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CN105377416A - Steam explosion methods before gasification - Google Patents

Steam explosion methods before gasification Download PDF

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Publication number
CN105377416A
CN105377416A CN201480027130.2A CN201480027130A CN105377416A CN 105377416 A CN105377416 A CN 105377416A CN 201480027130 A CN201480027130 A CN 201480027130A CN 105377416 A CN105377416 A CN 105377416A
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living beings
steam
biomass
section
pressure
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F·M·费拉罗
J·W·霍曼
R·S·安皮斯基
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Sundrop Fuels Inc
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Sundrop Fuels Inc
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Priority claimed from PCT/US2013/044143 external-priority patent/WO2013191897A1/en
Priority claimed from US14/276,719 external-priority patent/US9447326B2/en
Application filed by Sundrop Fuels Inc filed Critical Sundrop Fuels Inc
Publication of CN105377416A publication Critical patent/CN105377416A/en
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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10KPURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
    • C10K3/00Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide
    • C10K3/02Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment
    • C10K3/04Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment reducing the carbon monoxide content, e.g. water-gas shift [WGS]
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    • C10J3/00Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
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    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0903Feed preparation
    • C10J2300/0906Physical processes, e.g. shredding, comminuting, chopping, sorting
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    • C10JPRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
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    • C10J2300/0916Biomass
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    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0913Carbonaceous raw material
    • C10J2300/0916Biomass
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    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0953Gasifying agents
    • C10J2300/0969Carbon dioxide
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    • C10J2300/00Details of gasification processes
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    • C10J2300/0953Gasifying agents
    • C10J2300/0973Water
    • C10J2300/0976Water as steam
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    • C10J2300/00Details of gasification processes
    • C10J2300/09Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
    • C10J2300/0983Additives
    • C10J2300/0993Inert particles, e.g. as heat exchange medium in a fluidized or moving bed, heat carriers, sand
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    • C10J2300/1246Heating the gasifier by external or indirect heating
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    • C10J2300/00Details of gasification processes
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    • C10J2300/1269Heating the gasifier by radiating device, e.g. radiant tubes
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    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
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    • C10J2300/00Details of gasification processes
    • C10J2300/16Integration of gasification processes with another plant or parts within the plant
    • C10J2300/1603Integration of gasification processes with another plant or parts within the plant with gas treatment
    • C10J2300/1621Compression of synthesis gas
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    • C10J2300/00Details of gasification processes
    • C10J2300/16Integration of gasification processes with another plant or parts within the plant
    • C10J2300/164Integration of gasification processes with another plant or parts within the plant with conversion of synthesis gas
    • C10J2300/1656Conversion of synthesis gas to chemicals
    • C10J2300/1665Conversion of synthesis gas to chemicals to alcohols, e.g. methanol or ethanol
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    • C10J2300/00Details of gasification processes
    • C10J2300/18Details of the gasification process, e.g. loops, autothermal operation
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    • C10J2300/00Details of gasification processes
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    • C10J2300/1853Steam reforming, i.e. injection of steam only
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G OR C10K; LIQUIFIED PETROLEUM GAS; USE OF ADDITIVES TO FUELS OR FIRES; FIRE-LIGHTERS
    • C10L9/00Treating solid fuels to improve their combustion
    • C10L9/08Treating solid fuels to improve their combustion by heat treatments, e.g. calcining
    • C10L9/083Torrefaction
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • 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
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    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
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    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin

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Abstract

An integrated plant that includes a steam explosion process unit and biomass gasifier to generate syngas from biomass is discussed. A steam explosion process unit applies a combination of heat, pressure, and moisture to the biomass to make the biomass into a moist fine particle form. The steam explosion process unit applies steam with a high pressure to heat and pressurize any gases and fluids present inside the biomass to internally blow apart the bulk structure of the biomass via a rapid depressurization of the biomass with the increased moisture content. Those produced moist fine particles of biomass are subsequently fed to a feed section of the biomass gasifier, which reacts the biomass particles in a rapid biomass gasification reaction to produce syngas components.

Description

气化之前的蒸汽爆破方法Steam Explosion Method Before Gasification

相关申请案Related applications

本国际申请主张2014年5月13日提交的标题为“使用气化之前的蒸汽爆破方法的生物质的预处理(PretreatmentofBiomassUsingSteamExplosionMethodsBeforeGasification)”的美国申请第14/276,719号的优先权和权益,所述美国申请主张作为2012年6月22日提交的标题为“使用气化之前的蒸汽爆破方法的生物质的预处理(PretreatmentofBiomassUsingSteamExplosionMethodsBeforeGasification)”的美国非临时申请第13/531,318号的部分延续的优先权和权益。本申请还根据35U.S.C.§119主张2013年5月14日提交的标题为“使用气化之前的蒸汽爆破方法的生物质的预处理(PretreatmentofBiomassUsingSteamExplosionMethodsBeforeGasification)”的美国临时申请第61/823,360号的优先权和权益。本申请还主张作为2013年6月4日提交的标题为“使用气化之前的蒸汽爆破方法的生物质的预处理(PretreatmentofBiomassUsingSteamExplosionMethodsBeforeGasification)”的PCT申请第PCT/US2013/044143号的部分延续的优先权和权益,所述PCT申请是主张上述美国临时申请第61/823,360号和美国非临时申请第13/531,318号的优先权和权益的国际申请;所有上述申请在此以引用的方式并入。This international application claims priority and benefit to U.S. Application No. 14/276,719, filed May 13, 2014, entitled "Pretreatment of Biomass Using Steam Explosion Methods Before Gasification," said U.S. Application Claims Priority and Benefit in Part of U.S. Nonprovisional Application Serial No. 13/531,318, filed June 22, 2012, entitled "Pretreatment of Biomass Using Steam Explosion Methods Before Gasification" . This application also claims priority under 35 U.S.C. §119 to U.S. Provisional Application No. 61/823,360, filed May 14, 2013, entitled "Pretreatment of Biomass Using Steam Explosion Methods Before Gasification" rights and interests. This application also claims priority as a continuation-in-part of PCT Application No. PCT/US2013/044143, filed June 4, 2013, entitled "Pretreatment of Biomass Using Steam Explosion Methods Before Gasification" and benefit, said PCT application is an international application claiming priority to and benefit of the aforementioned U.S. Provisional Application No. 61/823,360 and U.S. Nonprovisional Application No. 13/531,318; all of which are hereby incorporated by reference.

技术领域technical field

本设计大体上涉及使用蒸汽爆破方法作为气化或燃烧之前的预处理的生物质的处理。在实施例中,本设计具体来说涉及一种集成设备,其使用此生物质以从所述生物质产生液体燃料,或将所述生物质转换成致密化形式以促进经济地传输到设施以用于进一步处理为液体燃料、热量/电力、动物饲料、床上用品或化学制品。The present design generally involves the treatment of biomass using a steam explosion method as a pretreatment prior to gasification or combustion. In an embodiment, the design specifically relates to an integrated plant that uses this biomass to produce liquid fuels from the biomass, or converts the biomass to a densified form to facilitate economical transport to a facility for use in For further processing into liquid fuels, heat/electricity, animal feed, bedding or chemicals.

背景技术Background technique

最初构想的技术是用干燥的木屑制作中等密度的纤维板。其它过程要求磨削木屑、使切屑干燥、再磨削切屑、使纤维保湿、使纤维致密化、然后使木屑致密化(例如呈颗粒的形式)的多个步骤。这些过程复杂、需要使用大量资金并需要大量能源。一些其它的典型过程需要使生物质切屑干燥,然后将切屑磨削至极小尺寸随后将它们发送至后续的加热/处理单元。此干燥和磨削花费大量的能源和资金成本。这些过程产生小纤维但其大小却是由蒸汽爆破过程(SEP)产生的细颗粒的大小的许多倍。使用SEP过程的先前工业希望维持构成生物质的纤维的完整性以及纤维强度;并且因此具有未经受如在蒸汽爆破单元中的苛刻条件的较长碎片。同样,未应用生物质的额外机械搅拌,因为这将进一步减小纤维长度和完整性两者。The technique originally conceived was to create medium-density fiberboard from dried wood chips. Other processes require multiple steps of grinding the chips, drying the chips, regrinding the chips, moisturizing the fibers, densifying the fibers, and then densifying the chips (eg, in the form of pellets). These processes are complex, capital-intensive, and energy-intensive. Some other typical processes require drying the biomass chips, then grinding the chips to a very small size before sending them to a subsequent heating/processing unit. This drying and grinding incurs substantial energy and capital costs. These processes produce small fibers but many times the size of the fine particles produced by the steam explosion process (SEP). Previous industries using the SEP process wished to maintain the integrity of the fibers making up the biomass as well as fiber strength; and thus had longer fragments that were not subjected to the harsh conditions as in a steam explosion unit. Also, no additional mechanical agitation of the biomass was applied as this would further reduce both fiber length and integrity.

发明内容Contents of the invention

一种集成设备,其包含蒸汽爆破单元和生物质气化炉以从生物质中产生合成气。蒸汽爆破单元将热量、压力和水分的组合应用到生物质以使生物质成为潮湿的细颗粒形式。蒸汽爆破单元应用具有高压的蒸汽以对生物质内部存在的任何气体和流体进行加热和加压。其中在至两段或更多段的出口孔处,经加压生物质的整体结构在内部被分裂以经由具有提高的水分含量的生物质的快速降压而在内部分裂。所产生的那些生物质的潮湿的细颗粒随后被馈送到生物质气化炉的进给区,其以快速生物质气化反应与生物质颗粒发生反应以产生合成气组分。蒸汽爆破单元的蒸汽爆破段耦合到精炼段,精炼段具有一个或多个刀片,其经配置以在生物质通过孔口离开蒸汽爆破段到吹洗管线之前机械地搅拌生物质。An integrated plant comprising a steam explosion unit and a biomass gasifier to produce syngas from biomass. A steam explosion unit applies a combination of heat, pressure and moisture to the biomass to bring the biomass into a moist fine particle form. A steam explosion unit applies steam at high pressure to heat and pressurize any gases and fluids present inside the biomass. Wherein at the exit holes to two or more stages the monolithic structure of the pressurized biomass is internally disintegrated to be internally disintegrated via rapid depressurization of the biomass with increased moisture content. The moist fine particles of those biomass produced are then fed to the feed zone of the biomass gasifier, which reacts with the biomass particles in a fast biomass gasification reaction to produce syngas components. The steam explosion section of the steam explosion unit is coupled to a refining section having one or more blades configured to mechanically agitate the biomass before it exits the steam explosion section through an orifice to a purge line.

附图说明Description of drawings

多个图式涉及本设计的实例实施例。Several figures relate to example embodiments of the present design.

图1A和1B示出了蒸汽爆破单元的实施例的流动示意图,所述蒸汽爆破单元具有用以接收生物质用作原料的输入腔、两个或更多个蒸汽供应输入端、以及用以预处理生物质以用于后续供应到生物质气化炉的两段或更多段。Figures 1A and 1B show a flow schematic diagram of an embodiment of a steam explosion unit having an input chamber to receive biomass as a feedstock, two or more steam supply inputs, and a The biomass is processed for subsequent supply to two or more stages of the biomass gasifier.

图2示出了用以从生物质中产生合成气并且从合成气中产生液体燃料制品的集成设备的流程图的实施例。Figure 2 shows an embodiment of a flow diagram of an integrated plant to produce syngas from biomass and liquid fuel products from the syngas.

图3-1到3-4示出了用于示例性生物质气化炉的替代配置。Figures 3-1 through 3-4 illustrate alternative configurations for an exemplary biomass gasifier.

图4A到图4C示出了具有通过木质素围绕并粘结在一起的纤维素纤维的纤维束的实例生物质切屑的不同放大水平。4A-4C show different magnification levels of example biomass chips having fiber bundles of cellulose fibers surrounded and bonded together by lignin.

图4D示出了爆破成生物质细颗粒的实例生物质切屑。Figure 4D shows example biomass chips exploded into fine particles of biomass.

图4E示出了具有被磨损的或部分地分离成个别纤维的一束纤维的生物质切屑。Figure 4E shows a biomass chip with a bundle of fibers abraded or partially separated into individual fibers.

图5示出了经配置以产生包含合成气体产物的化学制品的辐射热化学反应器的实施例的流动示意图。5 shows a flow schematic diagram of an embodiment of a radiant thermochemical reactor configured to produce chemicals comprising synthesis gas products.

虽然本设计能有各种修改和替代形式,但是已经在图式中借助于实例示出了其特定实施例并将在本文中详细地描述。本设计应理解成不限于所揭示的具体形式,而是相反,意图涵盖属于本设计的精神和范围的所有修改、等效物和替代方案。While the design is capable of various modifications and alternative forms, specific embodiments thereof have been shown by way of example in the drawings and will be described herein in detail. The design should be understood not to be limited to the particular forms disclosed, but on the contrary, the intention is to cover all modifications, equivalents, and alternatives falling within the spirit and scope of the design.

具体实施方式detailed description

在以下描述中,阐述许多特定细节,例如特定化学制品、附名组分、连接、热源类型等的实例,以便提供对本发明设计的透彻理解。然而,所属领域的技术人员将显而易见可在不具有这些特定细节的情况下实践本发明设计。在其它情况下,并未详细地但实际上在方块图中描述了熟知的组件或方法以便避免不必要地混淆本发明设计。因此,所阐述的特定细节仅是示例性的。特定细节可以不同于并且仍然预期在本发明设计的精神和范围内。In the following description, numerous specific details are set forth, such as examples of specific chemicals, named components, connections, heat source types, etc., in order to provide a thorough understanding of the invention's design. It will be apparent, however, to one skilled in the art that the inventive design may be practiced without these specific details. In other instances, well-known components or methods have not been described in detail, but rather in block diagrams in order to avoid unnecessarily obscuring the inventive design. Accordingly, the specific details set forth are examples only. Specific details may be varied and still be contemplated within the spirit and scope of the present design.

一般来说,描述用于生物质的预处理的多个实例过程和与生物质的预处理相关联的装置。以下图式和文本描述使用生物质的预处理的集成设备的各种实例实施方案。在实施例中,集成设备含有至少蒸汽爆破单元和生物质气化炉以从生物质中产生合成气。蒸汽爆破单元可以具有用以接收生物质用作原料的一个或多个输入腔、一个或多个蒸汽供应输入端、以及用以预处理生物质以使得生物质颗粒用于后续供应到生物质气化炉的两段或更多段。所述段使用应用到生物质的热量、压力和水分的组合以使生物质成为潮湿的细颗粒形式。通过应用来自第一蒸汽供应输入端的蒸汽以开始降低在木质素与来自生物质的纤维素纤维的半纤维素之间的粘结并提高接收到的生物质的水分含量,蒸汽爆破过程至少部分地分解接收到的生物质的整体结构。在最后一段中,应用来自第二蒸汽供应输入端的至少大气压力十四倍的蒸汽对生物质内部存在的任何气体和流体进行加热和加压。其中在来自两段或更多段的出口孔处,在内部分裂经加压生物质的整体结构。经由具有提高的水分含量和降低的粘结性的生物质的快速降压分裂生物质的整体结构。从所述段中产生为潮湿的细颗粒形式的生物质可以具有例如小于70微米厚且小于500微米长的平均尺寸。所产生的那些潮湿的生物质细颗粒随后被馈送到生物质气化炉的进给区。生物质气化炉具有反应器容器,其经配置以使潮湿的细颗粒形式的生物质起反应,所述潮湿的细颗粒形式的生物质归因于通过蒸汽爆破单元的分裂而相比于输入腔中的接收到的生物质切屑具有增大的表面积和减小的颗粒大小。生物质气化炉具有第三蒸汽供应输入端和一个或多个加热器,并且在存在蒸汽的情况下,呈细颗粒形式的生物质在反应器容器中在0.1秒到300.0秒之间的滞留时间内以快速生物质气化反应起反应从而产生至少合成气组分,包含氢气(H2)和一氧化碳(CO)。In general, a number of example processes for pretreatment of biomass and devices associated with pretreatment of biomass are described. The following figures and text describe various example embodiments of an integrated plant using pretreatment of biomass. In an embodiment, the integrated plant contains at least a steam explosion unit and a biomass gasifier to generate syngas from biomass. The steam explosion unit may have one or more input chambers to receive biomass as feedstock, one or more steam supply inputs, and to pre-treat the biomass for subsequent supply to the biomass gas Two or more stages of a furnace. The stage uses a combination of heat, pressure and moisture applied to the biomass to bring the biomass into a moist fine particle form. The steam explosion process is at least partially achieved by applying steam from the first steam supply input to begin reducing the bond between the lignin and the hemicellulose from the cellulose fibers of the biomass and increasing the moisture content of the received biomass Break down the overall structure of the received biomass. In the final stage, any gases and fluids present inside the biomass are heated and pressurized using steam at least fourteen times atmospheric pressure from the second steam supply input. Wherein the monolithic structure of the pressurized biomass is split internally at the exit holes from two or more stages. Disruption of the overall structure of the biomass via rapid depressurization of the biomass with increased moisture content and reduced cohesiveness. The biomass produced in wet fine particle form from the segments may have an average size, for example, less than 70 microns thick and less than 500 microns long. Those moist biomass fines produced are then fed to the feed zone of the biomass gasifier. The biomass gasifier has a reactor vessel configured to react moist fine-grained biomass that is due to disintegration by the steam explosion unit compared to the input The received biomass chips in the cavity have increased surface area and reduced particle size. A biomass gasifier having a third steam supply input and one or more heaters and, in the presence of steam, a residence time of biomass in the form of fine particles in the reactor vessel between 0.1 seconds and 300.0 seconds React in a fast biomass gasification reaction over time to produce at least syngas components, including hydrogen (H2) and carbon monoxide (CO).

可能的生物质气化炉实施方案具有高温蒸汽供应输入端和一个或多个加热器,例如气体燃烧器或蓄热式加热器。在存在蒸汽的情况下,通过蒸汽爆破单元分解的生物质颗粒在生物质气化炉中的反应器容器中在少于一秒的滞留时间内在高于700摄氏度的温度下以快速生物质气化反应起反应从而形成合成气组分,包含氢气(H2)和一氧化碳(CO),所述合成气组分被馈送到甲醇(CH30H)合成反应器。所属领域的技术人员将了解在此说明性文档内的下文论述的设计的许多部分和方面可以用作独立概念或彼此结合使用。Possible biomass gasifier embodiments have a high temperature steam supply input and one or more heaters, such as gas burners or regenerative heaters. In the presence of steam, the biomass particles decomposed by the steam explosion unit are gasified as fast biomass at temperatures above 700 degrees Celsius with a residence time of less than one second in the reactor vessel in the biomass gasifier The reaction reacts to form a syngas component, comprising hydrogen (H2) and carbon monoxide (CO), which is fed to a methanol (CH30H) synthesis reactor. Those skilled in the art will appreciate that many parts and aspects of the designs discussed below within this illustrative document can be used as stand-alone concepts or in conjunction with each other.

图1A和1B示出了蒸汽爆破单元的实施例的流动示意图,所述蒸汽爆破单元具有用以接收生物质用作原料的输入腔、两个或更多个蒸汽供应输入端、以及用以预处理生物质以用于后续供应到生物质气化炉的两段或更多段。Figures 1A and 1B show a flow schematic diagram of an embodiment of a steam explosion unit having an input chamber to receive biomass as a feedstock, two or more steam supply inputs, and a The biomass is processed for subsequent supply to two or more stages of the biomass gasifier.

在不进行额外干燥的情况下,进入的呈切屑形式的生物质中的含水量可以为在留在外部的生物质的15%到60%的范围内变化。可以通过与一些过滤器配合的削片机单元104产生生物质切屑,所述过滤器具有用以形成小于约一英寸且平均来说约0.5英寸平均长度和0.25英寸平均厚度的切屑的尺寸。(见例如图4a,其示出来自一块生物质453的生物质切屑451)生物质削片机单元104可以含有用以切击并切削生物质的四个或更多个刀片。生物质块的进给速度、刀片的速度、刀的突起距离以及刀角可以全部用以控制切屑大小。接着筛选切屑并且重新切削过大的那些切屑。可掺合来自不同源或木材种类的切屑以增强某些属性。可以使磁体或其它扫描仪经过以检测并移除杂质。在蒸汽爆破单元108中的热分解段中在输送机上或可能地置于压力容器中来馈送生物质切屑以开始使用初始低压饱和蒸汽分解、水化处理/湿润以及软化生物质切屑。低压饱和蒸汽可以在100摄氏度下。系统还可以在此位置注入一些助流剂(例如,来自生物质气化炉114的再循环炉灰)以防止被生物质切屑阻塞和堵塞。Without additional drying, the moisture content in the incoming biomass in the form of chips can range from 15% to 60% of the biomass remaining outside. Biomass chips may be produced by a chipper unit 104 in conjunction with filters sized to form chips that are less than about one inch and on average about 0.5 inches in average length and 0.25 inches in average thickness. (See eg Figure 4a which shows biomass chips 451 from a block of biomass 453) The biomass chipper unit 104 may contain four or more blades to chip and cut the biomass. The feed rate of the biomass piece, the speed of the blade, the protrusion distance of the knife, and the angle of the knife can all be used to control the chip size. The chips are then screened and those chips that are too large are recut. Chips from different sources or wood species can be blended to enhance certain properties. A magnet or other scanner can be passed to detect and remove impurities. The biomass chips are fed in the thermal decomposition section in the steam explosion unit 108 on a conveyor or possibly in a pressure vessel to start decomposition, hydration/wetting and softening of the biomass chips using initial low pressure saturated steam. Low-pressure saturated steam can be at 100 degrees Celsius. The system may also inject some flow aid at this location (eg, recycled ash from the biomass gasifier 114 ) to prevent clogging and clogging with biomass cuttings.

削片机单元104可以馈送并且蒸汽爆破单元108经配置以接收两个或更多个类型的生物质原料,其中不同类型的生物质包含1)软木、2)硬木、3)草、4)植物壳以及5)任何组合,其在蒸汽爆破单元108内经掺合并蒸汽爆破处理为均质化经焙烧原料,随后被收集并接着馈送到生物质气化炉114。蒸汽爆破单元108、干燥器112和生物质气化炉114设计为灵活地进给,经由至少控制产生自蒸汽爆破段和干燥器112的生物质颗粒的颗粒大小而不改变进给供应设备的物理设计或生物质气化炉114的物理设计。干燥器112可以是快速干燥器、转鼓干燥器、桨式干燥器、空气干燥器或类似此类装置。The chipper unit 104 may feed and the steam explosion unit 108 is configured to receive two or more types of biomass feedstock, where the different types of biomass include 1) softwood, 2) hardwood, 3) grass, 4) vegetation shell and 5) any combination which is blended and steam exploded in the steam explosion unit 108 into a homogenized torrefied feedstock which is then collected and then fed to the biomass gasifier 114 . The steam explosion unit 108, dryer 112 and biomass gasifier 114 are designed to be fed flexibly by at least controlling the particle size of the biomass particles produced from the steam explosion section and dryer 112 without changing the physical nature of the feed supply equipment. Design or physical design of the biomass gasifier 114. Dryer 112 may be a flash dryer, drum dryer, paddle dryer, air dryer, or similar such device.

如所论述,磁力过滤器和空气清洁过滤器系统可以耦合到热水化处理段以确保呈切屑形式的生物质在进入热水化处理段之前去除了金属碎片和大石块。磁力过滤器和空气清洁过滤器系统防止任何金属碎片和/或大石块堵塞包含排出出口的蒸汽爆破单元的部分。空气清洁过滤器系统帮助丢弃实际上大石块以及轻质沙。应注意,形成蒸汽爆破段的排出出口的孔口可以是例如0.25到0.375英寸。As discussed, a magnetic filter and air cleaning filter system can be coupled to the hydrothermal treatment section to ensure that the biomass in the form of shavings is free of metal debris and large rocks before entering the hydrohydration treatment section. The magnetic filter and air cleaning filter system prevents any metal debris and/or large rocks from clogging the portion of the steam explosion unit containing the discharge outlet. The air cleaning filter system helps discard virtually large rocks as well as light sand. It should be noted that the orifice forming the discharge outlet of the steam explosion section may be, for example, 0.25 to 0.375 inches.

蒸汽爆破单元108具有用以接收生物质用作原料的输入腔、一个或多个蒸汽供应输入端、以及用以预处理生物质以用于后续供应到生物质气化炉114的两段或更多段。所述段使用应用到生物质的热量、压力和水分的组合以使生物质成为潮湿的细颗粒形式。通过应用来自低压蒸汽供应输入端的蒸汽以开始降低在木质素与来自生物质的纤维素纤维的半纤维素之间的粘结并提高接收到的生物质的水分含量,蒸汽爆破过程至少部分地分解接收到的生物质的整体结构。(见例如图4B,其示出具有通过木质素围绕并粘结在一起的纤维素纤维的纤维束的生物质切屑)在最后一段中,应用来自高压蒸汽供应端的至少大气压力十四倍的蒸汽对生物质内部存在的任何气体和流体进行加热和加压,以在内部经由具有提高的水分含量和降低的粘结性的生物质的快速降压分裂接收到的生物质的整体结构。The steam explosion unit 108 has an input chamber to receive biomass as a feedstock, one or more steam supply inputs, and two or more stages to pretreat the biomass for subsequent supply to the biomass gasifier 114. Multi-segment. The stage uses a combination of heat, pressure and moisture applied to the biomass to bring the biomass into a moist fine particle form. The steam explosion process is at least partially broken down by applying steam from the input of a low pressure steam supply to start reducing the bond between the lignin and the hemicellulose from the cellulose fibers of the biomass and increasing the moisture content of the received biomass The overall structure of the received biomass. (See e.g. Figure 4B which shows biomass chips with fiber bundles of cellulose fibers surrounded and bonded together by lignin) In the last stage, steam at least fourteen times atmospheric pressure is applied from the high pressure steam supply Any gases and fluids present inside the biomass are heated and pressurized to break down the overall structure of the received biomass internally via rapid depressurization of the biomass with increased moisture content and reduced cohesiveness.

在实施例中,蒸汽爆破单元108的两段或更多段包含至少热水化处理段和蒸汽爆破段。In an embodiment, the two or more stages of the steam explosion unit 108 comprise at least a hydrohydration treatment stage and a steam explosion stage.

热水化处理段具有用以接收生物质的切屑的输入腔以及将低压饱和蒸汽应用到含有生物质切屑的容器中的低压蒸汽供应输入端。热水化处理段经配置以接收呈切屑形式的生物质,包含叶子、针叶、茎皮以及木材。热水化处理段在高于木质素的玻璃化转变点的温度下将低压蒸气应用到生物质,以便软化并提高生物质的水分含量,因此在蒸汽爆破段中生物质的纤维素纤维可以简单地自呈切屑形式的生物质在内部分裂。在实施例中,使用蒸汽将生物质切屑加热到高于60℃。低压蒸汽供应输入端在大约常压PSI的压力下在高于60摄氏度但低于145摄氏度的高温下将低压饱和蒸汽应用到含有生物质切屑的容器中,从而开始分解、水化处理并软化接收到的呈切屑形式的生物质。低压供应输入端可以由战略上围绕容器放置的若干喷嘴构成。一组温度传感器对接收到的生物质切屑的高温提供反馈。控制系统经配置以保持生物质切屑在热水化处理段中停留8到20分钟的滞留时间,所述滞留时间足够长以在生物质移出到蒸汽爆破段之前用水分浸透生物质切屑。对于来自树的树干的木块存在更短的滞留时间,且对于树枝、针叶等存在更长的滞留时间。The hydrothermal treatment section has an input chamber to receive cuttings of biomass and a low pressure steam supply input for applying low pressure saturated steam to a vessel containing cuttings of biomass. The hydrothermal treatment section is configured to receive biomass in the form of cuttings, including leaves, needles, bark, and wood. The hydrohydrolysis stage applies low-pressure steam to the biomass at a temperature above the glass transition point of lignin in order to soften and increase the moisture content of the biomass so that in the steam explosion stage the cellulose fibers of the biomass can simply self- Biomass in the form of chips breaks down internally. In an embodiment, steam is used to heat the biomass chips to above 60°C. The low pressure steam supply input applies low pressure saturated steam to the vessel containing the biomass cuttings at a pressure of about atmospheric PSI at an elevated temperature above 60°C but below 145°C to initiate decomposition, hydration and softening of the receiving biomass in the form of shavings. The low pressure supply input can consist of several nozzles strategically placed around the vessel. A set of temperature sensors provides feedback on the high temperature of the incoming biomass chips. The control system is configured to maintain the biomass cuttings in the hydrothermal treatment section for a residence time of 8 to 20 minutes long enough to saturate the biomass cuttings with moisture before the biomass moves out to the steam explosion section. There is a shorter residence time for pieces of wood from the trunk of a tree and longer residence times for twigs, needles, etc.

热水化处理段可能经由螺旋进给系统将已经过软化且水分含量提高的生物质切屑馈送到蒸汽爆破段。控制系统将蒸汽爆破段的压力维持在热水化处理段中存在的压力的10到30倍并且维持在高温下,例如160到270℃的温度,优选地,190℃到220℃。压力可以在180到450磅/平方英寸(PSI)下(优选地,300PSI)。蒸汽爆破段进一步将生物质的水分含量升高到按重量计至少40%,并且优选地,按重量计50%到60%的水分含量。按重量计的水分百分比可以是水的重量除以由生物质切屑加上水重量构成的总重量。在蒸汽爆破段中,经软化且含水的生物质切屑暴露于高温和高压蒸汽中持续3分钟到15分钟的充分时间段,以在部分中空的纤维素纤维和生物质材料的整体结构中的其它多孔区域内部形成高压蒸汽。(见例如图4C,其示出具有通过木质素围绕并粘结在一起的纤维素纤维的纤维束但是在放大时具有许多多孔区域的生物质切屑。)The hydrothermal treatment section feeds biomass chips, which have been softened and have increased moisture content, to the steam explosion section, possibly via a screw feed system. The control system maintains the pressure of the steam explosion section at 10 to 30 times the pressure present in the hydrohydration treatment section and at an elevated temperature, eg a temperature of 160 to 270°C, preferably 190°C to 220°C. The pressure may be at 180 to 450 pounds per square inch (PSI) (preferably, 300 PSI). The steam explosion stage further increases the moisture content of the biomass to at least 40% by weight, and preferably, a moisture content of 50% to 60% by weight. The percent moisture by weight may be the weight of water divided by the total weight of biomass chips plus the weight of water. In the steam explosion stage, the softened and hydrated biomass chips are exposed to high temperature and high pressure steam for a sufficient period of 3 minutes to 15 minutes to destroy other components in the partially hollow cellulosic fibers and the overall structure of the biomass material. High pressure steam is formed inside the porous region. (See, e.g., Figure 4C, which shows a biomass chip with fiber bundles of cellulose fibers surrounded and bonded together by lignin, but with many porous regions when zoomed in.)

在热水化处理段之后,呈切屑形式的经软化生物质经过1)挤压和2)压缩的任何组合成为插塞形式,其接着被馈送到连续式螺旋输送机系统。连续式螺旋输送机系统将呈插塞形式的生物质移动到蒸汽爆破段中。连续式螺旋输送机系统使用呈插塞形式的生物质防止来自在蒸汽爆破段中存在的高压蒸汽的回爆的反压影响热水化处理段。可以使用其它方法,例如1)止回阀和2)分段移动生物质,其中每段可通过打开和关闭机构分离。After the hydrothermal treatment stage, the softened biomass in the form of chips undergoes any combination of 1) extrusion and 2) compression into plug form, which is then fed to a continuous screw conveyor system. A continuous screw conveyor system moves the biomass in the form of a plug into the steam explosion section. The continuous screw conveyor system uses the biomass in the form of a plug to prevent the back pressure from the back explosion of the high pressure steam present in the steam explosion section from affecting the hydrothermal treatment section. Other methods can be used such as 1) check valves and 2) moving biomass in segments where each segment can be separated by an opening and closing mechanism.

蒸汽爆破段可以在高达850psi下操作但是优选地保持低于450psi。一组传感器可以检测操作压力。插塞式螺旋进给机沿着蒸汽爆破段传送切屑。高压蒸汽被引入到插塞式螺旋进给机在称为蒸汽混合输送机的区段中。高压供应输入端可以由战略上围绕蒸汽混合输送机放置的若干喷嘴构成。经由插塞式螺旋进给机精确地控制通过蒸汽爆破段馈送的生物质切屑材料的比率。通过控制系统单独地控制蒸汽爆破段内的滞留时间。在蒸汽爆破段中,呈插塞形式的生物质暴露于来自高压蒸汽输入端的至少160摄氏度和160PSI的高温和高压蒸汽中持续5分钟(并且优选地,大约10分钟),直到水分渗透生物质的整体结构的多孔部分并且生物质中的所有流体和气体上升到高压。在实施例中,蒸汽爆破段具有一组温度和压力传感器以及控制系统,其中生物质暴露于来自第二蒸汽输入端的至少188摄氏度和160PSI的高温和高压蒸汽中持续5分钟到20分钟之间,直到水分渗透生物质的整体结构的多孔部分。The steam explosion section can operate at up to 850 psi but is preferably kept below 450 psi. A set of sensors detects the operating pressure. A plug-type screw feeder conveys chips along the steam explosion section. High pressure steam is introduced into the plug screw feeder in a section called the steam mixing conveyor. The high pressure supply input can consist of several nozzles strategically placed around the steam mixing conveyor. The ratio of biomass chip material fed through the steam explosion section is precisely controlled via a plug screw feeder. The residence time in the steam explosion section is individually controlled by the control system. In the steam explosion section, the biomass in the form of a plug is exposed to high temperature and high pressure steam of at least 160 degrees Celsius and 160 PSI from the high pressure steam input for 5 minutes (and preferably, about 10 minutes) until moisture penetrates the biomass The porous part of the monolith and all fluids and gases in the biomass rise to high pressure. In an embodiment, the steam explosion section has a set of temperature and pressure sensors and a control system, wherein the biomass is exposed to high temperature and high pressure steam of at least 188 degrees Celsius and 160 PSI from a second steam input for between 5 minutes and 20 minutes, Until moisture penetrates the porous part of the overall structure of the biomass.

如所论述,当系统在生物质切屑中具有一定水平的湿度/水分以提供爆破源时蒸汽爆破过程最佳地作用。因此通常,当在蒸汽爆破反应器中时切屑的水分大体上为按重量计至少50%到55%。在蒸汽爆破单元108的蒸汽爆破段中,在含有具有经软化木质素的生物质切屑的室中,压力和温度升高到比热水化处理段中具有生物质切屑的容器的操作环境高至少二十度的升高的温度以及比室中的常压高十四倍的升高的压力,但是具有比热水化处理段中设置的时间段更短的持续时间。As discussed, the steam explosion process works best when the system has a certain level of humidity/moisture in the biomass cuttings to provide a source of explosion. Typically, therefore, the moisture of the chips when in the steam explosion reactor is generally at least 50% to 55% by weight. In the steam explosion section of the steam explosion unit 108, in the chamber containing the biomass chips with softened lignin, the pressure and temperature are raised to at least at least An elevated temperature of twenty degrees and an elevated pressure fourteen times higher than the normal pressure in the chamber, but with a shorter duration than the time period set in the hydrohydration treatment stage.

连续式螺旋输送机系统将呈插塞形式的生物质通过蒸汽爆破段馈送到精炼段。蒸汽爆破段耦合到精炼段,精炼段具有一个或多个刀片,其经配置以在经加压生物质通过出口孔离开蒸汽爆破段到维持在低于蒸汽爆破段内压力的三分之一的压力下的吹洗管线之前机械地搅拌经加压生物质以便在内部分裂经加压生物质。在精炼段中的机械搅拌经配置以使得呈颗粒形式的所得生物质具有生物质颗粒的平均尺寸的更一致的大小分布。精炼段的刀片机械地搅拌经加压且湿润的生物质并且将搅拌后的生物质送到孔口出口。A continuous screw conveyor system feeds the biomass in plug form through the steam explosion section to the refining section. The steam explosion section is coupled to a refining section having one or more blades configured to maintain a pressure below one-third of the pressure within the steam explosion section after the pressurized biomass exits the steam explosion section through an outlet hole. The pressurized biomass is mechanically agitated prior to the purge line under pressure in order to break down the pressurized biomass internally. The mechanical agitation in the refining section is configured so that the resulting biomass in particle form has a more consistent size distribution of the average size of the biomass particles. The blades of the refining section mechanically agitate the pressurized and wetted biomass and send the agitated biomass to the orifice outlet.

在实施例中,小开口形成出口并且进入维持在大约4到10巴的压力下的管或其它容器区域中,并且在高压下的任何内部流体或气体膨胀以在内部分裂生物质。在一些情况下,来自蒸汽爆破反应器中的高压的压降一直向下至大气压力。在任一情况下,在管中或在蒸汽爆破段中的出口与旋流器除水段之间的其它容器中发生的较大压降快速地下降。在实施例中,快速地进行压降,方法是通过将在160到450PSI之间的生物质的整体结构伸入在显著减压(例如4到10巴)下的管中,以引起在压力下降后或归因于在压力下降低于其蒸气压后液体水“闪蒸”成蒸气而导致的内部“爆破”蒸汽快速膨胀,其在内部将呈切屑形式的生物质分裂成生物质细小颗粒。在另一实施例中,蒸汽爆破段的蒸汽爆破反应器部分含有专用排出机构,其经配置以将生物质切屑材料“爆破”到大气压力下的下一段。排出机构打开并将来自高压蒸汽爆破反应器的生物质释放出此反应器排出出口阀门或门到泄料槽的进给管线中。In an embodiment, a small opening forms an outlet and into a tube or other container area maintained at a pressure of about 4 to 10 bar, and any internal fluid or gas at high pressure expands to split the biomass internally. In some cases, the pressure drop from the high pressure in the steam explosion reactor goes all the way down to atmospheric pressure. In either case, the large pressure drop that occurs in the pipe or other vessel between the outlet in the steam explosion section and the water removal section of the cyclone drops rapidly. In an embodiment, the pressure drop is performed rapidly by extending a monolithic structure of biomass between 160 and 450 PSI into a tube under a significant reduced pressure (e.g., 4 to 10 bar) to induce a drop in pressure Then, or due to the internal "explosion" of the rapid steam expansion due to the "flash" of liquid water into vapor after the pressure drops below its vapor pressure, it internally breaks down the biomass in the form of chips into fine particles of biomass. In another embodiment, the steam explosion reactor portion of the steam explosion section contains a dedicated exhaust mechanism configured to "explode" the biomass cutting material to the next section at atmospheric pressure. The discharge mechanism opens and releases the biomass from the high pressure steam explosion reactor out of the reactor discharge outlet valve or door into the feed line of the blowdown chute.

因此,出自此段中的蒸汽爆破反应器的经加压蒸汽或过热水快速地下降以引起爆破,这将生物质切屑分解成细小颗粒。(见例如图4D,其示出爆破成生物质细颗粒453的生物质切屑。)构成生物质的原始纤维束爆破成形成离散的细粉末颗粒的碎片。(见例如图4A到4C,其示出具有通过木质素围绕并粘结在一起的纤维素纤维的纤维束的生物质切屑的不同放大水平并与图4D形成对比。)Therefore, the pressurized steam or superheated water coming out of the steam explosion reactor in this section descends rapidly to cause the explosion, which breaks down the biomass cuttings into fine particles. (See, eg, Figure 4D, which shows biomass chips that explode into biomass fine particles 453.) The raw fiber bundles that make up the biomass explode into fragments that form discrete fine powder particles. (See, e.g., FIGS. 4A through 4C showing different magnification levels of biomass chips with fiber bundles of cellulose fibers surrounded and bonded together by lignin and contrasted with FIG. 4D.)

在容器/吹洗管线的末端处,水分和生物质切屑被挤出反应器排出口到在大致大气压力下的容器,例如吹洗管线。部分中空的纤维和生物质材料的其它多孔区域内部的高压蒸汽或水转换成蒸气使得生物质细胞爆破成细颗粒的潮湿粉末。生物质的整体结构包含木质素和围绕多个纤维素纤维的半纤维素的有机聚合物。生物质的整体结构在此SEP步骤中在内部分裂,此SEP步骤使用至少水分、压力和热量来释放和暴露纤维素纤维,以使其能够(作为实例)在生物质气化反应期间直接起反应而不是仅在木质素和半纤维素层已首先反应从而接着暴露纤维素纤维之后起反应。高温还减少了分解生物质的结构所需的能源/力,因为存在促进沿着中层的纤维分离的木质素软化。At the end of the vessel/purge line, moisture and biomass shavings are squeezed out of the reactor outlet to a vessel at approximately atmospheric pressure, such as the purge line. The conversion of high-pressure steam or water to steam inside the partially hollow fibers and other porous regions of the biomass material causes the biomass cells to explode into a fine-grained moist powder. The overall structure of biomass consists of organic polymers of lignin and hemicellulose surrounding multiple cellulose fibers. The overall structure of the biomass breaks down internally in this SEP step which uses at least moisture, pressure and heat to release and expose the cellulose fibers so that they can (as an example) react directly during the biomass gasification reaction Rather than reacting only after the lignin and hemicellulose layers have reacted first, thereby exposing the cellulose fibers. The high temperature also reduces the energy/force required to break down the structure of the biomass because there is lignin softening that promotes fiber separation along the mesolayer.

因此,在内部在蒸汽爆破段中,在蒸汽爆破反应器中存在机械机构开口(例如,阀门或门)或仅仅小孔。反应器填充有在高压力下可能呈插塞形式的经软化生物质切屑,并且在将那些经软化生物质切屑暴露于低压一段时间之后,以物理方式将含有木质素、纤维素纤维和半纤维素的生物质的纤维束的整体结构分裂成碎片并且彼此分离。当在蒸汽爆破反应器中在不太苛刻的条件下(例如,175到185摄氏度和160PSI)操作蒸汽爆破过程时,那么小纤维碎片大小的颗粒自排出口排出并且在更苛刻的条件下(例如,300PSI)产生非常非常精细的颗粒。Thus, internally in the steam explosion section, there are mechanical mechanism openings (eg valves or doors) or just small holes in the steam explosion reactor. The reactor is filled with softened biomass chips that may be in the form of plugs under high pressure, and after exposing those softened biomass chips to low pressure for a period of time, physically will contain lignin, cellulose fibers and hemifibers The overall structure of the fiber bundles of the prime biomass breaks into pieces and separates from each other. When the steam explosion process is operated under less severe conditions (e.g., 175 to 185 degrees Celsius and 160 PSI) in a steam explosion reactor, then small fiber fragment sized particles are discharged , 300PSI) produces very, very fine particles.

来自所述段的产生为潮湿的细颗粒形式的生物质具有小于50微米厚且小于500微米长的平均尺寸。在实施例中,蒸汽爆破段耦合到精炼段,精炼段具有一个或多个刀片,其经配置以在经加压生物质通过出口孔离开蒸汽爆破段到吹洗管线之前机械地搅拌经加压生物质,并且所产生的具有降低的水分含量的生物质细颗粒包含成碎裂的、撕破的、撕碎的及其任何组合的并且可以大体上具有小于30微米厚且小于250微米长的平均尺寸的纤维素纤维。所产生的那些潮湿的生物质细颗粒随后被馈送到生物质气化炉114的进给区。The biomass produced in wet fine particle form from the section has an average size of less than 50 microns thick and less than 500 microns long. In an embodiment, the steam explosion section is coupled to a refining section having one or more blades configured to mechanically agitate the pressurized biomass before it exits the steam explosion section through an outlet hole to a purge line. Biomass, and the resulting biomass fine particles having a reduced moisture content comprise fragmented, torn, shredded, and any combination thereof and may generally be less than 30 microns thick and less than 250 microns long Cellulose fibers of average size. Those moist biomass fines produced are then fed to the feed zone of the biomass gasifier 114 .

在内部将纤维束中的生物质的整体结构分裂成纤维素纤维、木质素和半纤维素的片段和碎片引起以下所有三者:1)相比于接收到的呈切屑形式的生物质,呈细颗粒形式的生物质的表面积增大,2)消除在开始纤维素纤维的反应之前使木质素和半纤维素的外层起反应的需要,以及3)呈细颗粒形式的生物质的粘度发生改变以如同沙粒而不是如同纤维流动。Internally splitting the overall structure of biomass in fiber bundles into fragments and fragments of cellulosic fibers, lignin and hemicellulose results in all three of the following: The increased surface area of the biomass in fine particle form, 2) eliminates the need to react the outer layers of lignin and hemicellulose before initiating the reaction of the cellulose fibers, and 3) the viscosity of the biomass in fine particle form occurs Change to flow like grains of sand instead of fibers.

由SEP反应器产生的至生物质的形态改变可以包含:Morphological changes to biomass produced by SEP reactors can include:

a.没有完整的纤维结构存在,而是所有部件爆破从而引起更多表面积,这导致在生物质气化炉中的更高反应速率;a. No complete fiber structure exists, but all parts are exploded causing more surface area, which leads to higher reaction rate in the biomass gasifier;

b.纤维呈现弯曲,它们分层,细胞壁被暴露并破裂;b. The fibers appear bent, they delaminate, and the cell walls are exposed and ruptured;

c.一些木质素保持依附纤维素纤维的细胞壁;c. Some lignin remains attached to the cell walls of the cellulose fibers;

d.半纤维素被部分地水解且连同木质素一起被部分地溶解;d. Hemicellulose is partially hydrolyzed and partially dissolved together with lignin;

e.木质素与碳水化合物/多糖(即半纤维素和纤维素)之间的粘结大部分断裂;以及e. The bond between lignin and carbohydrates/polysaccharides (i.e. hemicellulose and cellulose) is largely broken; and

f.本文中所论述的许多其它改变。f. Many other changes discussed herein.

所形成的潮湿的细颗粒可以是例如平均直径20到50微米厚并且长度小于100微米。应注意,1英寸=25,400微米。因此,生物质作为切屑来自削片机单元104时平均高达1英寸长且0.25英寸厚,并且作为潮湿的细颗粒时变成平均直径20到50微米厚且长度小于100微米,这在大小上减小了超过2000倍。饱和生物质切屑的剧烈爆破分解在以比呈切屑形式的生物质的多孔区域中的饱和高压水分可自生物质的结构逸出的速率更迅速的速率下发生。The moist fine particles formed may be, for example, 20 to 50 microns in average diameter thick and less than 100 microns in length. It should be noted that 1 inch = 25,400 microns. Thus, biomass coming from the chipper unit 104 as chips averages up to 1 inch long and 0.25 inches thick, and as wet fines becomes 20 to 50 microns in average diameter thick and less than 100 microns in length, which is reduced in size. more than 2000 times smaller. Vigorous explosive decomposition of saturated biomass cuttings occurs at a rate faster than the rate at which saturated high pressure moisture in the porous regions of the biomass in the form of chips can escape from the structure of the biomass.

应注意,不需要细胞或纤维束的外部机械分离,实际上所述过程使用蒸汽来从内部向外爆破细胞。(见图4E,其示出具有被磨损的或部分地分离成个别纤维的一束纤维的生物质切屑,生物质切屑451。)在生物质切屑上使用SEP产生纤维素和具有一些木质素涂层的半纤维素的细小颗粒。(见图4D,其示出实例生物质切屑,包含第一生物质切屑451,分解成生物质细颗粒453。)此呈细粒形式的木质素、半纤维素和纤维素的复合物具有高密度的可以在系统中移动/传送的高表面积。It should be noted that no external mechanical separation of cells or fiber bundles is required, in fact the process uses steam to blast the cells from the inside out. (See FIG. 4E, which shows a biomass chip with a bundle of fibers abraded or partially separated into individual fibers, biomass chip 451.) Using SEP on the biomass chip produces cellulose and has some lignin coating. layer of fine particles of hemicellulose. (See Figure 4D, which shows example biomass chips, including first biomass chips 451, decomposed into biomass fine particles 453.) This composite of lignin, hemicellulose, and cellulose in fine particle form has a high Density of high surface area that can be moved/conveyed in the system.

所产生的生物质细颗粒向下游被馈送到生物质气化炉114以用于在生物质气化炉114的反应器中的快速生物质气化反应,因为它们相比于接收到的呈切屑形式的生物质对于相同量的生物质形成更高的表面积与体积比,这允许更高热量传递到生物质材料以及生物质中的所有分子的更快速热分解和气化。The produced biomass fines are fed downstream to the biomass gasifier 114 for a fast biomass gasification reaction in the reactor of the biomass gasifier 114 as they are in the form of chips compared to the received The form of biomass creates a higher surface area to volume ratio for the same amount of biomass, which allows for higher heat transfer to the biomass material and faster thermal decomposition and gasification of all molecules in the biomass.

请参考图1B,作为一实例,其中一个或多个蒸汽供应输入端可以包含产生自从一个或多个旋流器单元回收的再循环脏水的低压蒸汽。例如,如本文所描述的实施例包含从旋流器单元导出废气并且将废气馈送到生物质气化炉。同样,那些气体和任何其它冷凝物可以馈送到松节油回收单元。因此,含有由蒸汽爆破段产生的自旋流器单元回收的有机化合物的气体被收集并且通过进给管线馈送到生物质气化炉。生物质气化炉接着将含有有机化合物的那些气体转换成合成气组分和其它气体。Referring to FIG. 1B , as an example, one or more of the steam supply inputs may contain low pressure steam generated from recycled dirty water recovered from one or more cyclone units. For example, embodiments as described herein include exporting off-gas from a cyclone unit and feeding the off-gas to a biomass gasifier. Likewise, those gases and any other condensate can be fed to a turpentine recovery unit. Thus, gas containing organic compounds recovered from the spinner unit produced by the steam explosion section is collected and fed to the biomass gasifier through a feed line. The biomass gasifier then converts those gases containing organic compounds into syngas components and other gases.

松节油和其它挥发物可以经由自一个或多个旋流器单元回收的脏冷凝水的蒸汽雾化被输送到生物质气化炉。例如,含有挥发物/松节油的进给蒸汽可以包含来自一个或多个旋流器的废气并且被馈送到气化炉。可以包含松节油回收单元、以及待销售的制品、气化炉、或用于气化炉的燃烧器系统或转化炉。另外,可以回收在压紧生物质时挤出的以及经由螺旋进给系统移动的脏水并将其送到松节油回收单元。Turpentine and other volatiles may be delivered to the biomass gasifier via steam atomization of dirty condensate recovered from one or more cyclone units. For example, feed steam containing volatiles/turpentine may contain waste gas from one or more cyclones and be fed to the gasifier. A turpentine recovery unit may be included, as well as products to be sold, a gasifier, or a burner system or reformer for a gasifier. Additionally, dirty water squeezed out when compacting the biomass and moved through the screw feed system can be recovered and sent to a turpentine recovery unit.

在实施例中,可能用循环操作而非连续输送机系统。循环操作允许软的潮湿切屑加载到SEP反应器中并且接着蒸汽输入端引入高温和高压蒸汽持续10分钟以升高生物质中的气体和液体的压力。在此阶段之后,阀门或门打开以使生物质颗粒伸入进给管线中到泄料槽中。In embodiments, looping operations may be used rather than continuous conveyor systems. Cyclic operation allowed soft wet cuttings to be loaded into the SEP reactor and then high temperature and high pressure steam was introduced at the steam input for 10 minutes to raise the pressure of the gases and liquids in the biomass. After this period, the valve or gate is opened to allow the biomass pellets to pass into the feed line to the blowdown chute.

蒸汽爆破段的出口段处的收集室用来收集减小成较小颗粒大小且呈浆状形式的生物质。一个或多个旋流式过滤器可以和进给管线成一直线以使水汽从生物质颗粒分离,其中生物质颗粒接着被馈送到泄料槽。A collection chamber at the outlet section of the steam explosion section is used to collect the biomass reduced to smaller particle size and in slurry form. One or more cyclone filters may be in-line with the feed line to separate moisture from the biomass particles, which are then fed to the blowdown tank.

应注意,也可以并入方法以减小蒸汽爆破单元的出口中的压力从而减少动力气体。因此,可以包含一个或多个减压区域以将来自SEP容器的高压降低至较低排出压力。因此,本设计可以包含从蒸汽爆破单元当中定位压降位置以将压力从蒸汽爆破单元中的高压降低至例如4到10巴的减压。可以在管道中较早地进行压降从而形成旋流。It should be noted that methods can also be incorporated to reduce the pressure in the outlet of the steam explosion unit to reduce motive gas. Therefore, one or more relief zones may be included to reduce the high pressure from the SEP vessel to a lower discharge pressure. Thus, the present design may include locating a pressure drop location from within the steam explosion unit to reduce the pressure from the high pressure in the steam explosion unit to a reduced pressure of eg 4 to 10 bar. A pressure drop can be made earlier in the pipe to create a swirling flow.

同样,在示例性实施例中,在生物质颗粒的SEP预处理步骤与夹带气体将生物质颗粒馈送到生物质气化炉中之间没有其它空气引入,这减少了辐射和净化气体。可以包含选项以使用出自蒸汽爆破单元的动力气体用于至生物质气化炉中的夹带气体。Also, in the exemplary embodiment, no additional air is introduced between the SEP pre-treatment step of the biomass particles and the entrained gas feeding the biomass particles into the biomass gasifier, which reduces radiation and purges the gas. An option may be included to use motive gas from the steam explosion unit for entrained gas into the biomass gasifier.

在另一实施例中,在蒸汽爆破段的出口处,呈插塞形式的生物质一度爆破成潮湿的细颗粒形式。填充有高压蒸汽和/或过热水的蒸汽爆破段含有排出出口,其经配置以将生物质材料“爆破”到在大气压力下的下一段以产生呈细颗粒形式的生物质。呈细颗粒形式的生物质在高速度下流过泄料槽的进给管线。In another embodiment, the biomass in the form of a plug is once exploded into moist fine particle form at the outlet of the steam explosion section. A steam explosion section filled with high pressure steam and/or superheated water contains discharge outlets configured to "explode" the biomass material to the next section at atmospheric pressure to produce biomass in fine particle form. Biomass in the form of fine particles flows through the feed line of the blowdown chute at high velocity.

呈潮湿的细颗粒形式的生物质进入泄料槽的进给管线。进给管线起初较小,例如直径仅1.5英寸,其中生物质颗粒在高速度下经过。可以在吹洗管线的初始部分中添加流动增强剂,例如蜡,同时纤维仍然湿润以改进材料一致性并且避免水力粘结。现在进给管线膨胀至直径为60英寸,并且呈潮湿的细颗粒形式的生物质通过围绕设置的加热线圈维持其热量并加热吹洗管线。维持生物质的温度往往会帮助生物质的松香和树脂酸结晶从而防止纤维颗粒一起凝聚成团。因此,温度有助于防止木质素结块以及防止松香硬化。Biomass in the form of moist fines enters the feed line of the blowdown chute. The feed line is initially small, eg, only 1.5 inches in diameter, through which the biomass particles pass at high velocity. Flow enhancers such as wax can be added in the initial part of the purge line while the fibers are still wet to improve material consistency and avoid hydraulic binding. The feed line is now expanded to a diameter of 60 inches and the biomass in the form of moist fines maintains its heat and heats the purge line through heating coils positioned around it. Maintaining the temperature of the biomass tends to help crystallize the rosin and resin acids of the biomass and prevent the fiber particles from agglomerating together. Thus, the temperature helps prevent lignin from caking and prevents rosin from hardening.

包含1)来自生物质气化炉114的再循环炉灰和2)烯烃(例如,蜡)中的任一种的助流剂在1)蒸汽爆破段的排出出口和2)进给管线中的任一个处注入以防止被生物质阻塞。另外,进给管线可以具有围绕进给管线设置的加热线圈以维持呈细颗粒形式的生物质的高温,从而帮助防止呈细颗粒形式的生物质中的松香和树脂酸的结晶。A flow aid comprising either 1) recycled ash from the biomass gasifier 114 and 2) an olefin (e.g., wax) in 1) the discharge outlet of the steam explosion section and 2) the feed line Inject at either to prevent clogging with biomass. In addition, the feed line may have heating coils disposed around the feed line to maintain the high temperature of the biomass in fine particle form to help prevent crystallization of rosin and resin acids in the biomass in fine particle form.

所产生的生物质颗粒归因于蒸汽在吹洗管线中闪蒸并作为水汽被排出而失去水分含量的较大百分比。所产生的生物质颗粒和水分接着由旋流式过滤器分离并且接着被馈送到泄料槽。因此,水分离单元内嵌有吹洗管线。蒸汽爆破段的出口段处的收集室用来收集减小成较小颗粒大小且呈浆状形式的生物质并且将其馈送到水分离单元。在旋流器单元和/或干燥器单元中从呈细颗粒形式的生物质去除水。The resulting biomass particles lost a large percentage of their moisture content due to steam flashing in the purge line and being expelled as water vapor. The resulting biomass particles and moisture are then separated by a cyclone filter and then fed to a blowdown chute. Therefore, the water separation unit has built-in purge lines. A collection chamber at the outlet section of the steam explosion section is used to collect the biomass reduced to smaller particle size in slurry form and feed it to the water separation unit. Water is removed from the biomass in fine particle form in a cyclone unit and/or a dryer unit.

生物质细颗粒的水分含量进一步在泄料槽的出口处通过干燥器单元(例如,快速干燥器或低温焙烧单元)变干,这将生物质细颗粒的水分含量降低至按重量计低于1%到20%。纤维制备的目标是形成如下生物质颗粒:其具有最大表面积且尽可能干燥至所输出生物质细颗粒的按重量计5%到20%的水分。快速干燥器仅仅吹出热空气以干燥来自泄料槽的生物质颗粒。快速干燥器可以大体上位于泄料槽的出口处或在其入口处替代旋流器,以使得所输出的生物质颗粒含有按重量计大于5%但是小于20%的水分含量。快速干燥器可以将生物质馈送到筒仓用于储存以进一步使SEP生物质细颗粒在被馈送到闭锁式料斗之前变干。在实施例中,浆式干燥器可以进一步归因于承载颗粒的气体进入干燥器时的速度而减小生物质颗粒大小,其充当针对进入的生物质颗粒的研磨机。The moisture content of the biomass fines is further dried at the outlet of the blowdown chute through a dryer unit (e.g., a flash dryer or a low-temperature roasting unit), which reduces the moisture content of the biomass fines to below 1 by weight. % to 20%. The goal of fiber production is to form biomass particles that have the largest surface area and are as dry as possible to a moisture of 5% to 20% by weight of the output biomass fines. The flash dryer blows only hot air to dry the biomass pellets from the blowdown chute. The flash dryer may be located substantially at the outlet of the blowdown chute or in place of the cyclone at its inlet so that the output biomass particles contain a moisture content greater than 5% but less than 20% by weight. A flash dryer can feed biomass to a silo for storage to further dry out the SEP biomass fines before being fed to a lock hopper. In an embodiment, the paddle dryer may further reduce the biomass particle size due to the velocity of the particle-carrying gas as it enters the dryer, which acts as a grinder for the incoming biomass particles.

所得生物质颗粒与热机械成浆(TMP)的不同之处在于颗粒更像晶体结构并且比往往会缠绕和结块的纤维更容易流动。The resulting biomass pellets differ from thermomechanical pulping (TMP) in that the pellets are more crystalline in structure and flow more easily than fibers, which tend to entangle and clump.

呈细颗粒形式的生物质的按重量计5%到约35%的减少的水分含量通过输送系统(作为实例)馈送到焙烧单元112,从而在从100到700摄氏度的温度下经历焙烧或热解,持续预置的时间量。A reduced moisture content of 5% to about 35% by weight of the biomass in the form of fine particles is fed through a conveying system (as an example) to the torrefaction unit 112 to undergo torrefaction or pyrolysis at temperatures from 100 to 700 degrees Celsius , for a preset amount of time.

输送机系统将呈颗粒形式的生物质供应到焙烧单元112以在低于700摄氏度的温度下处理生物质,持续预置的时间量以形成废气,将在创建通过贮槽收集的并且可以最终馈送到有机液体制品合成反应器(例如,甲醇合成反应器)的合成气组分的一部分时使用。The conveyor system supplies the biomass in pellet form to the roasting unit 112 to process the biomass at a temperature below 700 degrees Celsius for a preset amount of time to form an off-gas that will be collected in the created tank and can eventually be fed Used when part of the synthesis gas component to an organic liquid product synthesis reactor (eg, a methanol synthesis reactor).

出自泄料槽和快速干燥器的生物质细颗粒归因于蒸汽闪蒸、进一步空气干燥而已经具有低水分含量,并且是具有木质素涂层、木质素、纤维素和半纤维素等的片段的纤维素纤维的碎片的复合物。生物质气化炉114具有反应器容器,其经配置以使具有增大的表面积的呈潮湿细颗粒形式的生物质归因于通过蒸汽爆破单元108的分裂而起反应。生物质气化炉114具有高压蒸汽供应输入端和一个或多个加热器,并且在存在蒸汽的情况下,呈细颗粒形式的生物质在反应器容器中以0.1秒与5.0秒之间的滞留时间以快速生物质气化反应起反应从而产生至少合成气组分,包含氢气(H2)和一氧化碳(CO)。当所产生的细颗粒以高密度供应到生物质气化炉114时,接着小颗粒快速起反应并且更容易且彻底地将生物质的更大烃分子分解成合成气组分。因此,几乎所有生物质材料木质素、纤维素纤维和半纤维素彻底地气化,而非切屑的内部部分中的一些未分解至焦化切屑的硬皮外壳分解的相同范围。这些细颗粒相比于切屑形成更少的残余焦油、更少的炭涂层以及更少的沉淀物。因此,打碎呈纤维束的生物质的集成结构往往会减少后续在生物质气化中产生的焦油的量。这些细颗粒还允许更大堆积密度的材料被馈送到生物质气化炉114。作为附注,具有按重量计至少10%的水作为液体或蒸气可以协助产生除在生物质气化炉114中所产生的CO和H2之外的甲醇CH30H作为反应产物。Biomass fines coming out of blowdown chutes and flash dryers already have low moisture content due to steam flashing, further air drying and are fragments with lignin coating, lignin, cellulose and hemicellulose etc. A composite of fragments of cellulose fibers. The biomass gasifier 114 has a reactor vessel configured to react biomass in the form of wet fine particles having an increased surface area due to disintegration by the steam explosion unit 108 . The biomass gasifier 114 has a high pressure steam supply input and one or more heaters, and in the presence of steam, the biomass in the form of fine particles is retained in the reactor vessel at a residence time of between 0.1 seconds and 5.0 seconds Time reacts in a fast biomass gasification reaction to produce at least the syngas components, including hydrogen (H2) and carbon monoxide (CO). When the fine particles produced are supplied to the biomass gasifier 114 in high density, then the small particles react quickly and more easily and completely break down the larger hydrocarbon molecules of the biomass into syngas components. Thus, almost all of the biomass material lignin, cellulose fibers, and hemicellulose are gasified completely, while some of the inner portion of the non-chips are not decomposed to the same extent that the crusty outer shell of coker chips decomposes. These fine particles form less residual tar, less char coating, and less deposits than swarf. Thus, breaking up the integrated structure of biomass in fiber bundles tends to reduce the amount of tars that are subsequently produced in biomass gasification. These fine particles also allow for a greater bulk density of material to be fed to the biomass gasifier 114 . As a side note, having at least 10% by weight water as a liquid or vapor can assist in producing methanol CH30H as a reaction product in addition to the CO and H2 produced in the biomass gasifier 114 .

焙烧单元和生物质气化炉114可以组合为整合单元。The roasting unit and the biomass gasifier 114 may be combined into an integrated unit.

在替代方案中,潮湿的经分裂生物质颗粒可以呈浆料形式直接地或在干燥之后从蒸汽爆破反应器的输出端馈送到制粒机。制粒机可以将生物质从细颗粒形式致密成生物质颗粒,那些颗粒接着被馈送到生物质气化炉。生物质从细颗粒形式到颗粒形式的此直接馈送和转换节省了许多步骤以及与那些所消除步骤有关的大量能耗。替代地,可以传输颗粒到设施以用于进一步处理为液体燃料、热量/电力、动物饲料、垫料或化学制品。In an alternative, the wet split biomass particles can be fed from the output of the steam explosion reactor to the pelletizer in slurry form directly or after drying. Pelletizers can densify biomass from a fine-grained form into biomass granules, which are then fed to a biomass gasifier. This direct feeding and conversion of biomass from fine particle form to granular form saves many steps and the substantial energy consumption associated with those eliminated steps. Alternatively, the pellets can be transported to a facility for further processing as liquid fuel, heat/electricity, animal feed, bedding or chemicals.

在实施例中,生物质气化炉114设计为辐射地传送热量到流过反应器设计的生物质颗粒,其中生物质颗粒的快速气化滞留时间为0.1秒到10秒,优选地,少于一秒。生物质颗粒和流过辐射热反应器的反应气体基本上由来自辐射热反应器的表面的辐射热促进并且可能热传递地辅助流动中夹带的颗粒。反应器可以用一般超过900摄氏度以及优选地至少1200℃的温度加热颗粒以产生包含一氧化碳和氢气的合成气组分,并且将所产生的甲烷保持在退出制品、退出制品中残留的最小焦油以及所产生的炉灰的组分组成的<1%的水平下。In an embodiment, the biomass gasifier 114 is designed to radiatively transfer heat to the biomass particles flowing through the reactor design, wherein the rapid gasification residence time of the biomass particles is 0.1 seconds to 10 seconds, preferably, less than one second. The flow of biomass particles and reaction gases through the radiant reactor is substantially facilitated by radiant heat from the surfaces of the radiant reactor and possibly heat transferally assisting particles entrained in the flow. The reactor can heat the particles with temperatures generally in excess of 900 degrees Celsius, and preferably at least 1200 degrees Celsius, to produce a syngas component comprising carbon monoxide and hydrogen, and to keep the methane produced in the exit product, with minimal residual tar in the exit product and the resulting The component composition of the ash produced is at a level of <1%.

图3-1到3-4示出了生物质气化炉114的示例性实施例。图3-1示出了使用辐射热的喷泉反应器,其中承载生物质的夹带气体在气化炉的底部处进入并且通过中心管和在由中心管形成的隔墙上方的喷泉投射并落入在外管与中心管之间形成的区段中。图3-2和3-3示出了示例性卡口反应器辐射热设计,其中一系列辐射热管用以对注入的生物质加热。燃气燃烧器可以将热量直接提供到管或提供到供应到管的中间源,例如加热气体。生物质可以在管外部,而热量在内部供应到管。替代地,生物质可以在管板与耐火内衬之间。图3-4示出了示例性下向通风辐射热反应器,其中多个管用以向反应器提供辐射热。生物质可以或者在管外部而热量在内部供应到管,或反之亦然。An exemplary embodiment of a biomass gasifier 114 is shown in FIGS. 3-1 through 3-4. Figure 3-1 shows a fountain reactor using radiant heat, where entrained gas carrying biomass enters at the bottom of the gasifier and is projected through a central tube and a fountain above the partition wall formed by the central tube and falls into In the section formed between the outer tube and the center tube. Figures 3-2 and 3-3 illustrate exemplary bayonet reactor radiant heat designs in which a series of radiant heat pipes are used to heat injected biomass. Gas burners may provide heat directly to the tubes or to an intermediate source, such as heating gas, supplied to the tubes. Biomass can be outside the tubes while heat is supplied to the tubes internally. Alternatively, biomass may be between the tubesheet and refractory lining. 3-4 illustrate an exemplary downdraft radiant heat reactor in which multiple tubes are used to provide radiant heat to the reactor. Biomass can either be external to the tubes and heat supplied to the tubes internally, or vice versa.

热接收器106具有带有内壁的腔。相对于反应管102的热接收器106的腔壁的辐射促进的几何结构将化学反应器的多个管102定位成偏移以及在接收器106内部的交错布置。腔壁的表面积大于反应管102占用的面积以允许辐射从多个角度到达管102上的区域。接收器106腔的内壁和反应管102基本上通过辐射交换能源,其中壁和管102充当辐射的再发射器以获得到达所有管102的高辐射的热流通量,并且因此,避免屏蔽和阻挡辐射到达管102,从而允许反应管102获得从反应管102中的反应区的开始到结尾的极其一致的温度分布。The heat receiver 106 has a cavity with inner walls. The radiation-promoting geometry of the cavity walls of the thermal receiver 106 relative to the reaction tubes 102 positions the plurality of tubes 102 of the chemical reactor in an offset and staggered arrangement inside the receiver 106 . The surface area of the chamber walls is greater than the area occupied by the reaction tube 102 to allow radiation to reach areas on the tube 102 from multiple angles. The inner walls of the chamber of the receiver 106 and the reaction tubes 102 essentially exchange energy by radiation, wherein the walls and tubes 102 act as re-emitters of radiation to obtain a high radiative heat flux to all tubes 102, and thus, avoid shielding and blocking radiation to the tube 102 , allowing the reaction tube 102 to obtain an extremely consistent temperature profile from the beginning to the end of the reaction zone in the reaction tube 102 .

因此,反应管102和腔壁的几何结构通过以下方式使入射辐射的分布成形:使用这些1)交错的且偏移的管102,其结合2)相比于附件管102所占用的面积更大直径的腔壁,并且另外3)结合在几何结构处相对于彼此的多个反应管几何布置之间的相互管辐射交换。壁由高度反射辐射或吸收并再发射辐射的材料制成。入射辐射的分布的塑形使用在接收器106的腔内辐射的反射和吸收两者。因此,热接收器106的内壁通过或者1)吸收并再发射辐射能量,2)将入射辐射高度反射到管102,或3)这些的任何组合来对准并充当辐射分配器,从而维持附件超高热通量化学反应器的操作温度。充当辐射的再发射器的来自1)腔壁、2)直接来自蓄热式燃烧器以及3)来自其它管的外壁的辐射通过反应管102吸附,并且接着热量通过传导传递到反应管102的内壁,其中热量在900摄氏度与1600摄氏度之间的温度下(并且优选地,高于1100摄氏度)辐射到反应颗粒和气体。Thus, the geometry of the reaction tubes 102 and chamber walls shapes the distribution of incident radiation by using these 1) staggered and offset tubes 102, which in combination 2) occupy a larger area than the accessory tubes 102 diameter of the chamber wall, and additionally 3) inter-tube radiative exchange between multiple reaction tube geometric arrangements relative to each other in conjunction with the geometry. The walls are made of materials that either highly reflect radiation or absorb and re-emit radiation. The shaping of the distribution of the incident radiation uses both reflection and absorption of radiation within the cavity of the receiver 106 . Thus, the inner walls of the thermal receiver 106 align and act as radiation distributors by either 1) absorbing and re-emitting radiant energy, 2) highly reflecting incident radiation to the tube 102, or 3) any combination of these, thereby maintaining the attachment superconductivity. The operating temperature of a high heat flux chemical reactor. Radiation from 1) the cavity walls, 2) directly from the regenerative burner, and 3) from the outer walls of other tubes acting as re-emitters of radiation is absorbed by the reaction tube 102 and heat is then transferred to the inner wall of the reaction tube 102 by conduction , wherein heat is radiated to the reacting particles and gas at temperatures between 900 and 1600 degrees Celsius (and preferably above 1100 degrees Celsius).

如所论述,接收器106的腔的内壁以及反应管102在彼此之间主要通过辐射而不是通过对流或传导交换能源,从而允许反应管102获得极一致的温度分布,即使一般较低温度生物质颗粒和夹带气体从第一入口点在反应区中进入反应管102并且穿过经加热的腔以在第二出口点处离开反应区。来自内壁和反应管102的此辐射热传递促进化学反应并且使得化学反应物的温度快速提升到接近制品以及脱离反应器出口的其它排出材料的温度。As discussed, the inner walls of the cavity of the receiver 106 and the reaction tubes 102 exchange energy between each other primarily by radiation rather than by convection or conduction, allowing the reaction tubes 102 to obtain a very consistent temperature distribution, even with typically lower temperature biomass Particles and entrained gas enter the reaction tube 102 in the reaction zone from a first entry point and pass through the heated chamber to exit the reaction zone at a second exit point. This radiant heat transfer from the inner walls and reaction tubes 102 promotes the chemical reaction and rapidly raises the temperature of the chemical reactants to near the temperature of the product and other effluent materials exiting the reactor outlet.

反应管102中的每一个的气化反应区的长度和直径尺寸经设定大小以给出在至少900摄氏度的气化温度下大于0.1秒的滞留时间以及在多个反应管102中的气化区的出口。反应产物具有来自气化区的出口的等于或超出900摄氏度的温度,并且在此化学反应器设计中的多个反应管102增大了用于生物质颗粒的辐射交换以及套间辐射交换的可用反应器表面积。在反应管102中在反应区内在滞留时间内发生分散的落下的生物质微粒的快速气化与所得的稳定炉灰形成,从而使得焦油的完整改善为每标准立方米低于500毫克,并且至少90%的生物质转换至氢气和一氧化碳制品的生产。The length and diameter dimensions of the gasification reaction zone of each of the reaction tubes 102 are sized to give a residence time of greater than 0.1 seconds at a gasification temperature of at least 900 degrees Celsius and gasification in the plurality of reaction tubes 102 area exit. The reaction products have a temperature at or above 900 degrees Celsius at the outlet from the gasification zone, and the multiple reaction tubes 102 in this chemical reactor design increase the available reactions for radiative exchange of biomass particles as well as radiative exchange between jackets device surface area. Rapid gasification of dispersed falling biomass particles and resulting stable ash formation occurs within the reaction zone within the reaction tube 102 within the residence time, resulting in a complete improvement of tar below 500 milligrams per normal cubic meter and at least 90% conversion of biomass to production of hydrogen and carbon monoxide products.

为了实现高转换率和选择率,生物质气化要求温度超过1000℃。这些在标准的流体化床气化炉中是难以实现的,因为更高温度要求生物质本身的不断更大的部分的燃烧。因此,间接和流体化床气化通常限于800℃的温度。在这些温度下,不希望的更高烃(焦油)的产生是明显的。这些焦油堵塞下游设备并且使催化表面变脏/钝化,从而在焦油清除设备中需要大量的资本投资(总设备成本的10%到30%)。高热通量热系统能够极高效地获得高温。更重要的是,可以根据浓度和所需温度控制过程的效率,并且实现高温不再需要损耗生物质部分。因此,可以实现焦油裂化状况(1000到1300℃)中的温度,而不会损耗自生物质产生的燃料或总体处理效率。这免去了通常与生物质气化系统相关联的复杂焦油裂化设备列。另外,在高温下的操作改进了热传递并且减少了所需的滞留时间,从而减小了化学反应器的大小并且减少了其资金成本。To achieve high conversion and selectivity, biomass gasification requires temperatures in excess of 1000 °C. These are difficult to achieve in standard fluidized bed gasifiers because higher temperatures require the combustion of ever greater fractions of the biomass itself. Therefore, indirect and fluidized bed gasification are generally limited to temperatures of 800°C. At these temperatures, the production of undesired higher hydrocarbons (tars) is evident. These tars plug downstream equipment and foul/deactivate catalytic surfaces, requiring significant capital investment (10% to 30% of total equipment cost) in tar removal equipment. High heat flux thermal systems are able to achieve high temperatures extremely efficiently. What's more, the efficiency of the process can be controlled in terms of concentration and desired temperature, and achieving high temperatures no longer requires loss of biomass fraction. Thus, temperatures in tar cracking regimes (1000 to 1300°C) can be achieved without loss of fuel produced from biomass or overall process efficiency. This eliminates the complex train of tar cracking equipment normally associated with biomass gasification systems. Additionally, operation at high temperature improves heat transfer and reduces required residence time, thereby reducing the size and capital cost of the chemical reactor.

与1200℃与1450℃之间的壁温度清晰划定界限的操作温度以及超过900℃但是不高于二氧化硅熔化温度(1600℃)的排放气体温度通常不在气化中出现,并且当然不在间接(循环流体化床)气化中出现。可以在超高热通量化学反应器中进行的生物质的共气化和天然气的蒸汽转化的可能性不可在部分氧化气化炉中出现(因为甲烷将优先燃烧)。过程原料的灵活性源于简单的管状设计,并且出于这里所讨论的原因,大多数气化炉无法处理不同范围的燃料。Operating temperatures with a clearly demarcated wall temperature between 1200°C and 1450°C and exhaust gas temperatures above 900°C but not above the melting temperature of silica (1600°C) are generally not present in gasification, and certainly not in indirect (circulating fluidized bed) gasification occurs. The possibility of co-gasification of biomass and steam reforming of natural gas that can be performed in ultra-high heat flux chemical reactors cannot occur in partial oxidation gasifiers (since methane will be burned preferentially). The flexibility of the process feedstock comes from the simple tubular design and, for reasons discussed here, most gasifiers cannot handle a different range of fuels.

构成接收器306腔的内壁的材料可以具有机械和化学属性以在1100℃到1600℃之间的高温下保持其结构强度,对于接收器306腔具有ε>0.8的极高辐射率或ε<0.2的高反射率,以及高热容量(>200J/kg-K)和低热导率(<1W/m-K)。构成反应管302的材料具有高辐射率(ε>0.8)、高热导率(>1W/m-K)、适度的高热容量(>150J/kg-K)。The material making up the inner walls of the receiver 306 cavity may have mechanical and chemical properties to maintain its structural strength at elevated temperatures between 1100°C and 1600°C, with an extremely high emissivity of ε > 0.8 or ε < 0.2 for the receiver 306 cavity High reflectivity, as well as high heat capacity (>200J/kg-K) and low thermal conductivity (<1W/m-K). The material constituting the reaction tube 302 has high emissivity (ε>0.8), high thermal conductivity (>1W/m-K), and moderately high heat capacity (>150J/kg-K).

用以确定颗粒大小的实例粒度分析可以是数字图像处理颗粒大小和形状分析系统,例如,堀场集团有限公司(Horiba,Ltd.)的CamsizerXT粒度分析仪。此类系统使用一个或多个相机以为(例如,从30μm到30mm)的大小范围内的干粉和疏松材料提供快速且精确的粒度和颗粒形状分布。来自数字图像处理系统的测量允许现存数据与和筛选和沉积(其在一些情况下也可以用来测量粒度)一样有种种不同的技术相关联。在实施例中,使用堀场集团有限公司(Horiba,Ltd.)的CamsizerXT粒度分析仪测量蒸汽爆破的木屑的粒度。待测量的样本在可重复密封的袋中通过外部操纵捏合和搅拌袋中的材料来混合。在混合之后,例如大致3cm^3的样本量加载到仪器的样本料斗。目标是运行并分析足够的样本大小,例如至少来自每个样本的2百万颗粒,因此样本体积是就此程度唯一重要的,因为它相当于充足数目的颗粒。在仪器上的示例设定可以如下:0.2%的覆盖面积、图像比率1:1、具有X-喷射、间隙宽度=4.0mm、分散压力=380.0kPa、xFe_max[以及相应地xc_min]。控制进给比率以产生目标覆盖面积使得计算机可以足够快速地处理图像。相机成像比率是固定的,并且针对每次运行获得“基底”图像和变焦图像两者。平均粒度的单个值,例如直径小于50微米,可以是客观测量标准。在实施例中,Fe-max和xc-min两者的三点值是更完整的。因此,看起来如同6点值。粒度分布(PSD)可以定义为Fe-MaxD10、D50、D90以及Xc-minD10、D50、D90。接着测量可以使用多个值(例如,输入6值)来确定测量值。可以使用其它类似机构。An example particle size analysis to determine particle size may be a digital image processing particle size and shape analysis system, eg, Horiba, Ltd.'s CamsizerXT particle size analyzer. Such systems use one or more cameras to provide fast and accurate particle size and particle shape distributions for dry powders and bulk materials in the size range (eg, from 30 μm to 30 mm). Measurements from digital image processing systems allow correlation of existing data with a variety of techniques as well as screening and deposition (which in some cases can also be used to measure particle size). In the examples, the particle size of steam-exploded wood chips was measured using a Horiba, Ltd. Camsizer XT particle size analyzer. The samples to be measured are mixed in a resealable bag by kneading and stirring the contents of the bag with external manipulation. After mixing, a sample volume of, for example, approximately 3 cm3 is loaded into the instrument's sample hopper. The goal is to run and analyze a sufficient sample size, eg at least 2 million particles from each sample, so sample volume is only important to this extent as it equates to a sufficient number of particles. Example settings on the instrument may be as follows: 0.2% coverage, image ratio 1:1, with X-jet, gap width = 4.0mm, dispersion pressure = 380.0kPa, xFe_max [and correspondingly xc_min]. Controlling the feed rate to produce a target coverage area allows the computer to process the image quickly enough. The camera imaging ratio was fixed and both "base" and zoom images were acquired for each run. A single value for average particle size, eg, less than 50 microns in diameter, can be an objective measure. In the examples, three point values for both Fe-max and xc-min are more complete. Therefore, it looks like a 6-point value. Particle size distribution (PSD) can be defined as Fe-MaxD10, D50, D90 and Xc-minD10, D50, D90. Then measure can use multiple values (for example, enter 6 values) to determine the measured value. Other similar mechanisms may be used.

可以使用以体积为基础的Femax和xcmin进行计算。可以使用两个模型来分析颗粒图像:xc-min,其产生与通过以物理方式筛查/筛选样本所获得的那些结果相当的结果;以及Fe-max,其类似于用卡尺测量给定颗粒的最长尺寸。针对所有样本获得原始数据、频率图,封存的结果以及颗粒图像。D10、D50和D90可以体积为基础进行计算,是平均纵横比。D90描述其中分布的百分比九十具有较小粒度并且百分比十具有较大粒度的直径。D10直径具有百分比十较小和百分比九十较大。提供D10、D50和D90的三点规范被视为完整的且适合于大多数颗粒材料。在实施例中,粒度分布PSD可以定义为D50(μm)模型Fe-max。Calculations can be performed using volume-based Femax and xcmin. Two models can be used to analyze particle images: xc-min, which produces results comparable to those obtained by physically screening/screening samples; and Fe-max, which is similar to measuring the longest dimension. Get raw data, frequency plots, archived results, and particle images for all samples. D10, D50 and D90 can be calculated on a volume basis and are average aspect ratios. D90 describes the diameter in which ninety percent of the distribution has the smaller particle size and ten percent has the larger particle size. The D10 diameter has ten percent smaller and ninety percent larger. A three-point specification providing D10, D50 and D90 is considered complete and suitable for most granular materials. In an embodiment, the particle size distribution PSD can be defined as D50 (μm) model Fe-max.

表1-对于蒸汽爆破的木材的粒度分布Table 1 - Particle size distribution of wood for steam explosion

SEP处理的样本的粒度指数由xc-min和Fe-max模型产生。The particle size indices of the SEP-treated samples were generated by the xc-min and Fe-max models.

通过16巴的蒸汽压力和10分钟的反应时间产生表1中的实例。The examples in Table 1 were generated with a steam pressure of 16 bar and a reaction time of 10 minutes.

图2示出了用以从生物质中产生合成气并且从合成气中产生液体燃料制品的集成设备的流程图的实施例。蒸汽爆破单元308可以具有蒸汽爆破段和热水化处理段,其将生物质颗粒供应到或者干燥器、焙烧单元或者直接供应到生物质气化炉314。干燥器可以是快速干燥器、转鼓干燥器、桨式干燥器、空气干燥器或类似此类装置。Figure 2 shows an embodiment of a flow diagram of an integrated plant to produce syngas from biomass and liquid fuel products from the syngas. The steam explosion unit 308 may have a steam explosion section and a hydrothermal treatment section that supplies the biomass particles to either a dryer, a torrefaction unit or directly to the biomass gasifier 314 . The dryer can be a flash dryer, a drum dryer, a paddle dryer, an air dryer or similar such devices.

在实施例中,输送系统耦合到在蒸汽爆破单元308的出口段处的收集室,并且旋流器将呈颗粒形式的生物质供应到或者焙烧单元312或直接供应到生物质气化炉314,或供应到快速干燥器。在蒸汽爆破单元308中的蒸汽管段的接收器区段中构成生物质的大部分初始木质素和纤维素保持为所产生的生物质颗粒,但是现在大致上与在蒸汽爆破段308的出口段处的收集室中的纤维素纤维分离。In an embodiment, the delivery system is coupled to the collection chamber at the outlet section of the steam explosion unit 308 and the cyclone supplies the biomass in the form of particles to either the torrefaction unit 312 or directly to the biomass gasifier 314, Or supply to flash dryer. Most of the initial lignin and cellulose that make up the biomass in the receiver section of the steam pipe section in the steam explosion unit 308 remains as the biomass particles produced, but are now substantially the same as at the outlet section of the steam explosion section 308. The cellulose fibers in the collection chamber are separated.

蒸汽爆破单元308中的收集室经配置以收集在蒸汽爆破过程期间来自产生自生物质的任何废气的不凝烃类。The collection chamber in the steam explosion unit 308 is configured to collect non-condensable hydrocarbons from any off-gas generated from the biomass during the steam explosion process.

在蒸汽爆破段308之后,在水分离单元(例如,旋流器单元)中从生物质去除水,并且由松弛的纤维以及分离的木质素和纤维素组成的降低水分含量的生物质可以被馈送到干燥器。After the steam explosion stage 308, water is removed from the biomass in a water separation unit (e.g., a cyclone unit) and a reduced moisture content biomass consisting of flaccid fibers and separated lignin and cellulose can be fed to the dryer.

在实施例中,蒸汽爆破单元308中的一个或多个气体收集箱可以收集在SEP过程期间来自产生自生物质的任何废气的不凝烃类并且将那些不凝烃类与焙烧单元312中收集的任何物质一起送到催化转换器316。In an embodiment, one or more gas collection tanks in steam explosion unit 308 may collect non-condensable hydrocarbons from any off-gas generated from biomass during the SEP process and combine those non-condensable hydrocarbons with those collected in torrefaction unit 312 Anything is sent to catalytic converter 316 together.

在另一实施例中,降低水分含量的浆可以直接从蒸汽爆破单元308去往生物质气化炉314、焙烧单元312或催化转换器316。通常,生物质的颗粒去往焙烧单元312并且接着到生物质气化炉314上。然而,焙烧单元312和生物质气化炉可以组合成单个单元。In another embodiment, the reduced moisture slurry may go directly from steam explosion unit 308 to biomass gasifier 314 , torrefaction unit 312 , or catalytic converter 316 . Typically, particles of biomass go to a torrefaction unit 312 and then onto a biomass gasifier 314 . However, the roasting unit 312 and the biomass gasifier may be combined into a single unit.

可以掺合的生物质类型的一般组合物例如包含:Typical compositions of biomass types that can be blended include, for example:

生物质气化炉314具有反应器,其经配置以使通过蒸汽爆破单元308的两段或更多段分解的生物质颗粒起反应并且那些生物质颗粒随后被馈送到生物质气化炉314的进给区。生物质气化炉314具有高温蒸汽供应输入端和一个或多个加热器,并且在存在蒸汽的情况下,通过蒸汽爆破单元308分解的生物质颗粒在反应器容器中以在生物质气化炉314中小于五秒的滞留时间内在高于700摄氏度的温度下以快速生物质气化反应起反应从而产生至少合成气组分,包含氢气(H2)和一氧化碳(CO),其被馈送到甲醇(CH3OH)合成反应器310。在气化炉314中,传递到由疏松的纤维素纤维、木质素和半纤维素或纤维素纤维、木质素和半纤维素的碎片组成的生物质颗粒的热量不再需要渗透木质素和半纤维素层以到达纤维。在一些实施例中,快速生物质气化反应在高于700摄氏度的温度下进行以确保在气化反应期间形成最少量焦油。因此,700度的起始温度但低于950度可能是生物质气化炉操作的明显范围。使所有生物质气化更彻底且更容易。The biomass gasifier 314 has a reactor configured to react the biomass particles decomposed by the two or more stages of the steam explosion unit 308 and those biomass particles are then fed into the biomass gasifier 314 feed area. The biomass gasifier 314 has a high-temperature steam supply input and one or more heaters, and in the presence of steam, the biomass particles decomposed by the steam explosion unit 308 are in the reactor vessel to be released in the biomass gasifier 314 reacts in a rapid biomass gasification reaction at temperatures above 700 degrees Celsius with a residence time of less than five seconds to produce at least a syngas component, comprising hydrogen (H2) and carbon monoxide (CO), which is fed to methanol ( CH3OH) synthesis reactor 310. In the gasifier 314, the heat transferred to the biomass particles consisting of loose cellulose fibres, lignin and hemicellulose or fragments of cellulose fibres, lignin and hemicellulose no longer needs to penetrate the lignin and hemicellulose Cellulose layer to reach the fibers. In some embodiments, the fast biomass gasification reaction is performed at a temperature above 700 degrees Celsius to ensure a minimum amount of tar is formed during the gasification reaction. Therefore, a starting temperature of 700 degrees but below 950 degrees may be an obvious range for biomass gasifier operation. More complete and easier gasification of all biomass.

生物质气化炉314可以具有到以生物质颗粒的快速气化滞留时间(生物质颗粒的0.1秒到10秒且优选地少于一秒的快速气化滞留时间)流过反应器设计的颗粒以及流过辐射热反应器的反应气体的辐射热传递,并且来自辐射热反应器的表面以及在流动中夹带的颗粒的主要辐射热将颗粒和所得气体加热到大体上超过700摄氏度且优选地至少1200℃的温度,以产生包含一氧化碳和氢气的合成气组分,并且将所产生的甲烷保持在退出制品、退出制品中残留的最小焦油以及所产生的炉灰的组分组成的<1%的水平下。在一些实施例中,用于生物质气化的温度范围为高于800摄氏度到1400摄氏度。The biomass gasifier 314 may have particles designed to flow through the reactor with a fast gasification residence time of the biomass particles (0.1 seconds to 10 seconds and preferably less than one second fast gasification residence time of the biomass particles). and radiant heat transfer of the reaction gas flowing through the radiant thermal reactor, and the predominant radiant heat from the surfaces of the radiant thermal reactor and the particles entrained in the flow heats the particles and resulting gas to substantially more than 700 degrees Celsius and preferably at least A temperature of 1200°C to produce a syngas composition comprising carbon monoxide and hydrogen and to keep the methane produced at <1% of the component composition of exiting products, minimal tar residue in exiting products, and ash produced level down. In some embodiments, the temperature range for biomass gasification is greater than 800 degrees Celsius to 1400 degrees Celsius.

参考图2,设备使用三种方式的任何组合以产生用于甲醇生产的合成气。合成气可以是一氧化碳和氢气的混合物,其可以转换成适用作化学品原料、燃料和溶剂的大量有机化合物。例如,生物质气化炉314使生物质在足够高的温度下气化以消除在产生氢气和一氧化碳以用于甲醇生产时对催化剂的需要。Referring to Figure 2, the plant uses any combination of the three approaches to generate syngas for methanol production. Syngas can be a mixture of carbon monoxide and hydrogen, which can be converted into a wide range of organic compounds suitable as chemical feedstocks, fuels and solvents. For example, biomass gasifier 314 gasifies biomass at a temperature high enough to eliminate the need for a catalyst in producing hydrogen and carbon monoxide for methanol production.

生物质气化用来将生物质的复杂烃类分解成更简单的气态分子,主要是氢气、一氧化碳和二氧化碳。还形成一些矿物炉灰和焦油,以及甲烷、乙烷、水和其它组分。初级制品的的混合物根据所使用的生物质原料的类型和所使用的气化方法而改变。Biomass gasification is used to break down the complex hydrocarbons of biomass into simpler gaseous molecules, mainly hydrogen, carbon monoxide and carbon dioxide. Some mineral ash and tars are also formed, as well as methane, ethane, water and other components. The mixture of primary products varies according to the type of biomass feedstock used and the gasification method used.

生物质气化炉随后是气体净化区段以清洁退出生物质气化炉314的炉灰、硫、水和来自合成气流的其它污染物。合成气接着被压缩到用于甲醇合成所需的适当压力。来自蒸汽甲烷转化炉327的其它合成气可以连接压缩段的上游或下游。The biomass gasifier is followed by a gas cleaning section to clean the ash, sulfur, water and other contaminants from the syngas stream exiting the biomass gasifier 314 . The synthesis gas is then compressed to the appropriate pressure required for methanol synthesis. Additional syngas from steam methane reformer 327 may be connected upstream or downstream of the compression section.

来自气化炉和蒸汽甲烷转化炉327的H2和CO的合成气体被送到公共输入端至一个或多个甲醇合成反应器。通过控制系统从监测设备接收对退出生物质气化炉314和蒸汽甲烷转化炉327的合成气的组合物的分析并使得优化对甲醇合成的比例,可以优化氢气与一氧化碳的精确比例。通过一个或多个甲醇合成反应器产生的甲醇接着在甲醇至汽油的处理中进行处理。The synthesis gas of H2 and CO from the gasifier and steam methane reformer 327 is sent to a common input to one or more methanol synthesis reactors. The exact ratio of hydrogen to carbon monoxide can be optimized by the control system receiving an analysis of the composition of the syngas exiting the biomass gasifier 314 and steam methane reformer 327 from the monitoring equipment and allowing the ratio to methanol synthesis to be optimized. Methanol produced by one or more methanol synthesis reactors is then processed in a methanol-to-gasoline process.

在集成设备中产生的液体燃料可以是汽油或其它,例如柴油、喷气燃料或一些醇类。The liquid fuel produced in the integrated plant can be petrol or other such as diesel, jet fuel or some alcohols.

因此,生物质气化炉314和SMR327两者可以供应合成气组分到下游有机液体制品合成反应器,例如甲醇合成反应器310。接着甲醇供应到甲醇至汽油处理以形成高品质且高辛烷值的汽油。甲醇也可以供应到其它液化燃料处理,包含喷气燃料、DME、汽油、柴油和混合酒精。Thus, both biomass gasifier 314 and SMR 327 may supply syngas components to a downstream organic liquid product synthesis reactor, such as methanol synthesis reactor 310 . Methanol is then supplied to methanol-to-gasoline processing to form high-quality, high-octane gasoline. Methanol can also be supplied to the processing of other liquefied fuels, including jet fuel, DME, gasoline, diesel and blended alcohols.

图4A到图4C示出了具有通过木质素围绕并粘结在一起的纤维素纤维的纤维束的实例生物质切屑451的不同放大水平。4A-4C illustrate different magnification levels of an example biomass chip 451 having fiber bundles of cellulose fibers surrounded and bonded together by lignin.

图4D示出了爆破成生物质细颗粒453的实例生物质切屑,包含第一生物质切屑451。FIG. 4D shows example biomass chips, including first biomass chips 451 , exploded into biomass fines 453 .

图4E示出了具有被磨损的或部分地分离成个别纤维的一束纤维的生物质切屑451。Figure 4E shows a biomass chip 451 with a bundle of fibers abraded or partially separated into individual fibers.

图5示出了经配置以产生包含合成气体产物的化学制品的辐射热化学反应器的实施例的流动示意图。多外壳辐射热化学反应器514包含具有环形腔的耐火容器534,环形腔具有内壁。辐射热化学反应器514具有由实心材料制成的两个或更多个辐射管536。一个或多个辐射管536定位在带耐火内衬的容器534的腔内部。5 shows a flow schematic diagram of an embodiment of a radiant thermochemical reactor configured to produce chemicals comprising synthesis gas products. The multi-shell radiant thermochemical reactor 514 comprises a refractory vessel 534 having an annular cavity with an inner wall. The radiant thermochemical reactor 514 has two or more radiant tubes 536 made of solid material. One or more radiant tubes 536 are positioned inside the cavity of the refractory lined vessel 534 .

发热的热源538对管536的空间内部加热。因此,每个辐射管536用在管536的每个末端处的发热的热源538(例如,蓄热式燃烧器或燃气燃烧器)从内部加热。每个辐射管536通过管536的每个末端处的热量插入口以及可能地通过位于两个末端之间的一个或多个热量插入口用火和来自燃烧器的气体从内部加热。一个或多个天然气燃气燃烧器538的火焰和经加热气体充当发热的热源,其在900℃与1800℃之间的温度下供应到多个辐射管并且连接到辐射管536的两个末端。每个管536可以由SiC或其它类似材料制成。The exothermic heat source 538 heats the interior of the space of the tube 536 . Thus, each radiant tube 536 is internally heated with exothermic heat sources 538 (eg, regenerative burners or gas burners) at each end of the tube 536 . Each radiant tube 536 is internally heated with fire and gases from the burners through heat inserts at each end of the tube 536 and possibly through one or more heat inserts located between the two ends. The flame of one or more natural gas gas burners 538 and the heated gas act as an exothermic heat source, which is supplied to the plurality of radiant tubes and connected to both ends of the radiant tubes 536 at a temperature between 900°C and 1800°C. Each tube 536 may be made of SiC or other similar material.

一个或多个进给管线542将生物质和反应气体供应到化学反应器514的顶部或上部部分中。用于生物质颗粒和蒸汽的进给管线542在用于在内部加热的辐射管536的带耐火内衬的容器534中的入口点下方进入。进给管线112经配置以将包含1)生物质颗粒、2)反应气体、3)蒸汽、4)热传递辅助颗粒、或5)上述四种中的任一种的化学反应物供应到辐射热化学反应器中。通过辐射热促进的化学反应在具有内部火的多个辐射管536外部进行。通过辐射热促进的化学反应在带耐火内衬的容器534的腔的内壁以及一个或多个辐射管536中的每一个的外壁内进行。One or more feed lines 542 supply biomass and reaction gases into the top or upper portion of the chemical reactor 514 . Feed lines 542 for biomass pellets and steam enter below entry points in refractory lined vessel 534 for internally heated radiant tubes 536 . Feed line 112 is configured to supply chemical reactants comprising 1) biomass particles, 2) reactant gases, 3) steam, 4) heat transfer assist particles, or 5) any of the four above to the radiant heat in the chemical reactor. Chemical reactions facilitated by radiant heat take place outside the plurality of radiant tubes 536 with internal fires. Chemical reactions facilitated by radiant heat take place within the inner walls of the cavity of the refractory lined vessel 534 and the outer walls of each of the one or more radiant tubes 536 .

化学反应可以是包含1)生物质气化(CnHm+H2O→CO+H2+H2O+X)以及2)其它类似烃类分解反应中的一个或多个的吸热反应,其使用辐射热在辐射热化学反应器514中进行。蒸汽(H2O)与炭的摩尔比在1:1到1:4的范围内,并且温度足够高以在不存在催化剂的情况下进行化学反应。The chemical reaction may be an endothermic reaction involving one or more of 1) biomass gasification (CnHm+H2O→CO+H2+H2O+X) and 2) other similar hydrocarbon decomposition reactions using radiant heat at radiative The thermochemical reactor 514 is carried out. The molar ratio of steam (H2O) to char is in the range of 1:1 to 1:4, and the temperature is high enough to carry out the chemical reaction in the absence of a catalyst.

至辐射热反应器设计中的用作原材料的生物质颗粒具有以下有利效果:通过更有效地将辐射热传递到气体夹带的颗粒而提高并且能够维持超过1200摄氏度的工艺气体温度、对于给定量的生物质进给提高产生一氧化碳和氢气的合成气组分的气化炉良率、以及经由减少焦油和C2+烯烃的产生而改进工艺卫生。用于辐射热反应器的控制系统使从反应器的表面传递的辐射热匹配生物质颗粒的流动速率以产生以上优势。The use of biomass particles as raw material in radiant thermal reactor designs has the beneficial effect of increasing and being able to maintain process gas temperatures in excess of 1200 degrees Celsius for a given amount of Biomass feeding increases gasifier yield of syngas components producing carbon monoxide and hydrogen, and improves process hygiene through reduced production of tars and C2+ olefins. The control system for the radiant heat reactor matches the radiant heat transferred from the surface of the reactor to the flow rate of the biomass particles to yield the above advantages.

控制系统控制燃气燃烧器538以供应热能到化学反应器514,从而帮助使得化学反应器产生的辐射热具有高热通量。化学反应器514的内表面经对准以1)吸收并再发射辐射能量、2)高度反射辐射能量、以及3)这些的任何组合,从而维持附件超高热通量化学反应器514的操作温度。因此,耐火容器的腔内壁和一个或多个管536中的每一个的外壁发射辐射热能源到(例如)生物质颗粒以及在给定管536的外壁与耐火容器的内壁之间存在的任何其它热传递辅助颗粒。因此,耐火容器经由管536从沿着耐火容器的顶部和底部定位的燃烧器538吸收或反射浓缩能源以引起通过热辐射和反射的能源传输,从而将热通量大体上输送到化学反应器内部的生物质颗粒、热传递辅助颗粒以及反应气体。隔热耐火容器的腔的内壁以及多个管536通过或者吸收辐射并将其再辐射到热传递辅助颗粒或者将入射辐射反射到热传递辅助颗粒而充当辐射分配器。辐射热化学反应器514使用主要通过辐射的热传递而不是对流或传导促进的超高热通量和高温。The control system controls the gas burner 538 to supply thermal energy to the chemical reactor 514, thereby helping to have a high heat flux of the radiant heat generated by the chemical reactor. The interior surfaces of the chemical reactor 514 are aligned to 1) absorb and re-emit radiant energy, 2) highly reflect radiant energy, and 3) any combination of these to maintain the operating temperature of the adjacent ultra-high heat flux chemical reactor 514. Thus, the inner cavity walls of the refractory vessel and the outer walls of each of the one or more tubes 536 emit radiant heat energy to, for example, biomass particles and any other material that exists between the outer walls of a given tube 536 and the inner walls of the refractory vessel. Heat transfer assist particles. Accordingly, the refractory vessel absorbs or reflects concentrated energy via tubes 536 from burners 538 positioned along the top and bottom of the refractory vessel to cause energy transfer through thermal radiation and reflection, thereby delivering heat flux generally to the interior of the chemical reactor Biomass particles, heat transfer auxiliary particles and reaction gases. The inner walls of the cavity of the insulated refractory vessel and the plurality of tubes 536 act as radiation distributors by either absorbing radiation and reradiating it to the heat transfer aid particles or reflecting incident radiation to the heat transfer aid particles. The radiant thermochemical reactor 514 uses ultra-high heat flux and high temperature facilitated by heat transfer primarily by radiation rather than convection or conduction.

煤炭颗粒上通常使用的对流生物质气化炉通常最多到达5到10kW/m^2的热通量。高辐射热通量生物质气化炉将使用明显更大的热通量,是在对流促进的生物质气化炉中存在的那些量的至少三倍(即,高于25kW/m^2)。通常,在高温下(壁温度>950摄氏度)使用辐射,可以用适当地设计的反应器实现更高的通量(高于80kW/m^2的高热通量)。在一些情况下,高热通量可以是100kW/m^2到250kW/m^2。Convective biomass gasifiers commonly used on coal pellets typically achieve a heat flux of at most 5 to 10 kW/m^2. High radiant heat flux biomass gasifiers will use significantly greater heat fluxes, at least three times those present in convection-facilitated biomass gasifiers (i.e. above 25kW/m^2) . Typically, higher fluxes (high heat fluxes above 80 kW/m^2) can be achieved with properly designed reactors using radiation at high temperatures (wall temperatures >950 °C). In some cases, the high heat flux may be 100 kW/m^2 to 250 kW/m^2.

接下来,可以在通过计算机执行的计算机可执行指令的一般情境中(例如,程序模块)描述用于控制系统的各种算法和方法。通常,程序模块包含例程、程序、对象、组件、数据结构等,其执行特定任务或实施具体抽象数据类型。所属领域的技术人员可以将本文中的描述和/或图实施为计算机可执行指令,其可以在下文论述的任何形式的计算机可读媒体上实施。一般来说,程序模块可以实施为软件指令、电子硬件的逻辑块以及两者的组合。软件部分可以存储在机器可读媒体上并且以任何数目的编程语言编写,例如Java、C++、C等。机器可读媒体可以是硬盘驱动器、外部驱动器、DRAM、磁带机、存储条等但是不涵盖瞬时信号。因此,可以唯一地使用硬件逻辑、硬件逻辑与软件交互作用或仅使用软件构造算法和控制系统。Next, various algorithms and methods for controlling the system may be described in the general context of computer-executable instructions (eg, program modules) being executed by a computer. Generally, program modules include routines, programs, objects, components, data structures, etc. that perform particular tasks or implement concrete abstract data types. Those skilled in the art may implement the descriptions and/or figures herein as computer-executable instructions, which may be embodied on any form of computer-readable media discussed below. Generally, program modules may be implemented as software instructions, logical blocks of electronic hardware, or combinations of both. The software portion can be stored on a machine-readable medium and written in any number of programming languages, such as Java, C++, C, etc. The machine-readable medium can be a hard drive, external drive, DRAM, tape drive, memory stick, etc. but does not cover transitory signals. Thus, algorithms and control systems can be constructed using hardware logic exclusively, hardware logic interacting with software, or software only.

然而,本设计的一些特定实施例已经展示本设计不限于这些实施例。例如,来自各种设备过程的回收废热可以用来预热燃烧空气或可以用于其它类似加热构件。蓄热式气体燃烧器或常规燃烧器可以用作锅炉的热源。蒸汽甲烷转化可以是/包含SHR(蒸汽烃类转化炉),其使包含烃类(烷烃、烯烃、炔烃、芳族物、呋喃、酚类、甲酸、酮类、醛类、乙醚等)以及氧合物的短链烃类(<C20)分裂成合成气组分。本设计应被理解为不受本文所述的具体实施例限制,而是仅通过所附权利要求书的范围来限制。However, some specific embodiments of the design have shown that the design is not limited to these embodiments. For example, recovered waste heat from various plant processes can be used to preheat combustion air or can be used for other similar heating components. Regenerative gas burners or conventional burners can be used as the heat source for the boiler. Steam methane reforming may be/comprise SHR (Steam Hydrocarbon Reformer) which converts hydrocarbons (alkanes, alkenes, alkynes, aromatics, furans, phenols, formic acid, ketones, aldehydes, ethers, etc.) and Oxygenated short-chain hydrocarbons (<C20) split into syngas components. The design should be understood not to be limited by the particular embodiments described herein, but only by the scope of the appended claims.

Claims (20)

1., in order to produce an integrated equipment for synthesis gas from living beings, it comprises:
Steam blasting unit, it has to receive the input cavity that living beings chip is used as raw material, one or more steam supply input, and in order to living beings described in pretreatment for follow-up two sections that are fed to biomass gasifying furnace or more sections, wherein said two sections or more sections use the heat being applied to described living beings, the combination of pressure and moisture is with the fine particulate form making described living beings become humidity, the overall structure of the living beings chip received described in wherein said two sections or more sections are configured to decompose at least in part, method be by application from the first steam supply input steam with start to be reduced in lignin and from the cellulose fibre of described living beings hemicellulose between bonding and the moisture of the living beings chip received described in improving, and the steam then applied in the segment from least atmospheric pressure 14 times of the second steam supply input heats any gas of described living beings inside existence and fluid and pressurizes, wherein at the outlet opening place to described two sections or more sections, via the reduction of blood pressure in high-speed of described living beings described in internal division through the described overall structure of Pressed bio matter, described living beings wherein after division produce and are less than 70 micron thickness and the fine particulate form being less than the average-size of 500 microns long from described section of having of leaving, and the living beings fine grained of those humidities produced is fed to the feeding district of described biomass gasifying furnace subsequently, and
Wherein said biomass gasifying furnace has reactor vessel, it is configured to the living beings of the fine particulate form of described humidity are reacted, the living beings of the fine particulate form of described humidity have the granular size of reduction and the overall surface area increased owing to the division by described steam blasting unit compared to the living beings chip received described in described input cavity, wherein said biomass gasifying furnace has the 3rd steam supply input and one or more thermal source, and when there is described steam, the living beings of described fine particulate form react with quick bio matter gasification reaction thus produce at least synthesis gas components in described reactor vessel, comprise hydrogen (H2) and carbon monoxide (CO), wherein said steam blasting unit and described biomass gasifying furnace are parts for described integrated equipment.
2. integrated equipment according to claim 1, described two sections of wherein said steam blasting unit or more sections comprise at least hot water processing section and steam blasting section, wherein said hot water processing section has the described input cavity receiving described living beings chip, and described first steam supply input is configured to be applied to by low-pressure saturated steam under higher than 60 degrees Celsius but lower than the high temperature of 145 degrees Celsius under the pressure of about normal pressure PSI in the container containing described living beings chip, thus start to decompose, the living beings chip received described in hydration process also softens, wherein the high temperature of one group of temperature sensor to the described living beings chip received provides feedback, and wherein control system is configured to holdup time of keeping described living beings chip to stop in described hot water processing section 8 to 20 minutes, described holdup time long enough soaked into described living beings chip with moisture before being moved out to described steam blasting section in described living beings.
3. integrated equipment according to claim 2, wherein said hot water processing section will be fed to described steam blasting section through softening and that moisture improves described living beings chip via screwfeed system, described steam blasting section maintains the pressure of 10 to 30 times of the pressure existed in described hot water processing section by described control system under, and described steam blasting section raises the internal pressure of the described moisture of described living beings and the cell of the described living beings of formation further.
4. integrated equipment according to claim 1, wherein after described hot water processing section, described in chip formation through softening living beings through 1) extruding and 2) and compress be anyly combined into plug form, it is then fed to continous way conveying worm system, the described living beings in plug form move in steam blasting section by described system, wherein in described continous way conveying worm system, the described living beings in described plug form prevent from the back-pressure of the blowback of the high steam under at least ten four times of the normal pressure existed in comfortable described steam blasting section to affect described hot water processing section, and
The described synthesis gas components comprising described hydrogen (H2) and described carbon monoxide (CO) wherein from described biomass gasifying furnace is fed to downstream methanol synthesis reactor to form methyl alcohol, and described reactor is also a part for described integrated equipment.
5. integrated equipment according to claim 4, wherein said steam blasting section is coupled to refining section, described refining section has one or more blade, its be configured to described through Pressed bio matter to be left by described outlet opening described steam blasting section to maintain lower than pressure in described steam blasting section 1/3rd pressure under purge pipeline before mechanically stir described through Pressed bio matter so that through Pressed bio matter described in internal division, described mechanical agitation wherein in described refining section is configured to make gained living beings of a granular form have the more consistent size distribution of the average-size of described biological particles.
6. integrated equipment according to claim 2, wherein said steam blasting section has one group of temperature and pressure sensor and described control system, wherein said living beings are exposed to and continue between 5 minutes to 20 minutes in the high temperature and high pressure steam from described second steam supply at least 188 degrees Celsius of input and 160PSI, until the integrally-built porous part of living beings described in moisture penetration and all described fluid in described living beings and gas rise to described high pressure, wherein described living beings are fed to described outlet opening by described steam blasting section by conveyer system, the little opening of wherein said outlet opening enters in the pipe under the decompression maintaining 4 to 10 bar, and any internal flow under described high pressure or gas expansion are to split into the fine grained living beings of described humidity by the described overall structure of described living beings in inside.
7. integrated equipment according to claim 1, described two sections of wherein said steam blasting unit or more sections comprise hot water processing section and steam blasting section, wherein said hot water processing section has first group of temperature sensor and control system, it is configured to via described first steam supply input, described steam is applied to described living beings chip at the temperature of the glass transition point higher than described lignin, to soften and to improve the described moisture of described living beings, therefore at least described in described steam blasting section, the described cellulose fibre of living beings can from described living beings at internal division, wherein said hot water processing section is configured to receive described living beings chip, it can comprise leaf, needle, stem skin and bole, and then described control system uses described steam that the described living beings chip in described hot water processing section is heated to above 60 DEG C, be detained the time of 8 to 20 minutes, and then described living beings are delivered to described steam blasting section with other inside, porous zone formation high steam in the described overall structure of biological material described in the cellulose fiber peacekeeping of part hollow, and then make the environmental pressure of the described outlet opening through described steam blasting section decline fast, method is to cause Internal explosions in the pipe by the described overall structure of the described living beings maintained 160 to 450PSI by the described control system in described steam blasting section being stretched under reduced pressure, described living beings are split into living beings fine particle in inside by it, wherein in inside, the described overall structure of the living beings in fibre bundle is split into cellulose fibre, the fragment of lignin and hemicellulose and fragment cause following both: 1) compared to described receive in the living beings of chip formation, the surface area of the described living beings in fine particulate form increases, and 2) structure of the living beings produced in fine particulate form of described gained changes with as the grains of sand instead of as fiber flow.
8. integrated equipment according to claim 1, described two sections of wherein said steam blasting unit or more sections comprise hot water processing section and steam blasting section, wherein at the described outlet opening place of described steam blasting section, once described living beings explosion becomes the fine particulate form of described humidity, then described produced biological particles is owing to steam flash distillation being discharged and the percentage of the content that dries out as steam in purge pipeline, wherein said produced biological particles is then separated by swirl-type filter with moisture, the fine grain described moisture of wherein said living beings is become dry by drier in the exit of purge vessel further, fine grain for described living beings moisture is reduced to by weight lower than 20% by this, the described living beings fine grained with the moisture of reduction is then fed to silo for storage until be ready to be fed to described biomass gasifying furnace by wherein said drier.
9. integrated equipment according to claim 1, wherein steam blasting section is coupled to refining section, described refining section has one or more blade, its be configured to described mechanically stirred before Pressed bio matter leaves described steam blasting section to purge pipeline by described outlet opening described through Pressed bio matter, and described the produced living beings fine grained with the moisture of reduction comprises into cracked, tear, that tear up and any combination and have and be less than 30 micron thickness and the cellulose fibre being less than the average-size of 200 microns long, wherein said produced living beings fine grained is fed to described biomass gasifying furnace for the described quick bio matter gasification reaction in the described reactor vessel of described biomass gasifying furnace to downstream, because they form higher surface-to-volume ratio compared to the described living beings in chip formation received for the living beings of identical amount, this allows higher heat and quality to be delivered to more rapid thermolysis and the gasification of all molecules in described biological material and described living beings.
10. integrated equipment according to claim 2, the described steam blasting section being wherein filled with the high steam be greater than under 14 bar contains discharges outlet, it to be configured to described biological material " explosion " under reduced pressure next section to produce the described living beings in fine particulate form, wherein magnetic filter and air cleanness filter system, coupled to described hot water processing section to guarantee that the described living beings in chip formation eliminated metal fragment and ratchel before entering described hot water processing section, to prevent these metal fragments and ratchel blocking from comprising described part of discharging the described steam blasting unit of outlet, the wherein said living beings in fine particulate form are in the dirty feed line crossing purge vessel of high speed, and 1) the described of described steam blasting section discharge outlet and 2) any one in described feed line locate injection and comprise 1) charge of flowable solids and 2) obstruction that causes to prevent described living beings of the glidant of any one of gas, and other described feed line has the heater coil that arranges around described feed line to maintain the high temperature of the described living beings in fine particulate form thus to help prevent the crystallization of rosin in the described living beings in fine particulate form and resin acid.
11. integrated equipments according to claim 1, it comprises further:
Water separative element, collecting chamber wherein at the outlet section place of steam blasting section is reduced to compared with small particle size in order to collect and is the described living beings of slurry form and is fed to described water separative element, wherein in hydrocyclone unit, removes water from the described living beings in fine particulate form and the described living beings in fine particulate form is fed to drier to be reduced to by weight lower than 20% by the moisture of the described living beings in fine particulate form further; And
Gas wherein containing the organic compound reclaimed from described hydrocyclone unit produced by described steam blasting section is collected and is fed to described biomass gasifying furnace by feed line.
12. 1 kinds in order to produce the method for synthesis gas from the living beings in integrated equipment, it comprises:
The living beings received in chip formation are used as raw material and are fed to biomass gasifying furnace with living beings described in pretreatment in two sections or more sections for follow-up;
By heat in described two sections or more sections, the fine particulate form that the Combination application of pressure and moisture becomes moist to described living beings to make described living beings, steam blasting process wherein in described two sections or more sections decompose at least in part described in the overall structure of the living beings in chip formation that receives, method be the steam that there is low pressure by application with start to be reduced in lignin and from the cellulose fibre of described living beings hemicellulose between bonding and the moisture of the living beings chip received described in improving, and the steam then by application with more high pressure is heated any gas of described living beings inside existence and fluid and pressurizes, the described overall structure of the living beings in chip formation received described in internal division with the reduction of blood pressure in high-speed of the close-burning described living beings via the moisture and reduction with raising, the described living beings being wherein produced as the fine particulate form of described humidity from the steam blasting unit of described two sections or more sections have and are less than 70 micron thickness and the fine particulate form being less than the average-size of 500 microns long, and the living beings fine grained of those humidities produced is fed to the feeding district of described biomass gasifying furnace subsequently, and
Described living beings fine grained is reacted, described living beings fine grained has the granular size of reduction and the overall surface area increased owing to the division by described two sections of the described steam blasting unit in described biomass gasifying furnace or more sections compared to the described living beings in chip formation being used as raw material received, wherein deposit in the case of steam in described biomass gasifying furnace, the described particle of the described living beings produced by described steam blasting unit reacts to produce at least synthesis gas components with quick bio matter gasification reaction, comprise hydrogen (H2) and carbon monoxide (CO), wherein said steam blasting unit and described biomass gasifying furnace are parts for described integrated equipment.
13. methods for described integrated equipment according to claim 12, wherein said two sections or more sections comprise hot water processing section and steam blasting section, the low-pressure steam soaked into moisture is applied in the container of the described living beings in chip formation of accommodation by wherein said hot water processing section under the pressure of about normal pressure PSI under higher than 60 degrees Celsius but lower than the high temperature of 145 degrees Celsius, thus start to decompose, the living beings in chip formation received described in hydration process also softens, the described chip of wherein said living beings stops considerable 10 to 15 minutes to soak into moisture in described hot water processing section, and wherein said hot water processing section will be fed to described steam blasting section through softening and that moisture improves living beings chip, described steam blasting section under 160 pressure to 450PSI and temperature maintain between 160 to 270 DEG C.
14. methods for described integrated equipment according to claim 12, it comprises further:
Under 160 to 450PSI through the described living beings of pressurization to be left by outlet opening described steam blasting section to maintain lower than pressure in described steam blasting section 1/3rd pressure under purge pipeline before mechanically stir the described living beings in described steam blasting section so that in the described living beings of internal division through pressurizeing under 160 to 450PSI, the described mechanical agitation wherein in described refining section is configured to make gained living beings of a granular form have the more consistent size distribution of the average-size of described biological particles with the one or more blades in refining section.
15. methods for described integrated equipment according to claim 13, wherein after described hot water processing section, described in chip formation through softening living beings through 1) extruding and 2) any combination of compressing, it is then fed to conveyer system, described living beings move in described steam blasting section by described system, wherein in described conveyer system, described living beings prevent from the back-pressure of the blowback of the high steam existed in comfortable described steam blasting section to affect described hot water processing section.
16. methods for described integrated equipment according to claim 12, described two sections of wherein said steam blasting unit or more sections comprise hot water processing section and steam blasting section, steam is applied to described living beings by wherein said hot water processing section, use described steam be detained 8 to 20 minutes time chien shih its higher than 60 DEG C, so that softening and raising moisture, and then described living beings are delivered to the described steam blasting section of described living beings with the living beings in chip formation described in internal division, wherein said living beings are exposed to the sufficient time section continuing 3 to 15 minutes in high temperature and high pressure steam living beings between 160 to 450 pounds/square inch, high steam is formed with other inside, porous zone in the described overall structure of biological material described in the cellulose fiber peacekeeping of part hollow, and then make the pressure in the exit in described steam blasting section decline fast, method be by the described overall structure of the described living beings between 160 to 450 pounds/square inch is stretched into be less than described 160 to 450 pounds/square inch 1/3rd decompression under pipe in cause Internal explosions, described living beings are split into living beings fine particle in inside by it.
17. methods for described integrated equipment according to claim 14, wherein said living beings pass through the fine particulate form using the described outlet opening explosion of two or more pressure drops a series of through controlling of different-diameter section instead of the described steam blasting section of single continuous print diameter pressure drop to become described humidity, and wherein once described living beings explosion becomes the fine particulate form of described humidity, described produced biological particles is owing to steam flash and be discharged as steam and lose the percentage of described moisture, the fine grain moisture of wherein said living beings becomes dry further by flash dryer, fine grain for living beings described moisture is reduced to by weight lower than 20% by this.
18. methods for described integrated equipment according to claim 14, wherein said the produced living beings fine grained with the moisture of reduction comprises into cracked, tear, that tear up and any combination and have and be less than 50 micron thickness and the cellulose fibre being less than the average-size of 200 microns long, wherein said produced living beings fine grained is fed to described biomass gasifying furnace for the described quick bio matter gasification reaction in the reactor of described biomass gasifying furnace to downstream, because they form higher surface-to-volume ratio compared to the described living beings in chip formation received for the living beings of identical amount, this allows higher heat and quality to be delivered to more rapid thermolysis and the gasification of all molecules in described biological material and described living beings.
19. methods for described integrated equipment according to claim 12, it comprises further:
Collect in the discharge exit of described steam blasting unit and be reduced to compared with small particle size and described living beings in slurry form and be fed to water separative element, wherein in hydrocyclone unit, remove water from the described living beings in fine particulate form and the described living beings in fine particulate form are fed to flash dryer to be reduced to the described moisture of the described living beings in fine particulate form by weight lower than 20% further lower than the moisture of the described reduction of 40% by weight.
20. methods according to claim 19, wherein after described hot water processing section, described in chip formation through softening living beings through 1) extruding and 2) and compress be anyly combined into plug form, it is then fed to continous way conveying worm system, the described living beings in plug form move in described steam blasting section by described system, wherein in described continous way conveying worm system, the described living beings in described plug form prevent from the back-pressure of the blowback of the high steam existed in comfortable described steam blasting section to affect described hot water processing section, and
The described synthesis gas components comprising hydrogen (H2) and carbon monoxide (CO) wherein from described biomass gasifying furnace is fed to downstream methanol synthesis reactor to form methyl alcohol, and described reactor is also a part for described integrated equipment.
CN201480027130.2A 2013-05-14 2014-05-14 Steam explosion methods before gasification Pending CN105377416A (en)

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US14/276,719 US9447326B2 (en) 2012-06-22 2014-05-13 Pretreatment of biomass using steam explosion methods before gasification
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107312808A (en) * 2016-04-26 2017-11-03 财团法人食品工业发展研究所 Method for producing cellooligosaccharide
CN107880935A (en) * 2017-11-07 2018-04-06 武汉凯迪工程技术研究总院有限公司 Biomass is made up to the technique and its system of synthesis gas of gas blast

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10287508B2 (en) 2017-04-07 2019-05-14 Sundrop Fuels, Inc. Multi-purpose application of the second stage of a 2-stage bio-reforming reactor system for reforming bio-syngas, natural gas and process recycle streams
US10273415B2 (en) 2017-04-07 2019-04-30 Sundrop Fuels, Inc. Flexible options for utilizing naphtha from a low temperature Fischer-Tropsch process in a plant converting biomass to syncrude or transportation fuels
US10273422B2 (en) 2017-04-07 2019-04-30 Sundrop Fuels, Inc. Integrated biofuels process configurations, employing a 2-stage bio-reforming reactor system, in which renewable carbon content of gasoline and diesel are optimized for value
CA3060626A1 (en) 2017-04-27 2018-11-01 Sundrop Ip Holdings, Llc First stage process configurations in a 2-stage bio-reforming reactor system
SE543000C2 (en) 2018-06-26 2020-09-22 Valmet Oy Method and system for discharging hydrothermally treated lignocellulosic material
EP3696253B1 (en) * 2019-02-12 2021-04-21 Valmet Ab Process for improving structural integrity of hardwood black pellets
FR3095654B1 (en) * 2019-05-03 2022-01-21 Europeenne De Biomasse Steam cracking control to improve the PCI of black pellets
FR3095649B1 (en) * 2019-05-03 2022-09-16 Europeenne De Biomasse Powdery substrate obtained by steam cracking of a biomass without chemical auxiliary and its uses
JP7237267B1 (en) * 2023-01-13 2023-03-10 株式会社日立パワーソリューションズ Foreign matter detection device for wood chips fuel
CN116162502B (en) * 2023-03-16 2025-01-28 中国矿业大学 A system and process for strengthening lignite dehydration by coupling steam explosion with chemical reforming
CN117699895A (en) * 2023-11-23 2024-03-15 四川达兴能源有限责任公司 NaHS and/or Na 2 Coking ammonia distillation system with S substituted NaOH and ammonia distillation method thereof

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5769934A (en) * 1997-01-15 1998-06-23 Fmc Corporation Method for producing microcrystalline cellulose
US8057639B2 (en) * 2008-02-28 2011-11-15 Andritz Inc. System and method for preextraction of hemicellulose through using a continuous prehydrolysis and steam explosion pretreatment process
US8236535B2 (en) * 2008-04-30 2012-08-07 Xyleco, Inc. Processing biomass
US20100242352A1 (en) * 2009-06-09 2010-09-30 Sundrop Fuels, Inc. Systems and methods for reactor and receiver control of flux profile
NL2004898C2 (en) * 2010-06-16 2011-12-20 Stichting Energie Pyrolysis of lignin.
US8236173B2 (en) * 2011-03-10 2012-08-07 Kior, Inc. Biomass pretreatment for fast pyrolysis to liquids

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
PAK SUI LAM: "《PhD thesis, University of British Columbia, Vancouver, Canada》", 31 May 2011 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107312808A (en) * 2016-04-26 2017-11-03 财团法人食品工业发展研究所 Method for producing cellooligosaccharide
CN107880935A (en) * 2017-11-07 2018-04-06 武汉凯迪工程技术研究总院有限公司 Biomass is made up to the technique and its system of synthesis gas of gas blast

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