap or valve (1) of the storage bin (6), and load the medical waste into the storage bin (6), close or Seal the feeding port (2); Seal the feeding port (2) with a cover or valve (1); Pass water vapor (17) into the storage bin (6), The air in the storage bin (6) is driven out of the storage bin (6) through the tail gas outlet (3) of the storage bin (6), or the waste heat flue gas discharged from the thermal cracker (13) is introduced into the storage bin (6) In the outer heating flue layer (5), heat up the medical waste in the storage bin (6), at the same time, open the valve (40) on the exhaust gas outlet (3), and place the storage bin (6) in The water vapor, volatile substances and air are discharged from the storage bin (6), and introduced into the combustion furnace (27), and burned through the nozzle (26); or the medical treatment in the storage bin (6) may not be provided. Waste heating; open the connection valve (7) between the storage bin (6) and the thermal cracking kettle (13), and the medical waste drops to the thermal cracking kettle through the feed port (35) on the upper part of the cracking kettle (13) ( 13); then, close the feed valve (7) on the top of the cracker (13); repeat the above operation method cyclically, not only to ensure that the thermal cracker (13) is always in a closed condition, but also freely or continuously Loading and unloading to the storage silo (6) to achieve production continuity; returning the hydrocarbons (hydrocarbon oil (38) and / or flammable gas) generated in the thermal cracking reaction to A furnace (27), which is burned through a fuel nozzle (25) and a hydrocarbon gas nozzle (28), introduces high temperature flue gas into a thermal cracking kettle (13), and heats the thermal cracking kettle (13) at 300-450 ° C Under normal or higher pressure conditions, various organic substances (fiber, plastic, rubber, carbohydrates, and other organic substances) in the medical waste in the thermal cracker (13) undergo thermal cracking reactions and decompose into hydrocarbons. The gas phase, water and residue are continuously discharged from the thermal cracker (13), condensed by the condenser (20), and the hydrocarbon oil (38) is collected, and the non-condensed low molecular hydrocarbon gas is introduced into the combustion furnace (27) Combustion, combustion produces high-temperature flue gas, returns the high-temperature flue gas to the thermal cracking kettle (13), and heats the thermal cracking kettle (13) to provide the heat required for the thermal cracking reaction. The externally discharged hydrocarbons are gradually reduced, and the hydrocarbon oil (38) is input to the combustion furnace (27) by a pump (22), and is burned through a combustion nozzle (25) to maintain the heat required for the thermal cracking reaction; in order to avoid gradually increasing residues Occupied thermal cracker (13) The raw material space and thermal cracking space should be continuously discharged from the thermal cracking kettle (13) to maintain continuous production under high temperature conditions. When discharging slag, open the tail gas outlet (18) of the closed slag storage tank (15) ) The valve (39) on the pipe injects water vapor (17) in the outward direction of the tail gas outlet, and uses the physical principle of negative pressure or vacuum generated by the jet. 5 The air in the slag storage tank (15) is discharged with the water vapor (17) A vacuum or negative pressure environment is formed in the slag storage tank (15), and the slag storage tank (15) forms a vacuum or negative pressure environment; open the slag discharge port (37) valve (14) in the lower part of the thermal cracker (13), and the residue in the thermal cracker (13) Affected by the negative pressure and gravity in the slag storage tank (15), it is dropped into the slag storage tank (15) through the slag discharge valve (14) of the thermal cracking kettle (13); the thermal cracking kettle (13) and the The slag discharge valve (14) connected to the slag storage tank (15) closes the slag inlet (42) at the upper part of the slag storage tank (15), stops spraying water vapor (Π), and then opens the slag storage tank (15) The lower slag discharge hole wide door (16) discharges the residue out of the slag storage tank (15), and then closes the slag discharge valve (16); Or optionally in the thermal cracking vessel (13) in the residue discharge device freely, and to maintain a sealed condition within the pyrolysis reactor (13), to ensure the continuous thermal cracking reaction performed at high temperature conditions. The organic residues discharged from the slag storage irrigation (i5) are further transported into the combustion furnace (27), and treated by 850-1300 high temperature incineration to embers. The high-temperature flue gas generated after combustion is returned to the thermal cracking reactor (13) for reaction The kettle (13) provides heat. According to the changes in the composition and / or type of waste in medical waste, if the thermal cracking reaction can completely decompose medical waste or raw materials at a temperature of 300-450 ° C, the cracking residue is an inorganic substance, and the ash in the slag tank No need to return to the burner for incineration.
以下通过具体实施例更详细地说明本发明,但本发明并不受其限制。 实 施 例 将 500KG医疗废弃物通过储料仓( 6 )的加料口 ( 2 )进入到储料仓 ( 6 )中; 加料前, 先打开储料仓( 6 )上的水蒸汽进口 ( 4 )的阀门 ( 41 ) 和尾气出口 ( 3 ) 的阀门 ( 40 ), 将 0.03Mpa压力的水蒸汽 ( 17 )通入密 封的储料仓 (6) 中, 用水蒸汽 (17)将储料仓 (6) 内的高温烃类气体 经尾气出口 ( 3 )驱赶出储料仓 ( 6 ), 并将烃类气体输送到燃烧炉 ( 27 ), 通过喷嘴(26)去燃烧; 然后,关闭蒸汽阀门(41)和尾气出口阀门(40); 打开储料仓 ( 6 )的加料口盖子或阀门 (1), 将 500KG的医疗废弃物分次 装入储料仓(6) 中, 关闭或密封加料口 (2); 用盖子或阀门 (1) 密封 加料口 ( 2 ); 将热裂解釜 ( 13 )排出的余热烟气引入储料仓 ( 6 )外层的 加热烟道层 (5) 内, 给储料仓 (6) 内的医疗废弃物加热升温, 从储料 仓( 6 )排出的余热烟气再引入到余热锅炉 ( 12 ), 给余热锅炉 ( 12 )加 热产生水蒸汽(17), 回收热量; 同时, 打开储料仓(6)的尾气出口 (3) 上的阀门 (40), 将储料仓(6) 内废弃物产生的水蒸汽和易挥性物质以 及储料仓内的空气排出储料仓( 6 ), 并引入到燃烧炉( 27 ), 经喷嘴( 26 ) 进行燃烧处理; 打开储料仓 ( 6 )和热裂解釜 (13)之间的连接阀门 ( 7 ), 医疗废弃物经裂解釜(13)上部的进料口 (35) 下落到热裂解釜(13) 内; 然后, 关闭裂解釜(13)上部的进料阀门 (7); 循环地重复上述操 作方法 5次, 可将 500KG医疗废弃物投入热裂解釜(13) 内, 以确保热 裂解反应所需原料, 达到生产的连续性; 将裂解反应中产生的可燃性气 体和 /或烃油 (38)或购买商品燃料油引入到燃烧炉 (27), 经燃油喷嘴 (25)和燃气喷嘴(28)进行燃烧, 将高温烟气引入到热裂解釜(13), 给热裂解釜(13)中似的物料升温至 40(TC,加热 2小时, 热裂解釜(13) 内的医疗废弃物中的各种有机物 (纤维、 塑料、 橡胶、 碳水化合物及其 它有机物)发生热裂解反应, 分解成烃类气相物、 水和残渣, 不断地将 气相物排出热裂解釜 (13), 用室温空气与排出的气相物在冷凝器 (20) 中进行热交换, 气相物经冷凝器(20)冷凝, 收集得到烃油 (38), 而不 凝结的可燃性气体 (H2 和 C-C6 )被引入到燃烧炉 (27), 通过燃气喷嘴Hereinafter, the present invention will be described in more detail through specific examples, but the present invention is not limited thereto. Examples 5 00KG medical waste through the storage bin (6) of the feed opening (2) into a storage bin (6); before the addition, the storage bin is opened to the steam inlet valve (4) on (6) (41) and the valve (40) of the exhaust gas outlet (3), pass water vapor (17) with a pressure of 0.03Mpa into the sealed storage bin (6), and use water vapor (17) to place the inside of the storage bin (6) The high-temperature hydrocarbon gas is driven out of the storage bin (6) through the tail gas outlet (3), and the hydrocarbon gas is sent to the combustion furnace (27) for combustion through the nozzle (26); then, the steam valve (41) and the steam valve (41) are closed. Exhaust gas outlet valve (40); Open the filling port cover or valve (1) of the storage bin (6), load 500KG of medical waste into the storage bin (6) in stages, and close or seal the charging port (2) Seal the charging port (2) with a lid or valve (1); Introduce the waste heat flue gas from the thermal cracker (13) into the heating flue layer (5) on the outer layer of the storage silo (6) and feed it to the storage silo (6) The medical waste inside is heated and heated, and the waste heat flue gas discharged from the storage bin (6) is reintroduced into the waste heat boiler (12), and the waste heat boiler (12) is heated to generate water vapor (17). At the same time, open the valve (40) on the tail gas outlet (3) of the storage bin (6), and remove the water vapor and volatile substances generated by the waste in the storage bin (6) and the The air is discharged from the storage bin (6), and is introduced into the combustion furnace (27), and is burned through the nozzle (26); the connection valve (7) between the storage bin (6) and the thermal cracker (13) is opened, The medical waste is dropped into the thermal cracker (13) through the feed port (35) on the upper part of the cracker (13); then, the feed valve (7) on the upper part of the cracker (13) is closed; the above operation method is repeated cyclically 5 times, 500KG medical waste can be put into the pyrolysis kettle (13) to ensure the raw materials required for the pyrolysis reaction to achieve the continuity of production; the flammable gas and / or hydrocarbon oil produced in the cracking reaction (38) Or purchase commercial fuel oil to be introduced into the combustion furnace (27), burn through the fuel nozzle (25) and gas nozzle (28), introduce high temperature flue gas into the thermal cracking kettle (13), and feed the thermal cracking kettle (13) like The material is heated to 40 (TC, heated for 2 hours, thermal cracker (13) Various organic substances (fibers, plastics, rubber, carbohydrates and other organic substances) in the medical wastes within it undergo thermal cracking reactions, decompose into hydrocarbon gaseous substances, water and residues, and continuously discharge the gaseous substances out of the thermal cracking kettle (13 ), Use room temperature air and the discharged gas phase to perform heat exchange in the condenser (20), the gas phase is condensed by the condenser (20), and the hydrocarbon oil (38) is collected, and the non-condensable flammable gas (H 2 and CC 6 ) is introduced into the combustion furnace (27), through the gas nozzle
( 28 )进行燃烧, 将冷凝器( 20 )换热后的高温空气引入到燃烧炉( 27 ), 燃烧产生高温烟气, 将高温烟气返回到热裂解釜( 13 )给热裂解釜( 13 ) 加热, 提供热裂解反应所需热量; 在热裂解反应的中后期, 热裂解釜向 外排放的烃类渐渐减少, 用泵(22)将烃油 (38)输入到燃烧炉 (27), 经燃烧喷嘴 (25)进行燃烧, 保持热裂解反应所需热量; 为了避免渐渐 增多的残渣占用热裂解釜(13) 内的原料空间和热裂解空间, 应该不断 地将残渣排出热裂解釜(13),以维持高温条件下的连续化生产;排渣时, 打开密闭储渣罐 ( 15 )上部的尾气出口 ( 18 )管上的阀门 ( 39 ), 按尾气 出口向外的方向喷射水蒸汽( 17 ),利用射流产生负压或真空的物理原理, 储渣罐( 15 ) 内的空气随水蒸汽( 17 )排出储渣罐 ( 15 ), 储渣罐 ( 15 ) 内形成真空或负压环境; 打开热裂解釜(13) 下部的排渣口 (37) 阀门(28) Combustion is performed, and the high-temperature air exchanged by the condenser (20) is introduced into the combustion furnace (27), and combustion generates high-temperature flue gas, and the high-temperature flue gas is returned to the thermal cracking kettle (13) to the thermal cracking kettle (13) ) Heating to provide the heat required for the thermal cracking reaction; in the middle and late stages of the thermal cracking reaction, the hydrocarbons emitted from the thermal cracking kettle gradually decreased, and the hydrocarbon oil (38) was input to the combustion furnace (27) using a pump (22), Combustion through the combustion nozzle (25) to maintain the heat required for the thermal cracking reaction; in order to avoid the increasing residue occupying the raw material space and thermal cracking space in the thermal cracking kettle (13), the residue should be continuously discharged from the thermal cracking kettle (13) ) To maintain continuous production under high temperature conditions; when discharging slag, open the valve (39) on the tail gas outlet (18) tube at the upper part of the closed slag storage tank (15), and spray water vapor in the outward direction of the tail gas outlet ( 17), using the physical principle of negative pressure or vacuum generated by the jet, the air in the slag storage tank (15) is discharged with the water vapor (17) out of the slag storage tank (15), and a vacuum or negative pressure environment is formed in the slag storage tank (15) Open the lower part of the pyrolysis kettle (13); Slag hole (37) of the valve
(14), 热裂解釜(13) 中的残渣受储渣罐(15) 内的负压吸引和重力作 用, 经热裂解釜(13) 的排渣阀门 (14)往下落入到储渣罐(15) 内; 关闭热裂解釜 ( 13)与储渣罐 ( 15 )相连接的排渣阀门 ( 14 ), 即关闭储 渣罐 (15)上部的进渣口 (42), 停止喷射水蒸汽 (17), 然后, 打开储 渣罐 (15) 下部的排渣孔阀门 (16), 将残渣排出储渣罐 (15), 再关闭 排渣孔阀门( 16 );循环地重复上述排渣操作方法 1次,便将热裂解釜( 13) 中的残渣排出装置, 确保了热裂解反应在高温条件下的连续化进行; 将 储渣灌(15) 中排出的有机残渣输送到燃烧炉 (27) 内, 经 855-1050C 高温焚烧处理至烬, 燃烧后产生的高温烟气返回到热裂解反应釜(13) 给反应釜 (13)供热。 经过上述生产过程 (热裂解反应)得到如下结果: (14), the residue in the thermal cracking kettle (13) is attracted by the negative pressure in the slag storage tank (15) and the action of gravity, it is dropped into the slag storage tank through the slag discharge valve (14) of the thermal cracking kettle (13) (15) Inside; Close the slag discharge valve (14) connected to the thermal cracker (13) and the slag storage tank (15), that is, close the slag inlet (42) at the upper part of the slag storage tank (15), and stop spraying water vapor (17), then, open the slag discharge valve (16) at the lower part of the slag storage tank (15), discharge the residue out of the slag storage tank (15), and then close the slag discharge valve (16); repeat the above slag discharge operation cyclically Method 1 time, the pyrolysis kettle (13) The residue discharge device ensures the continuous progress of the thermal cracking reaction under high temperature conditions; the organic residue discharged from the slag storage irrigation (15) is transferred to the combustion furnace (27), and treated by 855-1050C high temperature incineration to embers The high-temperature flue gas generated after combustion is returned to the thermal cracking reactor (13) to supply heat to the reactor (13). After the above production process (thermal cracking reaction), the following results were obtained:
医疗废弃物: 500KG; Medical waste: 500KG;
医疗废弃物成份: 挥发物 70.5%, 固体类 19%, 金属及无机物 10.5%; 生活垃圾元素分析: H 5.1% , 0 18.2% , C 54% , S 0.4% Medical waste composition: volatiles 70.5%, solids 19%, metals and inorganics 10.5%; elemental analysis of domestic waste: H 5.1%, 0 18.2%, C 54%, S 0.4%
N 8.5%, 金属及无机物 13.8%;  N 8.5%, metal and inorganic matter 13.8%;
储料仓操作温度: 室温 至 120°C; Storage bin operating temperature: room temperature to 120 ° C;
储料仓操作压力: 常压 (小于 0. IMPa); Storage bin operating pressure: atmospheric pressure (less than 0. IMPa);
热裂解反应温度: 400 ±50°C; Thermal cracking reaction temperature: 400 ± 50 ° C;
热裂解反应时间: 1小时; Thermal cracking reaction time: 1 hour;
热裂解釜内压力: 0.03-0.07Mpa Pressure in the thermal cracking kettle: 0.03-0.07Mpa
储渣罐内操作压力: 410—709 匪 Hg (真空度或负压); Operating pressure in the slag tank: 410-709 Hg (vacuum degree or negative pressure);
燃烧炉内温度: 855-1050°C Combustion furnace temperature: 855-1050 ° C
反应产物(W%): 烃油 (C厂 C52 ) 94KG 18.8%; Reaction product (W%): hydrocarbon oil (C plant C 52 ) 94KG 18.8%;
气体( H2 和 d-C6 ) 203KG 40.6%; Gas (H 2 and dC 6 ) 203KG 40.6%;
无机残渣及金属 19.8%;  Inorganic residues and metals 19.8%;
水分 104KG 20.8%0 Moisture 104KG 20.8% 0

Claims

权利 要 求 Rights request
1. 一种处理医疗废弃物的方法, 医疗废弃物包含一种或多种下列物 质: 有机聚合物、 有机纤维物质.. 碳水化合物、 人体组织器官或其它有 机残余物、 无机-及金属材料、 器械等, 该方法包括以下步骤: 1. A method of treating medical waste, which includes one or more of the following: organic polymers, organic fiber substances: carbohydrates, human tissues or other organic residues, inorganic- and metallic materials, Equipment, etc., the method includes the following steps:
V ) 将所述的医疗废弃物装入裂解设备内并密闭该设备; vi ) 加热该裂解设备, 使物料在 300-450°C保持 0. 2-4小时, 进 行热裂解反应, 收集并利用热裂解反应的气相产物; vii ) 将裂解反应残渣排出裂解设备, 送到燃烧炉中焚烧至烬; viii ) 从燃烧炉中排出并处置焚烧后的灰渣。  V) loading the medical waste into a cracking device and sealing the device; vi) heating the cracking device to keep the material at 300-450 ° C for 0. 2-4 hours, performing a thermal cracking reaction, collecting and using The gaseous products of the thermal cracking reaction; vii) the residues of the cracking reaction are discharged from the cracking equipment and sent to a burner for incineration to ashes; viii) the burned ash is discharged from the burner and disposed of.
2.按权利要求 1的方法, 其特征在于, 所述的热裂解反应分两步进 行,第一步为将医疗废弃物在裂解设备包含的一个储料 /气化单元中升温 至不超过 250°C , 维持 0. 2-2 小时, 其间产生的气体产物送到燃烧炉中 燃烧并回收热量, 剩余物再引入裂解设备包含的一个热裂解单元中, 使 其在 300-450°C保持 0. 2-4小时, 以完成热裂解反应。 The method according to claim 1, characterized in that the thermal cracking reaction is performed in two steps, and the first step is to raise the medical waste in a storage / gasification unit included in the cracking equipment to a temperature not exceeding 2 5 0 ° C, maintained 0.2 - 2 hours, during which the generated gaseous products of combustion to a combustion furnace and heat recovery, the residue was introduced into a thermal cracking unit comprising the cracking unit, so that the 300-450 ° C Keep it for 0.2 to 4 hours to complete the pyrolysis reaction.
3.按权利要求 1或 1的方法, 其特征在于, 所述的裂解反应所产生 的气相产物的收集利用是指, 将气相产物经冷凝处理并收集冷凝下来的 液相烃油, 将未凝结的气体引入燃烧炉进行燃烧, 并利用燃烧放出来的 热为热裂解反应过程供热。  3. The method according to claim 1 or 1, characterized in that the collection and utilization of the gas-phase products produced by the cracking reaction means that the gas-phase products are subjected to condensation treatment and the condensed liquid-phase hydrocarbon oil is collected, and the non-condensed The gas is introduced into the combustion furnace for combustion, and the heat released by the combustion is used to provide heat for the thermal cracking reaction process.
4. 按权利要求 1的方法, 其特征在于, 其中所述的热裂解反应残渣 在燃烧炉内在 850- 130(TC焚烧, 裂解和焚烧操作的压力各为常压或稍獨: 力口压。 The method according to claim 1, wherein the thermal cracking reaction wherein the residue in the combustion furnace 8 5 0- 130 (TC incineration operation and incineration cracking pressure is atmospheric or slightly each alone: opening force Pressure.
5. 按权利要求 1的方法, 其特征在于, 其中所述的热裂解反应残渣 先排放到一个可密闭的储渣罐中, 待积累到一定量后再一并送到燃烧炉 焚烧。 5. The method according to claim 1, characterized in that said thermal cracking reaction residue It is first discharged into a sealable slag storage tank, and after a certain amount is accumulated, it is sent to a burner for incineration.
6. —种处理医疗废弃物的设备, 主要包括: 储料仓、 热裂解设备、 储渣罐、 燃烧炉、 烃油收集装置;  6. — A kind of equipment for treating medical waste, mainly including: storage silos, thermal cracking equipment, slag storage tanks, combustion furnaces, and hydrocarbon oil collection devices;
所述的储料仓包括: 可为圆柱形或矩形的壳体, 壳体的外层是加热 用的烟道气通道层, 壳体的上部装有加料开孔, 并配备密封盖或阀门; 壳体的下部装有通向热裂解设备的卸料口, 并配备阀门; 壳体上部装有 蒸汽进口和气体排放出口;  The storage bin includes: a cylindrical or rectangular shell, an outer layer of the shell is a flue gas channel layer for heating, an upper part of the shell is provided with a feeding opening, and is equipped with a sealing cover or a valve; The lower part of the shell is equipped with a discharge port leading to the thermal cracking equipment and is equipped with a valve; the upper part of the shell is equipped with a steam inlet and a gas exhaust outlet;
所述的热裂解设备位于储料仓的下方, 包括: 可为圆柱形或矩形的 上部壳体、 与上部壳体形状匹配但逐渐收口的圆锥形或弧顶向上的圆形 封头状下部壳体, 上部和下部壳体紧密结合; 壳体的外层是加热用的烟 道气通道层; 壳体的上部有加料开孔, 开孔上配备阀门, 此阀门与储料 仓的卸料口相连接; 壳体下部或下部侧面安装有排渣口, 并配备阀门, 此阀门与储渣罐的残渣入口相连接;壳体上部装有通向烃油收集装置和 / 或燃烧炉的气相物排放口;  The thermal cracking equipment is located below the storage silo, and includes: a cylindrical or rectangular upper shell, a conical or arc-shaped round head-shaped lower shell that matches the shape of the upper shell but gradually closes. Body, the upper and lower shells are closely combined; the outer layer of the shell is a flue gas channel layer for heating; the upper part of the shell has a feeding opening, and a valve is arranged on the opening. This valve is connected to the discharge opening of the storage bin. The lower part or the lower side of the shell is equipped with a slag discharge port and is equipped with a valve, which is connected to the residue inlet of the slag storage tank; the upper part of the shell is equipped with a gas phase material leading to the hydrocarbon oil collecting device and / or the combustion furnace exhaustion hole;
所述的储渣罐包括: 圆柱形或矩形壳体, 壳体的上部有残渣进入开 口, 壳体下部有排渣口, 并配备排渣阀门; 壳体上部装有尾气出口; 所述的燃烧炉包括: 供燃烧和焚烧的圆柱形或矩形壳体、 壳壁上有与 储料仓相连的气化物入口、 与烃油收集装置相连的未冷凝气化物入口、 液体烃油燃烧喷嘴、 燃烧获得的高温烟气出口、 来自储渣罐的残渣焚烧 入口以及壳内供固体物质焚烧用的炉排;  The slag storage tank includes: a cylindrical or rectangular shell, the upper part of the shell has a residue entry opening, the lower part of the shell has a slag discharge port, and is equipped with a slag discharge valve; the upper part of the shell is equipped with an exhaust gas outlet; the combustion The furnace includes: a cylindrical or rectangular shell for combustion and incineration, a gas inlet connected to a storage bin on the shell wall, an uncondensed gas inlet connected to a hydrocarbon oil collection device, a liquid hydrocarbon oil combustion nozzle, and combustion obtained High temperature flue gas outlets, residue incineration inlets from slag storage tanks, and grate in the shell for incineration of solid materials;
所述的烃油收集装置包括: 冷凝装置和气液分离装置,冷凝装置可以 接受来自于裂解设备的气化产物, 使其冷凝后分离为气液两种产物, 储 存于气液分离器或烃油储罐中, 可用室温空气或室温水给冷凝装置降温 换热, 换热后的热空气进入燃烧炉; 空气经冷凝装置后进入燃烧炉; 气 液分离装置或烃油储罐收集来自于冷凝装置的气液产物, 并有出口与燃 烧炉相连。 The hydrocarbon oil collecting device includes: a condensing device and a gas-liquid separation device. The condensing device may It accepts the gasification products from the cracking equipment, condenses and separates them into two kinds of gas-liquid products. It is stored in a gas-liquid separator or a hydrocarbon oil storage tank. The condensing device can be cooled and exchanged with room temperature air or room temperature water. After the hot air enters the combustion furnace; the air enters the combustion furnace after the condensation device; the gas-liquid separation device or the hydrocarbon oil storage tank collects the gas-liquid products from the condensation device, and has an outlet connected to the combustion furnace.
7. 按权利要求 6的设备, 其特征在于, 所述医疗废弃物处理设备可 以包括余热锅炉, 可以利用来自于其他装置的高温烟气以加水并产生水 蒸气。 7. The device according to claim 6, characterized in that the medical waste treatment equipment may include a waste heat boiler, and high-temperature flue gas from other devices may be used to add water and generate water vapor.
, ,
8. 按权利要求 6的设备, 其特征在于, 所述的裂解设备可以是旋转 式反应器, 或是圆柱形壳体, 壳体的底部可以是弧顶向上的圆形封头, 排渣孔配置在壳体下部的侧面上, 或矩形壳体反应器, 壳体内可以安装 搅拌器。 8. The device according to claim 6, characterized in that the cracking device can be a rotary reactor or a cylindrical shell, and the bottom of the shell can be a round head with an arc top upward, and a slag discharge hole It is arranged on the side of the lower part of the shell or a rectangular shell reactor, and a stirrer can be installed in the shell.
9. 按权利要求 6的设备, 其特征在于,裂解设备壳体内部装有加热 烟道管, 烟道管与壳体外层的烟道通道相连通。  9. The apparatus according to claim 6, characterized in that a heating flue pipe is arranged inside the casing of the cracking apparatus, and the flue pipe is in communication with the flue channel of the outer layer of the shell.
PCT/CN2003/000826 2003-03-20 2003-09-27 Method and apparatus for treating medical materials WO2004090422A1 (en)

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CN2371450Y (en) * 1998-12-23 2000-03-29 潘其俊 Medical refuse incinerator
RU2157950C1 (en) * 1999-10-22 2000-10-20 Коржевенко Геннадий Николаевич Installation for disposal of chemical, infected medical and biological waste and other hazardous materials, dead bodies of animals inclusive
RU2157951C1 (en) * 1999-10-22 2000-10-20 Тартынов Игорь Викторович Method for disposal of infected medical, chemical and biological waste and other hazardous materials, dead bodies of animals inclusive, and compound for its realization
US6139793A (en) * 1997-09-05 2000-10-31 Hydroclave Systems Corporation Waste treatment control system
JP2001021125A (en) * 1999-07-09 2001-01-26 Takuma Co Ltd Apparatus and method for recycling valuable material in equipment for dry distillation, thermal cracking, melting and combustion o waste
JP2001263624A (en) * 2000-03-21 2001-09-26 Makoto Ogose Method and system for carbonizing and melting organic matter
CN1339671A (en) * 2000-08-17 2002-03-13 郭春宝 Integrated continuous harmful refuse processing system comprising cracking furnace and incinerating furnace
WO2002021047A1 (en) * 2000-09-05 2002-03-14 Kawasaki Jukogyo Kabushiki Kaisha Waste-gasified fusion furnace and method of operating the fusion furnace

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6139793A (en) * 1997-09-05 2000-10-31 Hydroclave Systems Corporation Waste treatment control system
CN2371450Y (en) * 1998-12-23 2000-03-29 潘其俊 Medical refuse incinerator
JP2001021125A (en) * 1999-07-09 2001-01-26 Takuma Co Ltd Apparatus and method for recycling valuable material in equipment for dry distillation, thermal cracking, melting and combustion o waste
RU2157950C1 (en) * 1999-10-22 2000-10-20 Коржевенко Геннадий Николаевич Installation for disposal of chemical, infected medical and biological waste and other hazardous materials, dead bodies of animals inclusive
RU2157951C1 (en) * 1999-10-22 2000-10-20 Тартынов Игорь Викторович Method for disposal of infected medical, chemical and biological waste and other hazardous materials, dead bodies of animals inclusive, and compound for its realization
JP2001263624A (en) * 2000-03-21 2001-09-26 Makoto Ogose Method and system for carbonizing and melting organic matter
CN1339671A (en) * 2000-08-17 2002-03-13 郭春宝 Integrated continuous harmful refuse processing system comprising cracking furnace and incinerating furnace
WO2002021047A1 (en) * 2000-09-05 2002-03-14 Kawasaki Jukogyo Kabushiki Kaisha Waste-gasified fusion furnace and method of operating the fusion furnace

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