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CN110066083B - Sludge pyrolysis recycling system and pyrolysis method - Google Patents

Sludge pyrolysis recycling system and pyrolysis method Download PDF

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CN110066083B
CN110066083B CN201910288836.9A CN201910288836A CN110066083B CN 110066083 B CN110066083 B CN 110066083B CN 201910288836 A CN201910288836 A CN 201910288836A CN 110066083 B CN110066083 B CN 110066083B
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pyrolysis
sludge
solid
gas
reactor
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CN110066083A (en
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刘冬梅
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Beijing Zhongchuang Carbon Investment Energy Technology Co ltd
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Jiahe Juneng Tianjin Technology Co ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/10Treatment of sludge; Devices therefor by pyrolysis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/13Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B49/00Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated
    • C10B49/16Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated with moving solid heat-carriers in divided form
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B57/00Other carbonising or coking processes; Features of destructive distillation processes in general
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B57/00Other carbonising or coking processes; Features of destructive distillation processes in general
    • C10B57/08Non-mechanical pretreatment of the charge, e.g. desulfurization
    • C10B57/10Drying
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/40Valorisation of by-products of wastewater, sewage or sludge processing

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Materials Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The embodiment of the invention provides a sludge pyrolysis recycling system, which adopts solid porcelain balls or quartz sand as a heat carrier to rapidly transfer heat to sludge according to the material and pyrolysis characteristics of the sludge, and comprises a spiral pyrolysis reactor which is specially designed and can realize forced mixing and rapid heat transfer of the sludge. The invention adopts the solid heat carrier and sludge to mix and heat directly, and has high heat efficiency and uniform heating compared with an indirect heating mode; the spiral blades and the stirring blades are reasonably arranged in the pyrolysis reactor, so that the full mixing and the rapid heat transfer of the sludge and the heat carrier can be realized, the pyrolysis reaction rate is high, the system processing capacity is high, the coking problem caused by uneven sludge stirring is effectively solved, and the long-term stable operation of the system is realized; the waste heat flue gas pre-drying sludge is recycled, so that the energy grading utilization is realized, the energy consumption can be effectively reduced, and the energy utilization efficiency of the system is improved. The embodiment of the invention also provides a method for pyrolyzing the sludge by adopting the sludge pyrolysis recycling system.

Description

污泥热解资源化系统及热解方法Sludge pyrolysis resource utilization system and pyrolysis method

技术领域Technical field

本发明属于污水处理副产物污泥的无害化、资源化利用技术领域,特别涉及一种污泥热解资源化系统。本发明还提供了一种使用上述污泥热解资源化系统的污泥热解方法。The invention belongs to the technical field of harmlessness and resource utilization of sewage treatment by-product sludge, and particularly relates to a sludge pyrolysis resource utilization system. The present invention also provides a sludge pyrolysis method using the above-mentioned sludge pyrolysis resource utilization system.

背景技术Background technique

污泥为污水处理生产的副产物,组成成分极其复杂,除含有大量的水分外,还含有氮、磷等营养元素、重金属及有机质等,若将污泥直接排放到环境中,会对环境造成危害,并且污泥中所含有机质没有利用,是一种严重浪费。当前污泥处理技术主要包括填埋、堆肥、干化焚烧及热解等。其中,污泥热解为污泥资源化利用的重要手段。污泥热解即为在一定温度和缺氧条件下将污泥的干燥与热分解融为一体,在加热条件下将污泥转变为气、固两相,气体再通过冷凝转化为气、液两相,最终将污泥转化为气体、液体和固体三种相态物质,污泥转化所得的气体中富含气态烃类、氢气、一氧化碳等可燃气,液体经过油水分离可得到油品资源。因此,污泥热解技术可有效实现污泥的减量化、无害化及资源化,日益获得广泛的应用。Sludge is a by-product of sewage treatment production. Its composition is extremely complex. In addition to containing a large amount of water, it also contains nitrogen, phosphorus and other nutrients, heavy metals and organic matter. If the sludge is directly discharged into the environment, it will cause harm to the environment. Harmful, and the organic matter contained in the sludge is not utilized, which is a serious waste. Current sludge treatment technologies mainly include landfill, composting, drying and incineration, and pyrolysis. Among them, sludge pyrolysis is an important means for sludge resource utilization. Sludge pyrolysis is the integration of drying and thermal decomposition of sludge under certain temperature and anoxic conditions. Under heating conditions, the sludge is converted into gas and solid phases, and the gas is then converted into gas and liquid through condensation. Two-phase, the sludge is finally converted into three phase substances: gas, liquid and solid. The gas obtained by sludge conversion is rich in gaseous hydrocarbons, hydrogen, carbon monoxide and other combustible gases. Oil resources can be obtained from the liquid after oil-water separation. Therefore, sludge pyrolysis technology can effectively achieve the reduction, harmlessness and resource utilization of sludge, and is increasingly widely used.

目前针对污泥热解技术主要分为连续型和间歇型,其中:间歇型热解技术处理规模小,运行时间短,应用范围有限;连续型热解工艺主要是采取外壁加热的旋转窑式或螺旋搅拌式热解工艺,处理能力较强,适合工业应用,但在污泥连续热解过程中,污泥物料易粘附成块,使物料打散和传热困难,加热不均,发生反应不充分或反应时间长等问题,导致系统效率降低。鉴于现有技术的上述缺陷,亟待开发一种有利于污泥搅拌和传热的热解工艺,以实现污泥高效和连续热解处理,满足工业应用需要。At present, sludge pyrolysis technology is mainly divided into continuous type and intermittent type. Among them: intermittent pyrolysis technology has small processing scale, short running time and limited application scope; continuous pyrolysis technology mainly adopts the rotating kiln or rotary kiln type with outer wall heating. The spiral stirring pyrolysis process has strong processing capacity and is suitable for industrial applications. However, during the continuous pyrolysis process of sludge, the sludge materials tend to adhere to lumps, making it difficult to break up the materials and transfer heat, leading to uneven heating and reactions. Problems such as insufficient or long response time lead to reduced system efficiency. In view of the above-mentioned shortcomings of the existing technology, it is urgent to develop a pyrolysis process that is conducive to sludge mixing and heat transfer to achieve efficient and continuous pyrolysis treatment of sludge and meet the needs of industrial applications.

发明内容Contents of the invention

本发明要解决的现有污泥热解技术中存在的加热不均、热效率低、系统处理能力不足等问题,提供了新型的污泥热解反应系统及热解方法,采用内热式加热技术,以固体热载体作为反应传热载体,基于优化的热解反应器设计,具有加热均匀、高效低价、易工业化的特点。The present invention aims to solve the problems existing in the existing sludge pyrolysis technology such as uneven heating, low thermal efficiency, and insufficient system processing capacity. It provides a new sludge pyrolysis reaction system and pyrolysis method, which adopts internal heating technology. Using solid heat carrier as reaction heat transfer carrier and based on optimized pyrolysis reactor design, it has the characteristics of uniform heating, high efficiency and low price, and easy industrialization.

为解决前述技术问题,本发明的实施例提供一种污泥热解资源化系统,包括预干燥装置、进料载体斗、出料载体斗、热解反应器、热烟炉、加热提升管、冷凝器、油水分离器、旋风分离器和排渣器,其中:In order to solve the aforementioned technical problems, embodiments of the present invention provide a sludge pyrolysis resource utilization system, which includes a pre-drying device, a feed carrier hopper, a discharge carrier hopper, a pyrolysis reactor, a hot smoke furnace, and a heating riser. Condenser, oil-water separator, cyclone separator and slag discharger, including:

所述热解反应器包括上大下小的中空圆台结构的反应器筒体,所述反应器筒体的中轴位置安装有旋转轴;所述旋转轴上盘绕固定有螺旋叶,所述螺旋叶随所述旋转轴转动而搅动;所述预干燥装置对污泥原料进行预干燥,预干燥后的污泥送入所述热解反应器中;所述进料载体斗位于所述热解反应器上方,所述进料载体斗中的固体物出口连接所述热解反应器,向所述热解反应器中送入固体热载体;污泥和固体热载体在所述热解反应器中混合发生热解反应;所述热解反应器中的热解气送入所述冷凝器中,所述冷凝器中冷凝产生的液体送入所述油水分离器中,在所述油水分离器中分离出水和油;所述出料载体斗位于所述热解反应器下方,所述热解反应器中的固体物经所述出料载体斗送入所述加热提升管中;所述加热提升管下部连接所述热烟炉,将所述热烟炉中燃气燃烧产生的烟气送入所述加热提升管中用于对固体物进行加热提升;所述加热提升管上部的出口连接所述进料载体斗入口,将固体物和烟气送入所述进料载体斗中;所述进料载体斗的气体出口连接所述旋风分离器,将含尘烟气送入所述旋风分离器中;所述旋风分离器中分离出的固体物送入所述排渣器,由所述排渣器排出残渣。The pyrolysis reactor includes a reactor barrel with a hollow truncated cone structure with a large top and a small bottom. A rotating shaft is installed at the central axis of the reactor barrel; spiral blades are coiled and fixed on the rotating shaft, and the spiral The leaves stir with the rotation of the rotating shaft; the pre-drying device pre-dries the sludge raw materials, and the pre-dried sludge is sent to the pyrolysis reactor; the feed carrier hopper is located in the pyrolysis reactor. Above the reactor, the solid matter outlet in the feed carrier hopper is connected to the pyrolysis reactor, and solid heat carriers are fed into the pyrolysis reactor; sludge and solid heat carriers are stored in the pyrolysis reactor The pyrolysis reaction occurs during mixing; the pyrolysis gas in the pyrolysis reactor is sent to the condenser, and the liquid produced by condensation in the condenser is sent to the oil-water separator, and in the oil-water separator Water and oil are separated from the medium; the discharge carrier hopper is located below the pyrolysis reactor, and the solid matter in the pyrolysis reactor is sent into the heating riser through the discharge carrier hopper; the heating The lower part of the riser tube is connected to the hot smoke furnace, and the flue gas generated by the combustion of gas in the hot smoke furnace is sent into the heating riser tube for heating and lifting of solid objects; the outlet of the upper part of the heating riser tube is connected to the The inlet of the feed carrier hopper sends solid matter and flue gas into the feed carrier hopper; the gas outlet of the feed carrier hopper is connected to the cyclone separator, and dust-containing flue gas is sent into the cyclone separation in the device; the solid matter separated in the cyclone separator is sent to the slag discharger, and the residue is discharged from the slag discharger.

作为所述热解反应器的优选,所述螺旋叶上沿叶片延伸方向依次固定有多个搅拌叶,所述搅拌叶为方形或圆形凸起的筋条。Preferably, the pyrolysis reactor has a plurality of stirring blades fixed on the spiral blades along the blade extension direction, and the stirring blades are square or circular raised ribs.

作为所述热解反应器的优选,所述反应器筒体上端一侧设置有所述热载体进口和所述污泥进口,对侧设置有所述热解气出口,所述热载体进口位置高于所述污泥进口,所述反应器筒体下端侧部还设置有固体物出口;所述预干燥装置的污泥出口连接所述污泥进口,向所述热解反应器中送入污泥;所述进料载体斗的固体出口连接所述热载体进口,向所述热解反应器中送入固体热载体;所述热解气出口连接所述冷凝器的入口,将热解反应后的热解气送入所述冷凝器中;所述固体物出口连接所述出料载体斗,将热解反应后的固体混合物排出至所述出料载体斗中。进一步优选地,所述热解反应器的热解气出口与若干侧排气口连通,所述侧排气口伸入所述反应器筒体内,用于收集内部的热解气,并将收集到的热解气汇集导至所述热解气出口排出。As a preferred option of the pyrolysis reactor, the heat carrier inlet and the sludge inlet are provided on one side of the upper end of the reactor barrel, and the pyrolysis gas outlet is provided on the opposite side. The heat carrier inlet is located at the Higher than the sludge inlet, a solid matter outlet is also provided at the lower end side of the reactor barrel; the sludge outlet of the pre-drying device is connected to the sludge inlet and is fed into the pyrolysis reactor sludge; the solid outlet of the feed carrier hopper is connected to the heat carrier inlet, and the solid heat carrier is fed into the pyrolysis reactor; the pyrolysis gas outlet is connected to the inlet of the condenser, and the pyrolysis gas outlet is connected to the inlet of the condenser. The pyrolysis gas after the reaction is sent into the condenser; the solid matter outlet is connected to the discharge carrier hopper, and the solid mixture after the pyrolysis reaction is discharged into the discharge carrier hopper. Further preferably, the pyrolysis gas outlet of the pyrolysis reactor is connected to several side exhaust ports, and the side exhaust ports extend into the reactor barrel for collecting the internal pyrolysis gas and collecting the pyrolysis gas. The collected pyrolysis gases are collected and directed to the pyrolysis gas outlet for discharge.

作为所述加热提升管的优选,所述加热提升管由下至上依次为进料段、扩张段和提升段,所述进料段包括固体进料口、热烟气管道、外套管、内套管、溜料口及固体分布器,其中:As the preferred heating riser, the heating riser consists of a feed section, an expansion section and a lifting section from bottom to top. The feed section includes a solid feed port, a hot flue gas pipe, an outer casing, and an inner casing. Pipes, feed chute and solid distributor, including:

所述固体进料口设置在所述外套管的上侧部;所述内套管套置于所述外套管内,所述内套管下端与所述外套管下底之间设置所述溜料口,所述外套管中的固体物料可通过所述溜料口进入所述内套管中;所述热烟气管道自所述外套管底部插入,并从下方伸入所述内套管中,所述热烟气管道与所述内套管间具有间隙;所述固体分布器位于所述溜料口位置,并环绕在所述热烟气管道外壁上,所述固体分布器上设置有高压气进口及沿周向均匀布置的多个分布气喷嘴,分布气从所述高压气进口通入所述固体分布器中,并经所述分布气喷嘴向上方喷出。The solid feed port is provided on the upper side of the outer casing; the inner casing is placed inside the outer casing, and the material slide is arranged between the lower end of the inner casing and the bottom of the outer casing. port, the solid material in the outer casing can enter the inner casing through the material slip port; the hot flue gas pipe is inserted from the bottom of the outer casing and extends into the inner casing from below , there is a gap between the hot flue gas pipe and the inner casing; the solid distributor is located at the feed opening and surrounds the outer wall of the hot flue gas pipe, and the solid distributor is provided with A high-pressure gas inlet and a plurality of distributed gas nozzles evenly arranged along the circumferential direction. The distributed gas flows from the high-pressure gas inlet into the solid distributor and is sprayed upward through the distributed gas nozzles.

优选地,所述旋风分离器的气体出口与所述预干燥装置的气体进口连接,将所述旋风分离器中的烟气送入所述预干燥装置中作为烘干污泥的热源;所述预干燥装置中换热后的烟气经烟气出口送入尾气引风机,再从所述尾气引风机排出。Preferably, the gas outlet of the cyclone separator is connected to the gas inlet of the pre-drying device, and the flue gas in the cyclone separator is sent to the pre-drying device as a heat source for drying sludge; The heat-exchanged flue gas in the pre-drying device is sent to the exhaust gas induced draft fan through the flue gas outlet, and then discharged from the exhaust gas induced draft fan.

优选地,所述冷凝器的气体出口与所述热烟炉连接,将所述冷凝器中的不凝燃气送入所述热烟炉作为燃料。Preferably, the gas outlet of the condenser is connected to the hot smoke furnace, and the non-condensable gas in the condenser is sent to the hot smoke furnace as fuel.

本发明实施例还提供了一种污泥热解方法,使用上述技术方案提供的所述污泥热解资源化系统对污泥进行热解处理,包括如下步骤:Embodiments of the present invention also provide a sludge pyrolysis method, using the sludge pyrolysis resource utilization system provided by the above technical solution to perform pyrolysis treatment on sludge, including the following steps:

1. 将含水的污泥送入预干燥装置中进行预干燥;1. Send the water-containing sludge into the pre-drying device for pre-drying;

2. 将预干燥后的污泥送入热解反应器中与固体热载体混合,经热解反应得到高温热解气及包含固体热载体的固体物;2. Send the pre-dried sludge into the pyrolysis reactor and mix it with the solid heat carrier. After the pyrolysis reaction, high-temperature pyrolysis gas and solid matter containing the solid heat carrier are obtained;

3. 将热解反应器中的所述高温热解气送入冷凝器,冷凝后得到液体和不凝燃气;3. Send the high-temperature pyrolysis gas in the pyrolysis reactor to the condenser, and obtain liquid and non-condensable gas after condensation;

4. 将冷凝器中冷凝得到的所述液体在油水分离器中分离出水和油;4. Separate the water and oil from the liquid condensed in the condenser in the oil-water separator;

5. 将热解反应器中的所述固体物送入加热提升管中,所述固体物在加热提升管中被来自热烟炉的烟气加热并提升至进料载体斗中;5. Send the solid matter in the pyrolysis reactor into the heating riser, where the solid matter is heated by the flue gas from the hot smoke furnace and lifted into the feed carrier hopper;

6. 将进料载体斗中的固体热载体送入热解反应器中与所述预干燥后的污泥混合;6. Send the solid heat carrier in the feed carrier hopper into the pyrolysis reactor to mix with the pre-dried sludge;

7. 将进料载体斗中的含尘烟气送入旋风分离器中分离出固体和烟气,将固体作为残渣排出。7. Send the dusty flue gas in the feed carrier hopper to the cyclone separator to separate the solid and flue gas, and discharge the solid as residue.

优选地,将所述步骤3中冷凝器中冷凝后得到的不凝燃气送入所述热烟炉中作为燃料使用。Preferably, the non-condensable gas obtained after condensation in the condenser in step 3 is sent to the hot smoke furnace for use as fuel.

优选地,将所述步骤7中含尘烟气中分离出的烟气送入所述预干燥装置中作为烘干污泥的热源。Preferably, the flue gas separated from the dust-containing flue gas in step 7 is sent to the pre-drying device as a heat source for drying sludge.

本发明实施例的上述技术方案的有益效果为:The beneficial effects of the above technical solutions of the embodiments of the present invention are:

1. 根据污泥的物料和热解特性,采用固体热载体将热量传导给污泥,相比现有技术的间接加热方式,具有热效率高、加热均匀等优点;1. Based on the material and pyrolysis characteristics of the sludge, a solid heat carrier is used to conduct heat to the sludge. Compared with the existing indirect heating method, it has the advantages of high thermal efficiency and uniform heating;

2. 在热解反应器中合理设置螺旋叶和搅拌叶,可实现污泥和热载体充分混合及快速传热,热解反应速率快,系统处理能力强,同时有效解决因污泥搅拌不均带来的结焦问题,实现系统的长期稳定运行;2. Properly setting spiral blades and stirring blades in the pyrolysis reactor can achieve full mixing of sludge and heat carrier and rapid heat transfer. The pyrolysis reaction rate is fast, the system processing capacity is strong, and at the same time, it can effectively solve the problem of uneven sludge mixing. It reduces the coking problem and achieves long-term stable operation of the system;

3. 通过污泥的快速加热和油气快速导出,减少热解产物的二次裂解,实现热解油产率的高产率,最大化的实现污泥资源化利用;3. Through the rapid heating of sludge and the rapid export of oil and gas, the secondary cracking of pyrolysis products is reduced, a high yield of pyrolysis oil is achieved, and the utilization of sludge resources is maximized;

4. 采用污泥预干燥装置,利用余热烟气将污泥中的水分初步脱除,降低热解装置能耗,实现能量分级利用,提升系统能量利用效率。4. Use a sludge pre-drying device to initially remove moisture from the sludge using waste heat flue gas to reduce the energy consumption of the pyrolysis device, achieve graded utilization of energy, and improve the energy utilization efficiency of the system.

附图说明Description of drawings

图1为本发明实施例提供的污泥热解资源化系统的系统图;Figure 1 is a system diagram of a sludge pyrolysis resource utilization system provided by an embodiment of the present invention;

图2为本发明实施例提供的污泥热解资源化系统中热解反应器的结构示意图;Figure 2 is a schematic structural diagram of the pyrolysis reactor in the sludge pyrolysis resource utilization system provided by the embodiment of the present invention;

图3为本发明实施例提供的污泥热解资源化系统中加热提升管的结构示意图;Figure 3 is a schematic structural diagram of the heating riser in the sludge pyrolysis resource utilization system provided by the embodiment of the present invention;

图4为本发明实施例提供的污泥热解方法的步骤流程示意图。Figure 4 is a schematic flow chart of the steps of the sludge pyrolysis method provided by the embodiment of the present invention.

[主要元件符号说明][Explanation of main component symbols]

1-预干燥装置;11-尾气引风机;12-除尘器;1-Pre-drying device; 11-Tail gas induced draft fan; 12-Dust collector;

2-热解反应器;21-反应器筒体;22-旋转轴;23-螺旋叶;231-搅拌叶;24-热载体进口;25-污泥进口;26-固体物出口;27-热解气出口;271-侧排气口;2-pyrolysis reactor; 21-reactor barrel; 22-rotating shaft; 23-spiral blade; 231-stirring blade; 24-heat carrier inlet; 25-sludge inlet; 26-solid matter outlet; 27-heat Degassing outlet; 271-side exhaust port;

31-进料载体斗;32-出料载体斗;31-feed carrier hopper; 32-discharge carrier hopper;

41-出载体螺旋;42-进载体螺旋;41-Outgoing carrier helix; 42-Incoming carrier helix;

5-热烟炉;51-空气配风机;5-Hot smoke stove; 51-Air distribution fan;

6-加热提升管;61-进料段;611-固体进料口;612-热烟气管道;613-外套管;614-内套管;615-溜料口;616-固体分布器;616a-高压气进口;616b-分布气喷嘴;6L-固体物料线;62-扩张段;63-提升段;6-heating riser; 61-feed section; 611-solid feed port; 612-hot flue gas pipe; 613-outer casing; 614-inner casing; 615-feed opening; 616-solid distributor; 616a -High-pressure gas inlet; 616b-distributed gas nozzle; 6L-solid material line; 62-expansion section; 63-lifting section;

71-冷凝器;72-油水分离器;71-Condenser; 72-Oil-water separator;

8-旋风分离器;8-Cyclone separator;

9-排渣器。9-Slag discharger.

具体实施方式Detailed ways

为使本发明要解决的技术问题、技术方案和优点更加清楚,下面将结合附图及具体实施例进行详细描述。In order to make the technical problems, technical solutions and advantages to be solved by the present invention clearer, a detailed description will be given below with reference to the accompanying drawings and specific embodiments.

本发明针对现有污泥热解技术存在的加热不均、热效率低、系统处理能力不足等问题,提供了新型的污泥热解反应系统和热解方法,具有加热均匀、高效低价、易工业化等特点。Aiming at the problems of uneven heating, low thermal efficiency, and insufficient system processing capacity existing in the existing sludge pyrolysis technology, the present invention provides a new sludge pyrolysis reaction system and pyrolysis method, which has the characteristics of uniform heating, high efficiency, low price, and ease of use. industrialization and other characteristics.

为了实现上述技术方案,本发明的实施例提供了一种污泥热解资源化系统,如图1所示为其基本结构,包括预干燥装置1、进料载体斗31、出料载体斗32、热解反应器2、热烟炉5、加热提升管6、冷凝器71、油水分离器72、旋风分离器8和排渣器9,其中:In order to realize the above technical solution, embodiments of the present invention provide a sludge pyrolysis resource utilization system, the basic structure of which is shown in Figure 1, including a pre-drying device 1, a feed carrier hopper 31, and a discharge carrier hopper 32 , Pyrolysis reactor 2, hot smoke furnace 5, heating riser 6, condenser 71, oil-water separator 72, cyclone separator 8 and slag discharger 9, among which:

待处理的污泥原料从预干燥装置1送入系统,先在预干燥装置1中对污泥原料进行预干燥,预干燥后的污泥送入热解反应器2中。The sludge raw materials to be processed are sent into the system from the pre-drying device 1. The sludge raw materials are first pre-dried in the pre-drying device 1, and the pre-dried sludge is sent to the pyrolysis reactor 2.

进料载体斗31位于热解反应器2上方,进料载体斗31中的固体物出口连接热解反应器2,向热解反应器2中送入高温的固体热载体,作为更佳的实施方式,进料载体斗31通过进载体螺旋42将固体热载体输送入热解反应器2中,其中,固体热载体可采用瓷球或石英砂,也可根据需要选用其他材料;污泥和固体热载体在热解反应器2中混合后,由固体热载体向污泥传热,发生热解反应;出料载体斗32位于热解反应器2下方,热解反应器2中的固体物经出料载体斗32送入加热提升管6中,作为更佳的实施方式,出料载体斗32和加热提升管6之间连接出载体螺旋41,由出载体螺旋41将包含固体热载体的固体物运送入加热提升管6;加热提升管6下部连接热烟炉5,热烟炉5可连接空气配风机51注入空气助燃,将热烟炉5中燃气燃烧产生的烟气送入加热提升管6中用于对固体物进行加热提升;加热提升管6上部的出口连接进料载体斗31入口,将固体物和烟气一同送入进料载体斗31中;固体热载体在进料载体斗31、热解反应器2、出料载体斗32和加热提升管6形成循环。The feed carrier hopper 31 is located above the pyrolysis reactor 2. The solid matter outlet in the feed carrier hopper 31 is connected to the pyrolysis reactor 2, and high-temperature solid heat carriers are sent into the pyrolysis reactor 2 as a better implementation. In this way, the feed carrier hopper 31 transports the solid heat carrier into the pyrolysis reactor 2 through the feed carrier screw 42. The solid heat carrier can be porcelain balls or quartz sand, or other materials can be selected as needed; sludge and solids After the heat carrier is mixed in the pyrolysis reactor 2, heat is transferred from the solid heat carrier to the sludge, and a pyrolysis reaction occurs; the discharge carrier hopper 32 is located below the pyrolysis reactor 2, and the solid matter in the pyrolysis reactor 2 passes through The discharge carrier hopper 32 is sent into the heating riser 6. As a better embodiment, a carrier spiral 41 is connected between the discharge carrier hopper 32 and the heating riser 6. The solid heat carrier containing the solid heat carrier is discharged by the discharge carrier spiral 41. The materials are transported into the heating riser 6; the lower part of the heating riser 6 is connected to the hot smoke furnace 5. The hot smoke furnace 5 can be connected to the air distribution fan 51 to inject air to support combustion, and the flue gas generated by the gas combustion in the hot smoke furnace 5 is sent into the heating riser. 6 is used to heat and lift solid matter; the outlet of the upper part of the heating riser 6 is connected to the inlet of the feed carrier hopper 31, and the solid matter and flue gas are sent into the feed carrier hopper 31 together; the solid heat carrier is in the feed carrier hopper 31. The pyrolysis reactor 2, the discharge carrier hopper 32 and the heating riser 6 form a cycle.

热解反应器2中产生的高温热解气送入冷凝器71中,冷凝器71中冷凝产生的液体送入油水分离器72中,在油水分离器72中分离出水和油,可以将水和油外送;冷凝器71中热解气冷凝后剩余的不凝燃气可作为燃料外送,作为更佳的实施方式,可将冷凝器71的气体出口连接热烟炉5,将排出的不凝燃气送入热烟炉5中作为燃气使用。The high-temperature pyrolysis gas generated in the pyrolysis reactor 2 is sent to the condenser 71, and the liquid produced by condensation in the condenser 71 is sent to the oil-water separator 72. Water and oil are separated in the oil-water separator 72, and the water and oil can be separated. Oil is sent out; the non-condensable gas remaining after the pyrolysis gas is condensed in the condenser 71 can be sent out as fuel. As a better implementation, the gas outlet of the condenser 71 can be connected to the hot smoke furnace 5, and the discharged non-condensable gas can be sent out. The gas is sent into the hot smoke furnace 5 for use as gas.

进料载体斗31的气体出口连接旋风分离器8,将含尘烟气送入旋风分离器8中;旋风分离器8中分离出的固体物送入排渣器9,再由排渣器9作为系统残渣排出;旋风分离器8中分离出的烟气可以经必要处理后直接排出,作为更佳的实施方式,如图1所示,也可以将旋风分离器8的气体出口连接预干燥装置1,将烟气导入预干燥装置1中作为烘干污泥的热源,尾气引风机11连接预干燥装置1的烟气出口,将与含水污泥换热后的烟气送入除尘器12处理后排出。The gas outlet of the feed carrier hopper 31 is connected to the cyclone separator 8, and the dust-containing flue gas is sent to the cyclone separator 8; the solid matter separated in the cyclone separator 8 is sent to the slag discharger 9, and then the slag discharger 9 It is discharged as system residue; the flue gas separated in the cyclone separator 8 can be directly discharged after necessary treatment. As a better implementation, as shown in Figure 1, the gas outlet of the cyclone separator 8 can also be connected to a pre-drying device. 1. Introduce the flue gas into the pre-drying device 1 as a heat source for drying sludge. The tail gas induced draft fan 11 is connected to the flue gas outlet of the pre-drying device 1, and the flue gas after exchanging heat with the water-containing sludge is sent to the dust collector 12 for processing. then discharged.

如图2所示为热解反应器2的一个实例,热解反应器2包括反应器筒体21及反应器筒体21上设置的热载体进口24、污泥进口25和热解气出口27,反应器筒体21为上大下小的中空圆台结构,反应器筒体21的中轴位置安装有旋转轴22;旋转轴22上盘绕固定有螺旋叶23,螺旋叶23随旋转轴22转动而搅动;反应器筒体21上端一侧设置有热载体进口24和污泥进口25,对侧设置有热解气出口27,热载体进口24位置高于污泥进口25;反应器筒体21下端侧部还设置有供固体热载体和热解固体产物排出的固体物出口26。Figure 2 shows an example of a pyrolysis reactor 2. The pyrolysis reactor 2 includes a reactor barrel 21 and a heat carrier inlet 24, a sludge inlet 25 and a pyrolysis gas outlet 27 provided on the reactor barrel 21. , the reactor barrel 21 is a hollow truncated cone structure with a large top and a small bottom. A rotating shaft 22 is installed at the central axis of the reactor barrel 21; a spiral blade 23 is coiled and fixed on the rotating shaft 22, and the spiral blade 23 rotates with the rotating shaft 22. And stir; the upper end of the reactor barrel 21 is provided with a heat carrier inlet 24 and a sludge inlet 25, and the opposite side is provided with a pyrolysis gas outlet 27. The heat carrier inlet 24 is positioned higher than the sludge inlet 25; the reactor barrel 21 The lower end side is also provided with a solid matter outlet 26 for discharging solid heat carriers and pyrolysis solid products.

热解反应器2可采取以下设置,作为更佳的实施方式:The pyrolysis reactor 2 can adopt the following settings as a better implementation:

反应器筒体21的侧部立面与下底面的夹角α大于90°,以不超过135°为更佳;反应器筒体21的侧部可设置若干与热解气出口27连通的侧排气口271,侧排气口271数量以三至五个为佳,侧排气口271伸入反应器筒体21内,用于收集内部的热解气并汇集导至热解气出口27排出;可设置侧排气口271为圆形或方形,自反应器筒体21内壁水平伸出4~95mm;The angle α between the side elevation and the lower bottom surface of the reactor barrel 21 is greater than 90°, preferably no more than 135°; the side of the reactor barrel 21 can be provided with several side openings connected to the pyrolysis gas outlet 27 The number of exhaust ports 271 and side exhaust ports 271 is preferably three to five. The side exhaust ports 271 extend into the reactor barrel 21 and are used to collect the internal pyrolysis gas and guide it to the pyrolysis gas outlet 27 Discharge; the side exhaust port 271 can be set to be circular or square, extending horizontally by 4~95mm from the inner wall of the reactor barrel 21;

旋转轴22安装在反应器筒体21的中轴位置,自上而下竖直贯通反应器筒体21;旋转轴22上盘绕固定有螺旋叶23,螺旋叶23可采用焊接方式与旋转轴22固定,当旋转轴22转动时,螺旋叶23叶片以旋转轴22为轴搅动,对反应器筒体21中的生物质进行搅拌推挤;可设置螺旋叶23相邻叶片的间距为300~500mm,螺旋叶23边缘与反应器筒体21内侧壁的间距为5~100mm;为进一步提升搅拌效果,螺旋叶23上沿叶片延伸方向可依次焊接固定多个筋条作为搅拌叶231,筋条为方形或圆形凸起,凸起的高度可设置为50~100mm,相邻筋条之间的间距可设置为200~300mm。The rotating shaft 22 is installed at the central axis of the reactor barrel 21 and runs vertically through the reactor barrel 21 from top to bottom; spiral blades 23 are coiled and fixed on the rotating shaft 22, and the spiral blades 23 can be welded to the rotating shaft 22. Fixed, when the rotating shaft 22 rotates, the spiral blades 23 stir with the rotating shaft 22 as the axis, stirring and pushing the biomass in the reactor barrel 21; the distance between adjacent blades of the spiral blade 23 can be set to 300~500mm. , the distance between the edge of the spiral blade 23 and the inner wall of the reactor barrel 21 is 5~100mm; in order to further improve the mixing effect, a plurality of ribs can be welded and fixed on the spiral blade 23 in sequence along the blade extension direction as the mixing blade 231, the ribs are For square or circular protrusions, the height of the protrusion can be set to 50~100mm, and the spacing between adjacent ribs can be set to 200~300mm.

所述污泥热解资源化系统中,针对固体热载体加热提升需求,加热提升管采用如图3所示的实例,其具体结构与设置为:In the sludge pyrolysis resource utilization system, in response to the heating and lifting requirements of the solid heat carrier, the heating riser adopts the example shown in Figure 3, and its specific structure and settings are:

加热提升管6由下至上依次为进料段61、扩张段62和提升段63,进料段61包括固体进料口611、热烟气管道612、外套管613、内套管614、溜料口615及固体分布器616。固体进料口611设置在外套管613的上侧部;内套管614套设于外套管613内,内套管614下端与外套管613下底之间设置溜料口615,外套管613中的固体物料可通过溜料口615进入内套管614中;热烟气管道612自外套管613底部插入,并从下方伸入内套管614中,热烟气管道612与内套管614间具有间隙;固体分布器616位于溜料口615位置,并环绕在热烟气管道612外壁上,固体分布器616上设置有高压气进口616a及沿周向均匀布置的多个分布气喷嘴616b,分布气从高压气进口616a通入固体分布器616中,并经分布气喷嘴616b向上方喷出。The heating riser 6 is composed of a feed section 61, an expansion section 62 and a lift section 63 from bottom to top. The feed section 61 includes a solid feed port 611, a hot flue gas pipe 612, an outer casing 613, an inner casing 614, and a slide material. Port 615 and solid distributor 616. The solid feed port 611 is provided on the upper side of the outer casing 613; the inner casing 614 is set inside the outer casing 613, and a feed opening 615 is provided between the lower end of the inner casing 614 and the lower bottom of the outer casing 613. The solid material can enter the inner casing 614 through the feed opening 615; the hot flue gas pipe 612 is inserted from the bottom of the outer casing 613 and extends into the inner casing 614 from below. There is a gap; the solid distributor 616 is located at the feed opening 615 and surrounds the outer wall of the hot flue gas pipe 612. The solid distributor 616 is provided with a high-pressure gas inlet 616a and a plurality of distributed gas nozzles 616b evenly arranged along the circumferential direction. The distributed gas flows into the solid distributor 616 from the high-pressure gas inlet 616a, and is sprayed upward through the distributed gas nozzle 616b.

作为更佳的实施方式,固体进料口611位置离外套管613底部距离宜设置为500~1000mm,送入的固体物料堆积形成倾斜的固体物料线6L;内套管614直径为200~800mm,内套管614供热烟气流通,热烟气在内套管614中流动的速度限制在30~75m/s;热烟气管道612直径比内套管614直径小20~50mm,形成热烟气管道612与内套管614之间的间隙,热烟气管道612管口伸入内套管614的长度H为10~50mm;溜料口615高度设置为50~150mm,其溜料速度通过固体分布器616的分布气气速进行调整;固体分布器的分布气采用压缩的空气或氮气,高压气进口616a处的气体压力范围为0.1~0.6Mpa,分布气喷嘴616b的数量为八至十六个,喷嘴可采取圆顶风帽式,将出气速度控制在30~50m/s。As a better implementation, the distance between the position of the solid feed port 611 and the bottom of the outer casing 613 should be set to 500~1000mm, and the fed solid material accumulates to form an inclined solid material line 6L; the diameter of the inner casing 614 is 200~800mm. The inner casing 614 supplies heating flue gas, and the speed of the hot flue gas flowing in the inner casing 614 is limited to 30~75m/s; the diameter of the hot flue gas pipe 612 is 20~50mm smaller than the diameter of the inner casing 614, forming hot flue gas. The gap between the pipe 612 and the inner casing 614, the length H of the hot flue gas pipe 612 pipe mouth extending into the inner casing 614 is 10~50mm; the height of the feed opening 615 is set to 50~150mm, and the feed speed passes through the solid The distribution gas speed of the distributor 616 is adjusted; the distribution gas of the solid distributor is compressed air or nitrogen, the gas pressure range at the high-pressure gas inlet 616a is 0.1~0.6Mpa, and the number of the distribution gas nozzles 616b is eight to sixteen The nozzle can adopt a dome hood type to control the air outlet speed at 30~50m/s.

本发明实施例还提供了一种生物质热解反应方法,使用前述生物质立式热解反应系统处理生物质原料,包括如下步骤:Embodiments of the present invention also provide a biomass pyrolysis reaction method that uses the aforementioned biomass vertical pyrolysis reaction system to process biomass raw materials, including the following steps:

S1. 将含水的污泥送入预干燥装置中进行预干燥;S1. Send the water-containing sludge into the pre-drying device for pre-drying;

S2. 将预干燥后的污泥送入热解反应器中与固体热载体混合,经热解反应得到高温热解气及包含固体热载体的固体物;S2. Send the pre-dried sludge into the pyrolysis reactor to mix with the solid heat carrier, and obtain high-temperature pyrolysis gas and solid matter containing the solid heat carrier through the pyrolysis reaction;

S3. 将热解反应器中的所述高温热解气送入冷凝器,冷凝后得到液体和不凝燃气;S3. Send the high-temperature pyrolysis gas in the pyrolysis reactor to the condenser, and obtain liquid and non-condensable gas after condensation;

S4. 将冷凝器中冷凝得到的所述液体在油水分离器中分离出水和油;S4. Separate the water and oil from the liquid condensed in the condenser in the oil-water separator;

S5. 将热解反应器中的所述固体物送入加热提升管中,所述固体物在加热提升管中被来自热烟炉的烟气加热并提升至进料载体斗中;S5. Send the solid matter in the pyrolysis reactor into the heating riser, where the solid matter is heated by the flue gas from the hot smoke furnace and lifted into the feed carrier hopper;

S6. 将进料载体斗中的固体热载体送入热解反应器中与所述预干燥后的污泥混合;S6. Send the solid heat carrier in the feed carrier hopper into the pyrolysis reactor to mix with the pre-dried sludge;

S7. 将进料载体斗中的含尘烟气送入旋风分离器中分离出固体和烟气,将固体作为残渣排出。S7. Send the dusty flue gas in the feed carrier hopper to the cyclone separator to separate the solid and flue gas, and discharge the solid as residue.

上述步骤更佳的实施方式如下:A better implementation of the above steps is as follows:

步骤S1中,高含水污泥送入预干燥装置进行预干燥时的干燥温度设定为100~200°C;为提高能量利用率,充分利用高温烟气的余热,可将步骤7中旋风分离器从含尘烟气中分离出的烟气送入预干燥装置中作为烘干污泥的热源,该烟气温度控制在200~400°C。In step S1, the drying temperature when the high water content sludge is sent to the pre-drying device for pre-drying is set to 100~200°C; in order to improve energy utilization and make full use of the waste heat of high-temperature flue gas, the cyclone separation in step 7 can be The flue gas separated from the dusty flue gas is sent to the pre-drying device as a heat source for drying sludge. The temperature of the flue gas is controlled at 200~400°C.

步骤S2中,预干燥后的污泥送入热解反应器与固体热载体进行混合,该固体热载体温度控制在600~800°C,根据不同种类污泥的性质,通过调整热解反应器中螺旋叶的转速,可控制污泥在热解反应器中的停留时间为1~10min,使污泥热解产生高温热解气。In step S2, the pre-dried sludge is sent to the pyrolysis reactor for mixing with the solid heat carrier. The temperature of the solid heat carrier is controlled at 600~800°C. According to the properties of different types of sludge, the pyrolysis reactor is adjusted The rotation speed of the middle spiral blade can control the residence time of the sludge in the pyrolysis reactor to 1~10 minutes, so that the sludge can be pyrolyzed to produce high-temperature pyrolysis gas.

步骤S3中,高温热解气送入冷凝装置进行油水冷凝时,冷凝温度为20~50℃,冷凝后得到的不凝燃气可作为产品外送,或直接送入热烟炉中作为燃气使用,不凝燃气在热烟炉燃烧产生高温烟气。In step S3, when the high-temperature pyrolysis gas is sent to the condensation device for oil-water condensation, the condensation temperature is 20~50°C. The non-condensable gas obtained after condensation can be sent out as a product, or directly sent to the hot smoke furnace for use as gas. Non-condensable gas burns in a hot smoke furnace to produce high-temperature flue gas.

步骤S5中,热解反应器排出的包含固体热载体的固体物温度为400~500°C,固体物在加热提升管内被800~1200°C的燃烧烟气加热并提升至进料载体斗中。In step S5, the temperature of the solid matter containing the solid heat carrier discharged from the pyrolysis reactor is 400~500°C. The solid matter is heated by the combustion flue gas of 800~1200°C in the heating riser and lifted into the feed carrier hopper. .

以下是采用上述热解反应系统和热解方法对污泥进行热解的具体实施例:The following are specific examples of pyrolysis of sludge using the above pyrolysis reaction system and pyrolysis method:

以某污泥为例,污泥的主要性质如下表:Taking a certain sludge as an example, the main properties of the sludge are as follows:

项目project 单位unit 数值numerical value 备注Remark 水含量water content %% 79.3079.30 收到基received base 泥含量Mud content %% 20.7020.70 收到基received base

将该高含水污泥送入预干燥装置进行预干燥,干燥温度180°C,进入预干燥装置的高温烟气温度为350°C,出预干燥装置时,污泥的含水率降为21%。预干燥后污泥送入热解反应器与固体热载体进行混合,其中热载体温度700°C。所用的热解反应器夹角α为125°,螺旋叶间距为250mm,螺旋叶上焊接高度为50mm的方型搅拌叶,各搅拌叶间距为150mm,热解反应器侧部设置三个与热解气出口连通的侧排气口,其中螺旋叶与反应器筒体内壁的间距为30mm,侧排气口水平伸入反应器筒体20mm。通过调整热解反应器螺旋转速,使污泥停留时间为6min,热解产生的高温热解气送入冷凝装置进行油水冷凝,冷凝温度为40°C。热解反应器排出的固体物温度为500°C。送入加热提升管内的固体热载体被温度1000°C燃烧烟气加热并提升至进料载体斗,输入热解反应器后与污泥混合。The high water content sludge is sent to the pre-drying device for pre-drying. The drying temperature is 180°C. The high-temperature flue gas temperature entering the pre-drying device is 350°C. When leaving the pre-drying device, the moisture content of the sludge drops to 21%. . After predrying, the sludge is sent to the pyrolysis reactor for mixing with the solid heat carrier, where the temperature of the heat carrier is 700°C. The angle α of the pyrolysis reactor used is 125°, the distance between the spiral blades is 250mm, the spiral blades have square stirring blades with a welding height of 50mm, the spacing between the stirring blades is 150mm, and there are three heat pumps on the side of the pyrolysis reactor. The side exhaust port is connected to the degassing outlet. The distance between the spiral blade and the inner wall of the reactor barrel is 30 mm. The side exhaust port extends horizontally into the reactor barrel by 20 mm. By adjusting the spiral speed of the pyrolysis reactor so that the sludge residence time is 6 minutes, the high-temperature pyrolysis gas generated by pyrolysis is sent to the condensation device for oil-water condensation, and the condensation temperature is 40°C. The temperature of the solids discharged from the pyrolysis reactor is 500°C. The solid heat carrier sent into the heating riser is heated by the combustion flue gas with a temperature of 1000°C and lifted to the feed carrier hopper, where it is input into the pyrolysis reactor and mixed with the sludge.

以上述热解系统的产物为基准,其中:热解油产率为25.3%,热解气产率40.2%,渣产率11.2%,热解水产率23.3%,气体成分以CH4、H2、CO为主,热值高达3750kcal/Nm3Based on the products of the above pyrolysis system, the yield of pyrolysis oil is 25.3%, the yield of pyrolysis gas is 40.2%, the yield of slag is 11.2%, and the yield of pyrolysis water is 23.3%. The gas components are CH 4 and H 2 , CO mainly, with a calorific value as high as 3750kcal/Nm 3 .

对于上述的本发明的实施例,方案中公知的具体结构及特性等常识未作过多描述;各实施例采用递进的方式描述,各实施例中所涉及到的技术特征在彼此之间不构成冲突的前提下可以相互组合,各实施例之间相同相似部分互相参见即可。Regarding the above-mentioned embodiments of the present invention, common knowledge such as the well-known specific structures and characteristics of the solutions are not described too much; each embodiment is described in a progressive manner, and the technical features involved in each embodiment are different from each other. They can be combined with each other if there is a conflict, and the same and similar parts between the various embodiments can be referred to each other.

在本发明的描述中,术语“上”、“下”、“水平”、“内”、“外”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本发明和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,不应理解为对本发明的限制。除非另有明确的规定和限定,术语“相连”、“连接”应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或一体地连接;可以是直接相连,也可以通过中间媒介间接相连,可以是两个元件内部的连通。In the description of the present invention, the orientation or positional relationship indicated by the terms "upper", "lower", "horizontal", "inner", "outer", etc. are based on the orientation or positional relationship shown in the drawings, and are only for convenience. The invention is described and the description is simplified without indicating or implying that the device or element referred to must have a particular orientation, be constructed and operate in a particular orientation and should not be construed as a limitation of the invention. Unless otherwise clearly stated and limited, the terms "connected" and "connected" should be understood in a broad sense. For example, it can be a fixed connection, a detachable connection, or an integral connection; it can be directly connected or through an intermediate connection. The medium is indirectly connected, which can be the internal connection between two components.

以上实施例仅用以说明本发明的技术方案而非对其限制,尽管参照上述实施例对本发明进行了详细的说明,所属领域的普通技术人员依然可以对本发明的具体实施方式进行修改或者等同替换,这些未脱离本发明精神和范围的任何修改或者等同替换,均在申请待批的本发明的权利要求保护范围之内。The above embodiments are only used to illustrate the technical solutions of the present invention but not to limit them. Although the present invention has been described in detail with reference to the above embodiments, those of ordinary skill in the art can still make modifications or equivalent substitutions to the specific embodiments of the present invention. , any modifications or equivalent substitutions that do not depart from the spirit and scope of the invention are within the scope of the claims of the pending invention.

Claims (9)

1. The utility model provides a mud pyrolysis resourceful system, includes predrying unit (1), feed carrier fill (31), ejection of compact carrier fill (32), pyrolysis reactor (2), hot smoke stove (5), heating riser (6), condenser (71), oil-water separator (72), cyclone (8) and scum ware (9), its characterized in that:
the pyrolysis reactor (2) comprises a reactor cylinder body (21) with a hollow round platform structure, the upper part of which is large and the lower part of which is small, and a rotary shaft (22) is arranged at the center axis position of the reactor cylinder body (21); a spiral blade (23) is coiled and fixed on the rotating shaft (22), and the spiral blade (23) rotates along with the rotating shaft (22) to stir;
the pre-drying device (1) pre-dries the sludge raw material, and the pre-dried sludge is sent into the pyrolysis reactor (2); the feeding carrier hopper (31) is positioned above the pyrolysis reactor (2), a solid outlet in the feeding carrier hopper (31) is connected with the pyrolysis reactor (2), and a solid heat carrier is fed into the pyrolysis reactor (2); the sludge and the solid heat carrier are mixed in the pyrolysis reactor (2) to carry out pyrolysis reaction;
the pyrolysis gas in the pyrolysis reactor (2) is sent into the condenser (71), liquid generated by condensation in the condenser (71) is sent into the oil-water separator (72), and water and oil are separated in the oil-water separator (72); the discharging carrier hopper (32) is positioned below the pyrolysis reactor (2), and solid matters in the pyrolysis reactor (2) are sent into the heating riser (6) through the discharging carrier hopper (32); the lower part of the heating riser tube (6) is connected with the hot smoke furnace (5), and flue gas generated by gas combustion in the hot smoke furnace (5) is sent into the heating riser tube (6) for heating and lifting solid matters; an outlet at the upper part of the heating riser (6) is connected with an inlet of the feeding carrier bucket (31) to send solid matters and flue gas into the feeding carrier bucket (31); the gas outlet of the feeding carrier hopper (31) is connected with the cyclone separator (8) and sends dust-containing flue gas into the cyclone separator (8); the solid matters separated in the cyclone separator (8) are sent to the slag extractor (9), and residues are discharged by the slag extractor (9);
the heating riser (6) is from bottom to top in proper order feed section (61), expansion section (62) and hoisting section (63), feed section (61) are including solid feed inlet (611), hot flue gas pipeline (612), outer tube (613), interior sleeve pipe (614), swift current material mouth (615) and solid distributor (616), wherein:
the solid feed inlet (611) is arranged at the upper side part of the outer sleeve (613); the inner sleeve (614) is arranged in the outer sleeve (613), the material sliding opening (615) is arranged between the lower end of the inner sleeve (614) and the lower bottom of the outer sleeve (613), and solid materials in the outer sleeve (613) can enter the inner sleeve (614) through the material sliding opening (615); the hot flue gas pipeline (612) is inserted from the bottom of the outer sleeve (613) and extends into the inner sleeve (614) from below, a gap is reserved between the hot flue gas pipeline (612) and the inner sleeve (614), and the inner sleeve (614) supplies heat and circulates flue gas; the solid distributor (616) is positioned at the position of the material sliding opening (615) and surrounds the outer wall of the hot flue gas pipeline (612), the solid distributor (616) is provided with a high-pressure air inlet (616 a) and a plurality of distribution air nozzles (616 b) which are uniformly distributed along the circumferential direction, and the distribution air is introduced into the solid distributor (616) from the high-pressure air inlet (616 a) and is sprayed upwards through the distribution air nozzles (616 b).
2. The sludge pyrolysis recycling system according to claim 1, wherein a plurality of stirring blades (231) are sequentially fixed on the spiral blades (23) of the pyrolysis reactor (2) along the extending direction of the blades, and the stirring blades (231) are square or round raised ribs.
3. The sludge pyrolysis recycling system according to claim 1, characterized in that the upper end side of the reactor cylinder (21) is provided with the heat carrier inlet (24) and the sludge inlet (25), the opposite side is provided with the pyrolysis gas outlet (27), the heat carrier inlet (24) is positioned higher than the sludge inlet (25), the lower end side of the reactor cylinder (21) is further provided with a solid outlet (26), wherein:
the sludge outlet of the pre-drying device (1) is connected with the sludge inlet (25), and sludge is fed into the pyrolysis reactor (2); the solid outlet of the feeding carrier hopper (31) is connected with the heat carrier inlet (24) and is used for feeding solid heat carriers into the pyrolysis reactor (2); the pyrolysis gas outlet (27) is connected with the inlet of the condenser (71), and pyrolysis gas after pyrolysis reaction is sent into the condenser (71); the solid outlet (26) is connected with the discharging carrier bucket (32) and discharges the solid mixture after the pyrolysis reaction into the discharging carrier bucket (32).
4. A sludge pyrolysis recycling system according to claim 3, characterized in that the pyrolysis gas outlet (27) of the pyrolysis reactor (2) is in communication with a number of side exhaust openings (271), which side exhaust openings (271) extend into the reactor cylinder (21) for collecting the pyrolysis gas inside and leading the collected pyrolysis gas to the pyrolysis gas outlet (27) for discharge.
5. Sludge pyrolysis recycling system according to claim 1, characterized in that the gas outlet of the cyclone separator (8) is connected with the gas inlet of the pre-drying device (1), and the flue gas in the cyclone separator (8) is sent into the pre-drying device (1) as a heat source for drying sludge; and the flue gas after heat exchange in the pre-drying device (1) is sent into a tail gas induced draft fan (11) through a flue gas outlet, and is discharged from the tail gas induced draft fan (11).
6. Sludge pyrolysis reclamation system according to any of claims 1 to 5, characterized in that the gas outlet of the condenser (71) is connected to the hot fume furnace (5) and non-condensable gas in the condenser (71) is fed into the hot fume furnace (5) as fuel.
7. A method for pyrolysis of sludge, characterized in that the sludge is subjected to pyrolysis treatment using the sludge pyrolysis recycling system according to any one of claims 1 to 6, comprising the steps of:
step 1: the sludge containing water is sent into a pre-drying device for pre-drying;
step 2: the sludge after pre-drying is sent into a pyrolysis reactor to be mixed with a solid heat carrier, and pyrolysis reaction is carried out to obtain pyrolysis gas and solid matters containing the solid heat carrier;
step 3: sending the high-temperature pyrolysis gas in the pyrolysis reactor into a condenser, and condensing to obtain liquid and non-condensable gas;
step 4: separating water and oil from the liquid obtained by condensation in the condenser in an oil-water separator;
step 5: feeding the solids in the pyrolysis reactor into a heating riser where the solids are heated by flue gas from a hot flue gas furnace and lifted into a feed carrier hopper;
step 6: feeding the solid heat carrier in the feeding carrier hopper into a pyrolysis reactor to be mixed with the pre-dried sludge;
step 7: and sending the dust-containing flue gas in the feeding carrier hopper into a cyclone separator to separate solids and flue gas, and discharging the solids as residues.
8. The sludge pyrolysis method as claimed in claim 7, wherein the non-condensable gas obtained by condensing in the condenser in the step 3 is fed into the hot smoke furnace to be used as fuel.
9. The sludge pyrolysis method as claimed in claim 7, wherein the flue gas separated from the dust-containing flue gas in step 7 is fed into the pre-drying device as a heat source for drying the sludge.
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