CN111908764A - Mechanical vapor recompression drying system and method - Google Patents

Mechanical vapor recompression drying system and method Download PDF

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CN111908764A
CN111908764A CN202010863126.7A CN202010863126A CN111908764A CN 111908764 A CN111908764 A CN 111908764A CN 202010863126 A CN202010863126 A CN 202010863126A CN 111908764 A CN111908764 A CN 111908764A
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sludge
steam
condensed water
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water
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曹俊杰
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Suzhou Xiangyun Energy Saving Technology Co ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/13Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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Abstract

本发明公开了一种机械蒸汽再压缩干燥系统及方法,其包括污泥存储池、污泥注射泵、薄层蒸发干燥器、挤压分条成型机、网带干燥机、干泥仓、蒸汽压缩机、旋风除尘器、水洗除尘器、冷凝水缓冲罐、以及与冷凝水缓冲罐相连且用于抽吸系统空气维持真空并排放不凝气体的真空泵。本发明可节省大量能源消耗及冷却水系统消耗。过程中无废气排放,系统无冷却水系统,节省了冷却塔水份蒸发损失。

Figure 202010863126

The invention discloses a mechanical vapor recompression drying system and method, comprising a sludge storage tank, a sludge injection pump, a thin-layer evaporation dryer, an extrusion slitting machine, a mesh belt dryer, a dry mud silo, a steam A compressor, a cyclone, a water scrubber, a condensate buffer tank, and a vacuum pump connected to the condensate buffer tank and used to suck system air to maintain a vacuum and discharge non-condensable gases. The invention can save a lot of energy consumption and cooling water system consumption. There is no exhaust gas emission in the process, and the system has no cooling water system, which saves the evaporation loss of cooling tower water.

Figure 202010863126

Description

机械蒸汽再压缩干燥系统及方法Mechanical vapor recompression drying system and method

技术领域technical field

本发明涉及污泥干燥技术领域,具体涉及一种机械蒸汽再压缩干燥系统及方法。The invention relates to the technical field of sludge drying, in particular to a mechanical vapor recompression drying system and method.

背景技术Background technique

机械式蒸汽再压缩(Mechanical Vapor Recom-pression)系统,简称MVR系统,是一种新型高效节能系统。MVR蒸发技术节能效果显著,与多效蒸发技术相比,MVR系统全部回收了二次蒸汽的潜热,热效率一般相当于5-10效蒸发器。Mechanical vapor recompression (Mechanical Vapor Recom-pression) system, referred to as MVR system, is a new type of high-efficiency and energy-saving system. Compared with the multi-effect evaporation technology, the MVR system fully recovers the latent heat of the secondary steam, and the thermal efficiency is generally equivalent to a 5-10-effect evaporator.

在干燥和蒸发浓缩等工业领域,会产生大量的水蒸汽。水蒸汽携带的能量中绝大部分为潜热,显热仅为很小一部分。机械式蒸汽再压缩系统,有效回收了水蒸汽的潜热,从而达到节能降耗的目的。其工作原理是对蒸发器产生的蒸汽,经机械式蒸汽压缩机作用后,温度、压力、焓值均得到提升,返回蒸发器作为加热的热源,补充液体蒸发需要吸收的热能并维持蒸发温度。系统本身能基本达到热平衡,新鲜蒸汽仅用于补充系统热损失和进出料热焓,从而大幅度减少蒸发器对外来新鲜蒸汽的消耗,达到了降低能耗的目的。MVR用于固体干燥领域的应用较少,传热温差小、干燥时间长、机械传动能耗大、系统需要密封、需要高性能压缩机等均是其应用的制约因素。In industrial fields such as drying and evaporative concentration, a large amount of water vapor is generated. Most of the energy carried by water vapor is latent heat, and sensible heat is only a small part. The mechanical vapor recompression system effectively recovers the latent heat of water vapor, thereby achieving the purpose of saving energy and reducing consumption. Its working principle is that the temperature, pressure and enthalpy value of the steam generated by the evaporator are increased after being acted by the mechanical steam compressor, and the steam is returned to the evaporator as a heating heat source to supplement the heat energy that needs to be absorbed by the liquid evaporation and maintain the evaporation temperature. The system itself can basically achieve thermal balance, and the fresh steam is only used to supplement the heat loss of the system and the enthalpy of incoming and outgoing materials, thereby greatly reducing the consumption of external fresh steam by the evaporator and achieving the purpose of reducing energy consumption. The application of MVR in the field of solid drying is less, the small heat transfer temperature difference, the long drying time, the large energy consumption of mechanical transmission, the need for sealing the system, and the need for high-performance compressors are all restricting factors for its application.

常见的固体蒸汽干燥技术多采用间接的传导换热或直接的对流换热方式。间接的传导换热常见于空心桨叶机、转盘式干燥器、转鼓式干燥器、夹壁式干燥器等。直接的对流换热常见于过热蒸汽干燥和热风干燥等。它们均需要大温差和机械搅拌或强制对流方式来强化换热。Common solid steam drying technologies mostly use indirect conduction heat transfer or direct convection heat transfer. Indirect conduction heat transfer is common in hollow blade dryers, rotary disk dryers, rotary drum dryers, sandwich wall dryers, etc. Direct convection heat transfer is common in superheated steam drying and hot air drying. They all require large temperature differences and mechanical agitation or forced convection to enhance heat exchange.

研究表明:固体中水份主要是自由水、间隙水、表层水和化学结合水。依这些水份的蒸发干燥过程中,蒸发速率分为“恒速段”、“降速段”和“最后阶段”。一般污泥含水率低于65%左右后,“恒速段”结束进入较难和更耗能的“降速段”干燥蒸发。The research shows that the water in the solid is mainly free water, interstitial water, surface water and chemically bound water. According to the evaporation and drying process of these moisture, the evaporation rate is divided into "constant speed section", "speed reduction section" and "final stage". Generally, when the moisture content of the sludge is lower than about 65%, the "constant speed section" ends and enters the more difficult and more energy-consuming "speed reduction section" for drying and evaporation.

南京航空航天大学周雷《基于蒸汽再压缩技术的低温干燥系统设计与节能分析》表明,低温干燥过程,理论上系统能耗随着蒸发温度与压缩机压比的降低而不断下降;与相同条件下的常规低温干燥系统相比,基于蒸汽再压缩技术的低温干燥系统的能耗仅为常规低温回热干燥系统的7.7%。MVR技术应用基于节能原理和现有技术限制,需要低压比压缩和小温差换热,导致干燥时间过长、强化换热的机械搅拌和传动能耗过高而降低了MVR节能效果。同时,过高的蒸发温度导致更多的系统热损耗,为了系统热量平衡而增大对系统补充热量,导致节能效果进一步降低。同时,可实现高压比的螺杆蒸汽压缩机目前市场应用并不常见,也是导致MVR干燥节能应用困难的原因之一。为保证干燥效果还需控制好一定的干燥速度,把MVR技术与真空低温干燥技术相结合是MVR干燥的发展方向,但进入“降速段”后,蒸发速率还是不尽人意。Zhou Lei, Nanjing University of Aeronautics and Astronautics, "Design and Energy-Saving Analysis of Low-Temperature Drying System Based on Vapor Recompression Technology" shows that in the low-temperature drying process, theoretically, the energy consumption of the system decreases with the decrease of the evaporation temperature and the compressor pressure ratio; with the same conditions Compared with the conventional low-temperature drying system under low temperature, the energy consumption of the low-temperature drying system based on vapor recompression technology is only 7.7% of that of the conventional low-temperature regenerative drying system. The application of MVR technology is based on the principle of energy saving and the limitation of existing technology, which requires low pressure ratio compression and small temperature difference heat exchange, which leads to long drying time, high energy consumption of mechanical stirring and transmission to strengthen heat exchange, and reduces the energy saving effect of MVR. At the same time, the excessively high evaporation temperature leads to more heat loss of the system, and the supplementary heat to the system is increased to balance the heat of the system, resulting in a further reduction of the energy saving effect. At the same time, the current market application of screw steam compressors that can achieve high pressure ratio is not common, which is also one of the reasons for the difficulty in the application of MVR drying and energy saving. In order to ensure the drying effect, it is necessary to control a certain drying speed. The combination of MVR technology and vacuum low-temperature drying technology is the development direction of MVR drying, but after entering the "speed reduction section", the evaporation rate is still unsatisfactory.

过热蒸汽干燥是指利用过热蒸汽直接与被干燥的物料接触而去除其内部水分的一种新型干燥方式。在相同的温度下,过热蒸汽和热空气相比,由于过热蒸汽存在潜热,所以单位质量的过热蒸汽所携带热量远大于热空气,且用过热蒸汽干燥固体时,由于固体表面是水分蒸发到过热蒸汽,没有扩散阻力。过热蒸汽干燥的速度和过热蒸汽的温度也是相关的。福建农林大学卢烨的《土豆的过热蒸汽与真空联合干燥》研究和实验表明,低温过热蒸汽在土豆的干燥过程中也能到达比较理想的干燥速度。Superheated steam drying refers to a new drying method that uses superheated steam to directly contact the material to be dried to remove its internal moisture. At the same temperature, compared with hot air, superheated steam has latent heat, so the heat per unit mass of superheated steam is much greater than that of hot air, and when superheated steam is used to dry solids, because the surface of the solid is water evaporated to superheated Steam, there is no diffusion resistance. The speed of superheated steam drying and the temperature of the superheated steam are also related. The research and experiment of "Superheated Steam and Vacuum Combined Drying of Potatoes" by Lu Ye of Fujian Agriculture and Forestry University shows that low-temperature superheated steam can also achieve an ideal drying speed in the drying process of potatoes.

干燥过程中污染物会随着蒸发过程进入二次蒸汽的冷凝水。南昌航空大学官勇的《城市污泥过热蒸汽干燥冷凝液特性研究》和山东大学洪永强的《高盐有机废水蒸馏压缩过程污染物迁移研究》表明,低温蒸发进入二次蒸汽冷凝水的污染物主要是醇类有机物和氨等,无机盐类含量极低。而高温蒸发过程,污染物成分复杂,污染量更多。传统的高温污泥蒸发,冷凝水需要再次进入污水厂处理后才能达标排放或回用。During the drying process, the pollutants will enter the condensed water of the secondary steam with the evaporation process. "Research on the Characteristics of Urban Sludge Superheated Steam Drying Condensate" by Guan Yong of Nanchang Aviation University and "Study on the Migration of Contaminants in the Distillation and Compression Process of High-Salt Organic Wastewater" by Hong Yongqiang of Shandong University show that the main pollutants entering the secondary steam condensate by low temperature evaporation are mainly It is organic alcohol and ammonia, etc., and the content of inorganic salts is extremely low. In the high-temperature evaporation process, the pollutant composition is complex and the amount of pollution is more. The traditional high-temperature sludge evaporates, and the condensed water needs to enter the sewage treatment plant again before it can be discharged or reused up to the standard.

为了解决上述问题,以下几个专利“CN103011546B”、“CN107098562A”、“CN106495427A”、“CN103708697B”、“CN103588375B”、“CN103285637B”、“CN105254147B”、“CN110040935A”采用了相应的技术手段:In order to solve the above problems, the following patents "CN103011546B", "CN107098562A", "CN106495427A", "CN103708697B", "CN103588375B", "CN103285637B", "CN105254147B", "CN110040935A" adopted corresponding technical means:

1)“一种两段式污泥干化及能量回收系统及其干化工艺”,采用间壁式干化设备和带式干化机的两段干化工艺。采用带式干燥器的热量回收于间壁换热器污泥的二次蒸汽,相当于水份的“两效蒸发”,从而实现节能。1) "A two-stage sludge drying and energy recovery system and its drying process", which adopts a two-stage drying process of partition type drying equipment and belt dryer. The heat of the belt dryer is recovered from the secondary steam of the sludge in the partition heat exchanger, which is equivalent to the "two-effect evaporation" of water, thereby realizing energy saving.

2)“两段式污泥干化工艺的新型热能梯级再利用系统”,该系统包括薄层蒸发器及带式干燥机分两段干化的工艺。系统热量输入来自于热电厂高温蒸汽。通过闪蒸罐将I段薄层蒸发器内的一次蒸汽冷凝水闪蒸成低温低压蒸汽,用于II段热风的再加热,从而可以减少新鲜蒸汽的补充量,实现既省蒸汽又省冷却水的目的。2) "New-type thermal energy cascade reuse system for two-stage sludge drying process", the system includes a thin-layer evaporator and a belt dryer in two-stage drying process. The heat input of the system comes from the high temperature steam of the thermal power plant. The primary steam condensed water in the thin-layer evaporator of the first stage is flashed into low-temperature and low-pressure steam through the flash tank, which is used for the reheating of the hot air of the second stage, so as to reduce the supplementary amount of fresh steam and save both steam and cooling water. the goal of.

3)“MVR过热蒸汽污泥连续干燥系统及工作方法”,该系统采用过热蒸汽作为干燥介质,干燥过程产生的二次蒸汽分成两路:一路小部分蒸汽通过压缩机压缩变成高压的过热蒸汽进入换热器的热端,换热冷凝后进入冷凝水罐;另一路大部分水蒸汽进入换热器冷端,经加热后送回干燥器内。该干燥系统主要采用压缩方法来回收干燥过程产生的二次蒸汽的显热与潜热。3) "MVR superheated steam sludge continuous drying system and working method", the system uses superheated steam as the drying medium, and the secondary steam generated in the drying process is divided into two paths: a small part of the steam is compressed by the compressor into high-pressure superheated steam It enters the hot end of the heat exchanger, and then enters the condensed water tank after heat exchange and condensation; the other way, most of the water vapor enters the cold end of the heat exchanger, and is sent back to the dryer after being heated. The drying system mainly adopts the compression method to recover the sensible heat and latent heat of the secondary steam generated in the drying process.

4)“机械蒸汽再压缩热泵MVR污泥干化系统”,污泥通过空心桨叶式干燥机干燥处理后产生的二次蒸汽,该二次蒸汽通过压缩机压缩后再回到空心桨叶机体内,回收污泥干燥过程中产生的二次蒸汽的全部潜热。4) "Mechanical vapor recompression heat pump MVR sludge drying system", the secondary steam generated after the sludge is dried by the hollow paddle dryer, the secondary steam is compressed by the compressor and then returned to the hollow paddle body Inside, all the latent heat of the secondary steam generated during the sludge drying process is recovered.

5)“一种污泥MVC蒸发烘干系统及其烘干污泥的方法”,污泥蒸发过程的二次蒸汽通过蒸汽压缩机压缩机后进入烘干装置作为蒸汽补充热源,利用高温冷凝水洗涤净化蒸汽。5) "A sludge MVC evaporation drying system and method for drying sludge", the secondary steam in the sludge evaporation process passes through the steam compressor and enters the drying device as a steam supplementary heat source, using high temperature condensed water Washing purification steam.

6)“低温真空脱水干化成套设备及其工艺”,真空系统对被加热的物料腔室抽真空,腔室内蒸发的水蒸汽在换热器中冷凝成为液态水排放,达到低温蒸发的目的。6) "Low-temperature vacuum dehydration and drying equipment and its process", the vacuum system evacuates the heated material chamber, and the evaporated water vapor in the chamber is condensed into liquid water in the heat exchanger and discharged to achieve the purpose of low-temperature evaporation.

7)“一种污泥过热蒸汽干燥乏汽余热三重利用”,同时回收乏汽显热和潜热,废水循环利用、废气零污染排放。整个装置实现了污泥过热蒸汽干燥乏汽余热三次利用。干燥过程通过对乏汽显热和潜热同时回收,防止干燥过程中产生冷凝,缩短了干燥时间;干燥过程中只需在初始阶段通入过热蒸汽,后期蒸汽循环使用,减少了热源的输入,降低了能耗。7) "Triple utilization of waste heat of waste steam drying with superheated steam of sludge", at the same time recovery of sensible heat and latent heat of spent steam, recycling of waste water, and zero pollution discharge of waste gas. The whole device realizes the three-time utilization of the waste heat of the waste steam from the superheated steam drying of the sludge. In the drying process, the sensible heat and latent heat of the exhausted steam are recovered at the same time to prevent condensation during the drying process and shorten the drying time; in the drying process, only superheated steam needs to be introduced in the initial stage, and the steam is recycled in the later stage, which reduces the input of heat source and reduces the energy consumption.

8)“一种多层组合自落式污泥干燥装置及干燥方法”采用间接干燥结合过热二次蒸汽的方式干燥污泥,利用MVR蒸发技术有效缩短了干燥的时长。8) "A multi-layer combined self-falling sludge drying device and drying method" uses indirect drying combined with superheated secondary steam to dry sludge, and uses MVR evaporation technology to effectively shorten the drying time.

虽然上述技术专利或相关研究在解决了固体干燥节能或MVR技术在干燥领域的应用方法,实施过程中存在的诸多问题,一些问题尚未得到有效解决。例如“CN103011546B”、“CN107098562A”两段式污泥干化过程的热能回收利用过程,相当于“两效蒸发”节能效果。干燥过程全部采用高温蒸汽作为能源,能耗相对于MVR技术还是较高。“CN106495427A”MVR过热蒸汽污泥连续干燥系统及工作方法,二次蒸汽的显热与潜热,用于进料污泥的预热。基于物料质量和热量衡算,二次蒸汽的潜热热量远大于污泥的预热热量,降低了热量回收比例。“CN103708697B”、“CN103588375B”利用MVR蒸发技术通过空心桨叶式或其他间接热传导烘干装置来干燥污泥,在实践过程中需要对系统大量补充热量,同时污泥在进入“降速段”后蒸发时间过长,机械传动或搅拌强化传热及热量损失导致节能收益下降。“CN103285637B”低温真空脱水干化成套设备及其工艺和“CN105254147B”一种污泥过热蒸汽干燥乏汽余热三重利用,能耗也均来源于低温(80℃-90℃)热源或蒸汽,能耗相对于MVR技术还是较高。“CN110040935A”一种多层组合自落式污泥干燥装置及干燥方法,系统补充热量直接加热被压缩后的二次蒸汽,一部分二次蒸汽作为过热蒸汽直接进入干燥腔内和污泥对流换热,一部分二次蒸汽进入间接干燥器内腔和污泥传导换热。间接干燥器内腔的过热蒸汽相比于饱和蒸汽,传热效果理论上并不理想,同时对系统补充热量在二次蒸汽成为冷凝水后,未更多的回收其显热。Although the above technical patents or related research have solved the application method of solid drying energy saving or MVR technology in the field of drying, there are many problems existing in the implementation process, and some problems have not been effectively solved. For example, "CN103011546B", "CN107098562A" two-stage sludge drying process heat energy recovery and utilization process, equivalent to "two-effect evaporation" energy-saving effect. The drying process uses high temperature steam as the energy source, and the energy consumption is still higher than that of the MVR technology. "CN106495427A" MVR superheated steam sludge continuous drying system and working method, the sensible heat and latent heat of secondary steam are used for the preheating of feed sludge. Based on the material quality and heat balance, the latent heat of the secondary steam is much larger than the preheating heat of the sludge, which reduces the heat recovery ratio. "CN103708697B" and "CN103588375B" use MVR evaporation technology to dry sludge through hollow paddle type or other indirect heat conduction drying devices. In practice, a large amount of heat needs to be added to the system. At the same time, after the sludge enters the "speed reduction section" Evaporation time is too long, mechanical transmission or stirring enhances heat transfer and heat loss, resulting in a decrease in energy-saving benefits. "CN103285637B" low temperature vacuum dehydration and drying complete equipment and its process and "CN105254147B" a kind of sludge superheated steam drying waste steam waste heat triple utilization, energy consumption also comes from low temperature (80 ℃-90 ℃) heat source or steam, energy consumption Compared with MVR technology, it is still higher. "CN110040935A" is a multi-layer combined self-falling sludge drying device and drying method. The system supplements heat to directly heat the compressed secondary steam, and a part of the secondary steam directly enters the drying chamber as superheated steam to exchange heat with the sludge by convection. , a part of the secondary steam enters the inner cavity of the indirect dryer and conducts heat exchange with the sludge. Compared with saturated steam, the heat transfer effect of the superheated steam in the inner cavity of the indirect dryer is not ideal in theory. At the same time, the supplementary heat to the system does not recover more sensible heat after the secondary steam becomes condensed water.

综上所述,有必要提出一种新的机械蒸汽再压缩干燥系统及方法。In summary, it is necessary to propose a new mechanical vapor recompression drying system and method.

发明内容SUMMARY OF THE INVENTION

有鉴于此,本发明提出了一种操作简单、性能可靠、制造成本低、拆卸维修方便、干燥连续速度快、补充热量小、系统能耗低的机械蒸汽再压缩干燥系统及方法。In view of this, the present invention proposes a mechanical vapor recompression drying system and method with simple operation, reliable performance, low manufacturing cost, convenient disassembly and maintenance, fast drying continuous speed, small supplementary heat, and low system energy consumption.

根据本发明的目的,本发明提供第一技术方案:一种机械蒸汽再压缩干燥系统,其包括存储常温污泥来料且内有冷凝水换热盘管的污泥存储池、与污泥存储池输出相连且设有夹套式换热器的污泥注射泵、与污泥注射泵输出相连的薄层蒸发干燥器、与薄层蒸发干燥器输出相连的挤压分条成型机、与挤压分条成型机输出相连的网带干燥机、与网带干燥机输出相连的干泥仓、设置在薄层蒸发干燥器和网带干燥机之间的蒸汽压缩机、与网带干燥机相连且用于分离二次蒸汽和污泥粉尘的旋风除尘器、与旋风除尘器输出相连且用于对二次蒸汽水洗清洁的水洗除尘器、与薄层蒸发干燥器相连且收集冷凝水的冷凝水缓冲罐、以及与冷凝水缓冲罐相连且用于抽吸系统空气维持真空并排放不凝气体的真空泵。According to the purpose of the present invention, the present invention provides a first technical solution: a mechanical vapor recompression drying system, which includes a sludge storage tank for storing incoming sludge at room temperature and having a condensed water heat exchange coil inside, and a sludge storage tank. The sludge injection pump connected to the output of the pool and provided with a jacket heat exchanger, the thin-layer evaporation dryer connected to the output of the sludge injection pump, the extrusion slitting machine connected to the output of the thin-layer evaporation dryer, and the extrusion A mesh belt dryer connected to the output of the slitting and forming machine, a dry mud silo connected to the output of the mesh belt dryer, a steam compressor arranged between the thin-layer evaporative dryer and the mesh belt dryer, connected to the mesh belt dryer and a cyclone dust collector for separating secondary steam and sludge dust, a water washing dust collector connected to the output of the cyclone dust collector and used for washing and cleaning the secondary steam, and a condensed water connected to the thin-layer evaporative dryer and collecting the condensed water A buffer tank, and a vacuum pump connected to the condensate buffer tank and used to suck system air to maintain vacuum and discharge non-condensable gas.

在第一技术方案的基础上,进一步包括如下附属技术方案:On the basis of the first technical solution, the following subsidiary technical solutions are further included:

所述薄层蒸发干燥器包括至少一个筒形加热仓、位于筒形加热仓内侧且表面均匀分布多个刮板的刮板转子、位于筒形加热仓外侧且驱动刮板转子旋转的电机、与水洗除尘器输出相连的蒸汽入口、与冷凝水缓冲罐的输入相连的蒸汽及冷凝水出口、与污泥注射泵输出相连的污泥进料口、以及与挤压分条成型机输入相连的污泥出口。The thin-layer evaporative dryer comprises at least one cylindrical heating bin, a scraper rotor located inside the cylindrical heating bin and a plurality of scrapers evenly distributed on the surface, a motor located outside the cylindrical heating bin and driving the scraper rotor to rotate, and The steam inlet connected to the output of the water washing dust collector, the steam and condensed water outlet connected to the input of the condensate buffer tank, the sludge inlet connected to the output of the sludge injection pump, and the sewage outlet connected to the input of the extrusion slitting machine. Mud export.

所述网带干燥机为密闭式结构,内部设有蒸汽循环风机和加热器。The mesh belt dryer is a closed structure with a steam circulating fan and a heater inside.

所述水洗除尘器包括冷凝水喷淋头、位于冷凝水喷淋头上方的除沫器、与冷凝水喷淋头相连的加药装置、与冷凝水喷淋头相连的第一循环泵、以及将污泥返回污泥存储池的排污泵。The water-washing dust collector includes a condensed water spray head, a demister located above the condensed water spray head, a dosing device connected to the condensed water spray head, a first circulating pump connected to the condensed water spray head, and Sewage pumps that return sludge to sludge storage tanks.

还包括将干泥仓内干泥挤压造粒后出料的造粒机、位于污泥注射泵和水洗除尘器之间的第二循环泵、以及与污泥存储池相连且内有电化学氧化除垢仪的冷凝水池。It also includes a granulator for extruding and granulating the dry mud in the dry mud silo, a second circulating pump located between the sludge injection pump and the water washing dust collector, and a sludge storage tank connected with an electrochemical device. Condensation sump of the oxidizing descaler.

还包括设置在薄层蒸发干燥器和蒸汽压缩机之间的第一过滤器、和设置在薄层蒸发干燥器和水洗除尘器之间的第二过滤器。It also includes a first filter disposed between the thin-layer evaporative dryer and the vapor compressor, and a second filter disposed between the thin-layer evaporative dryer and the water scrubber.

本发明提供第二技术方案:一种机械蒸汽再压缩干燥方法,其包括:The present invention provides a second technical solution: a mechanical vapor recompression drying method, comprising:

S1:将湿污泥通过传输装置从污泥存储池传输至薄层蒸发干燥器,过程中湿污泥和冷凝水在换热器换热,由入口的5-35℃加热至65-80℃;冷凝水由进口的80-98℃冷却至出口的15-45℃;S1: The wet sludge is transferred from the sludge storage tank to the thin-layer evaporative dryer through the transmission device. During the process, the wet sludge and condensed water are exchanged in the heat exchanger, and heated from 5-35 °C at the inlet to 65-80 °C ; The condensed water is cooled from 80-98 ℃ at the inlet to 15-45 ℃ at the outlet;

S2:预热后的污泥在薄层蒸发干燥器内,在旋转刮板叶片的作用下形成薄层黏附于蒸发干燥器筒体内表面,筒体内为负压系统,压力设定为25-47.5KPa,对应的水份蒸发温度为65-80℃;其中污泥和筒壁传导换热的热源来自步骤S4的蒸汽,换热温差为18-33℃,污泥含水率由80%-95%降低至55%-65%;S2: The preheated sludge forms a thin layer in the thin-layer evaporative dryer under the action of the rotating scraper blade and adheres to the inner surface of the evaporative dryer cylinder. There is a negative pressure system in the cylinder, and the pressure is set to 25-47.5 KPa, the corresponding water evaporation temperature is 65-80 °C; the heat source for heat exchange between the sludge and the cylinder wall comes from the steam in step S4, the heat exchange temperature difference is 18-33 °C, and the sludge moisture content is 80%-95% reduced to 55%-65%;

S3:将含水率55%-65%的污泥挤压分条为宽度2-5mm的粘稠条状污泥再进入网带干燥机;S3: extrude the sludge with a moisture content of 55%-65% into sticky strips with a width of 2-5mm and then enter the mesh belt dryer;

S4:进入网带干燥机内的污泥在网带传输过程中,和过热蒸汽对流换热,进一步蒸发干燥后进入干泥仓,由造粒机挤压造粒后出料,其中污泥含水率由55%-65%进一步蒸发干燥为含水率20%-45%污泥,完成网带干燥机内干燥过程;而压缩机出口的饱和蒸汽进入网带干燥机后,通过加热器加热提升过热度20-50℃后,由循环风机强制循环和污泥对流换热;富余的过热蒸汽进入旋风分离、水洗除尘和过滤后成为洁净的饱和蒸汽再次进入步骤S2;S4: During the transmission process of the mesh belt, the sludge entering the mesh belt dryer exchanges heat with the superheated steam, and then enters the dry sludge bin after further evaporation and drying, and is extruded and granulated by the granulator. The drying rate is further evaporated from 55%-65% to sludge with a moisture content of 20%-45% to complete the drying process in the mesh belt dryer; after the saturated steam from the compressor outlet enters the mesh belt dryer, it is heated by a heater to lift After the temperature is 20-50°C, the circulating fan is forced to circulate and exchange heat with the sludge convection; the excess superheated steam enters the cyclone separation, washing and dedusting and filtering to become clean saturated steam and then enters step S2 again;

S5:步骤S2中蒸发过程产生的二次蒸汽经过过滤器过滤后,进入蒸汽压缩机压缩后再进入步骤S4,来自冷凝水缓冲罐的冷凝水喷入蒸汽压缩机吸气入口,压缩比为2.0-4.5,蒸汽温升18-33℃;S5: After the secondary steam generated by the evaporation process in step S2 is filtered by the filter, it enters the steam compressor for compression and then enters step S4, and the condensed water from the condensed water buffer tank is sprayed into the suction inlet of the steam compressor, and the compression ratio is 2.0 -4.5, steam temperature rise 18-33℃;

S6:一部份冷凝水进入步骤S5降低压缩机排气过热度;一部分进入步骤S4中的水洗除尘器后,排入污泥池;剩余部分冷凝水则通过步骤S1中换热器换热后进入冷凝水罐,通过电化学氧化除垢仪去除微量有机物后排放或回用;S6: a part of the condensed water enters step S5 to reduce the superheat degree of the compressor exhaust; a part enters the water washing dust collector in step S4, and is discharged into the sludge tank; the remaining part of the condensed water passes through the heat exchanger in step S1 after heat exchange Enter the condensed water tank, remove trace organic matter through electrochemical oxidation descaling instrument, and then discharge or reuse;

S7:由真空泵排除冷凝水缓冲罐和冷凝水罐中不凝气体至结束。S7: The non-condensable gas in the condensed water buffer tank and the condensed water tank is removed by the vacuum pump to the end.

与现有技术相比,本发明的技术方案有以下优点:Compared with the prior art, the technical scheme of the present invention has the following advantages:

采用MVR技术应用于固体干燥领域,相对于传统的利用热源加热蒸发技术,可节省大量能源消耗及冷却水系统消耗。过程中无废气排放,系统无冷却水系统,节省了冷却塔水份蒸发损失。采用低温蒸发的二次蒸汽冷凝水污染物低,其主要成分为可挥发有机物,通过“电化学氧化”等方法低成本处理后冷凝水可直接达标排放。而高温蒸发的二次蒸汽冷凝水往往还需要再次进入污水处理厂处理。Using MVR technology in the field of solid drying can save a lot of energy consumption and cooling water system consumption compared to the traditional heating and evaporation technology using heat sources. There is no exhaust gas emission in the process, and the system has no cooling water system, which saves the evaporation loss of cooling tower water. The secondary steam condensed water that uses low temperature evaporation has low pollutants, and its main component is volatile organic compounds. After low-cost treatment by "electrochemical oxidation" and other methods, the condensed water can be directly discharged up to the standard. The secondary steam condensate water evaporated at high temperature often needs to be re-entered into the sewage treatment plant for treatment.

“低温真空蒸发”过程中,物料入口温度和蒸发温度小,减少了物料的预热热量;“低温过热蒸汽蒸发”过程中,物料出口温度相对较低、含水率低,减少了出口物料的热量损失;系统整体工作温度和环境温度温差低,也减少了系统的散热热量损失。In the process of "low temperature vacuum evaporation", the inlet temperature and evaporation temperature of the material are small, which reduces the preheating heat of the material; in the process of "low temperature superheated steam evaporation", the outlet temperature of the material is relatively low and the moisture content is low, which reduces the heat of the material at the outlet The temperature difference between the overall operating temperature of the system and the ambient temperature is low, which also reduces the heat loss of the system.

在整个蒸发过程中,仅对高粘性低蒸发速度的污泥(含水率55%-65%以下),采用温度和换热温差相对比较大的“过热蒸汽蒸发”方式对流换热。缩短整体干燥时间的同时,有利于热量回收,补充热量也小。本系统补充热量的费用和能源品位高低无关,和量相关。补充热量主要用于加热二次蒸汽用于提升二次蒸汽显热。过热蒸汽和污泥对流换热时,换热温差高换热效果好。During the whole evaporation process, only for the sludge with high viscosity and low evaporation rate (water content below 55%-65%), the "superheated steam evaporation" method with relatively large temperature and heat exchange temperature difference is adopted for convective heat transfer. While shortening the overall drying time, it is beneficial to heat recovery and the supplementary heat is also small. The cost of supplementary heat in this system has nothing to do with the energy grade, but is related to the quantity. The supplementary heat is mainly used to heat the secondary steam to increase the sensible heat of the secondary steam. When superheated steam and sludge are convectively exchanged, the heat exchange temperature difference is high and the heat exchange effect is good.

不影响连续蒸发速度的情况下,通过“过热蒸汽”蒸发阶段参数适当调整,可产生不同干度的污泥颗粒,干化范围70%-95%。Without affecting the continuous evaporation rate, by properly adjusting the parameters of the "superheated steam" evaporation stage, sludge particles of different dryness can be produced, and the drying range is 70%-95%.

热量消耗最大的水份蒸发全部的潜热可得到回收利用,高温冷凝水的全部或大部分热量得到回收利用。All the latent heat of evaporation of the water with the largest heat consumption can be recycled, and all or most of the heat of the high-temperature condensate can be recycled.

系统二次蒸汽温度可达120℃-150℃,但压力低于0.1MPa,系统管道和容器均非“压力容器”,可有效降低生产制造和使用维护成本。污泥直接接触的气体是二次蒸汽,无空气污染排放。在低含氧环境,没有燃烧和粉尘爆炸危险,安全性更好。The temperature of the secondary steam of the system can reach 120℃-150℃, but the pressure is lower than 0.1MPa, and the system pipelines and vessels are not "pressure vessels", which can effectively reduce the cost of production, use and maintenance. The gas in direct contact with the sludge is secondary steam, and there is no air pollution emission. In a low-oxygen environment, there is no danger of combustion and dust explosion, and the safety is better.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to explain the embodiments of the present invention or the technical solutions in the prior art more clearly, the following briefly introduces the accompanying drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. For those of ordinary skill in the art, other drawings can also be obtained according to these drawings without creative efforts.

图1为本发明的结构示意图。FIG. 1 is a schematic structural diagram of the present invention.

具体实施方式Detailed ways

如图1,本发明提供一种机械蒸汽再压缩干燥系统的第一实施例,其包括存储常温污泥来料且内有冷凝水换热盘管111的污泥存储池110、与污泥存储池110输出相连且设有夹套式换热器121、第一外部热源加热器122的污泥注射泵120、与污泥注射泵120输出相连的薄层蒸发干燥器130、与薄层蒸发干燥器130输出相连的挤压分条成型机140、与挤压分条成型机140输出相连的网带干燥机150、与网带干燥机150输出相连的干泥仓160、设置在薄层蒸发干燥器130和网带干燥机150之间的蒸汽压缩机220、与网带干燥机150相连且用于分离二次蒸汽和污泥粉尘的旋风除尘器230、与旋风除尘器230输出相连且用于对二次蒸汽水洗清洁的水洗除尘器240、与薄层蒸发干燥器130相连且收集冷凝水的冷凝水缓冲罐310、以及与冷凝水缓冲罐310相连且用于抽吸系统空气维持真空并排放不凝气体的真空泵400。As shown in FIG. 1 , the present invention provides a first embodiment of a mechanical vapor recompression drying system, which includes a sludge storage tank 110 that stores incoming sludge at room temperature and has a condensed water heat exchange coil 111 inside, and a sludge storage tank 110 . The output of the pool 110 is connected and is provided with a jacket heat exchanger 121, a sludge injection pump 120 of the first external heat source heater 122, a thin layer evaporation dryer 130 connected to the output of the sludge injection pump 120, and a thin layer evaporation dryer 130. The extrusion slitting machine 140 connected to the output of the device 130, the mesh belt dryer 150 connected to the output of the extrusion slitting machine 140, the dry mud bin 160 connected to the output of the mesh belt dryer 150, and the The steam compressor 220 between the dryer 130 and the mesh belt dryer 150, the cyclone dust collector 230 connected to the mesh belt dryer 150 and used to separate secondary steam and sludge dust, and the output of the cyclone dust collector 230 connected to the The water washing dust collector 240 for cleaning the secondary steam water, the condensed water buffer tank 310 connected to the thin layer evaporative dryer 130 and collecting the condensed water, and the condensed water buffer tank 310 connected to the suction system air for maintaining vacuum and discharging Vacuum pump 400 for non-condensable gas.

污泥存储池110存储来料常温污泥。在污泥存储池内壁有冷凝水换热盘管111。冷凝水换热盘管111内部为冷凝水,冷凝水和污泥换热后排放至冷凝水池320。污泥注射泵120提供动力将污泥存储池110内的污泥输送至薄层蒸发器130污泥入口,且内部固体挤压推送的压力能保障污泥存储池110和薄层蒸发器130内腔密闭而不串气。污泥输送管道外设夹套式换热器121,夹套式换热器121内部为冷凝水,冷凝水和污泥换热后排入污泥存储池110。外部热源加热器122提供热量供系统补充热量加热污泥提升温度。The sludge storage tank 110 stores incoming sludge at room temperature. There is a condensed water heat exchange coil 111 on the inner wall of the sludge storage tank. The condensed water heat exchange coil 111 contains condensed water, and the condensed water and the sludge are discharged to the condensed water tank 320 after heat exchange. The sludge injection pump 120 provides power to transport the sludge in the sludge storage tank 110 to the sludge inlet of the thin-layer evaporator 130, and the pressure of the internal solid extrusion can ensure the sludge storage tank 110 and the thin-layer evaporator 130. The cavity is closed without gas. A jacket-type heat exchanger 121 is provided outside the sludge conveying pipeline, and the inside of the jacket-type heat exchanger 121 is condensed water, which is discharged into the sludge storage tank 110 after heat exchange between the condensed water and the sludge. The external heat source heater 122 provides heat for the system to supplement heat to heat the sludge to raise the temperature.

薄层蒸发干燥器130包括至少一个柱状的筒形加热仓和内设的刮板转子。筒形加热仓的一端设有电机,刮板转子通过电机驱动。刮板转子表面均匀分布刮板叶片。刮板叶片将污泥从薄层蒸发干燥器130的一端推送至另一端,并使污泥均匀遍布整个筒形加热仓的圆筒内壁。筒形加热仓一端设有蒸汽入口131,筒形加热仓另一端设有蒸汽及冷凝水出口132。筒形加热仓另一端设有污泥进料口133,筒形加热仓一端设有污泥出口134。进一步,筒形加热仓为间壁式结构,内部可流通蒸汽。筒形加热仓外表面加设保温层,筒形加热仓内表面和刮板转子同轴。The thin-layer evaporative dryer 130 includes at least one cylindrical cylindrical heating chamber and a built-in scraper rotor. One end of the cylindrical heating bin is provided with a motor, and the scraper rotor is driven by the motor. Scraper blades are evenly distributed on the surface of the scraper rotor. The scraper blade pushes the sludge from one end of the thin-layer evaporative dryer 130 to the other end, and makes the sludge evenly spread over the inner cylindrical wall of the entire cylindrical heating chamber. One end of the cylindrical heating bin is provided with a steam inlet 131, and the other end of the cylindrical heating bin is provided with a steam and condensed water outlet 132. The other end of the cylindrical heating bin is provided with a sludge feeding port 133, and one end of the cylindrical heating bin is provided with a sludge outlet 134. Further, the cylindrical heating chamber is a partition structure, and steam can be circulated inside. An insulating layer is added on the outer surface of the cylindrical heating bin, and the inner surface of the cylindrical heating bin is coaxial with the scraper rotor.

挤压分条成型机140是一台带有孔格网的污泥挤压设备。来自薄层蒸发器130中污泥出口134的污泥,在挤压分条成型机140作用下,将污泥挤压切碎成“条状”后散落在网带干燥机150的传送网带上。挤压分条成型机140内固体推挤压力能保障薄层蒸发器130和网带干燥机150腔体密闭而不串气。网带干燥机150为密闭式结构,内部带蒸汽的循环风机151和第二外部热源加热器152。进一步地,网带干燥机150的循环风机151位于夹套式换热器121内。外部热源加热器152和122优选热源为电加热、高温热泵或外部直接引入的高温蒸汽。进一步,网带干燥机150将循环加热的过热蒸汽输送至蒸汽压缩机220压缩,形成升温升压的水蒸汽,这些水蒸汽是薄层蒸发器130污泥蒸发的二次蒸汽。过热蒸汽在循环风机151的作用下强制循环,和网带上的污泥对流换热干燥污泥水份。干泥仓160用于存储网带干燥机150和旋风除尘器230生产的干污泥。造粒机161将干泥仓160内的干泥挤压造粒后出料。造粒机161内固体推挤压力能保障造粒机161和外部大气环境密闭而不串气。第一、第二过滤器210、250为空气高效过滤器,用于过滤气体中微尘。蒸汽压缩机220为水蒸汽压缩机,优选为双螺杆蒸汽压缩机,压缩比2.0-4.5。蒸汽压缩机220入口注入来自冷凝水缓冲罐310的高温冷凝水,用于降低排气过热度。旋风除尘器230用于分离来自网带干燥机150腔室内的二次蒸汽和污泥粉尘。二次蒸汽进入水洗除尘器240,污泥粉尘进入干泥仓160。水洗除尘器240用于对二次蒸汽的水洗清洁和降低其过热度。水洗除尘器240的系统补水来自冷凝水缓冲罐310的高温冷凝水。在循环泵244的作用下由水洗除尘器240的上部冷凝水喷淋头241喷淋水洗二次蒸汽。加药装置243向循环水添加有机酸,用于清洗去除二次蒸汽中的游离氨气。水洗除尘器240底部有排污口,通过排污泵245返回污泥存储池110。除沫器242用于对水洗后的二次蒸汽气水分离,二次蒸汽除尘、除氨后进入第二过滤器250。清洁和饱和二次蒸汽返回薄层蒸发器130的蒸汽夹套。冷凝水缓冲罐310用于存储薄层蒸发器130的冷凝水。冷凝水缓冲罐310上部为气体,下部为液态水。冷凝水池320是密闭结构的储水箱,上部为气体,下部为液态水。进一步,冷凝水池320内有电化学氧化除垢仪321,用于降低冷凝水中挥发性有机物,降低冷凝水COD并达标排放或回用。真空泵400用于抽吸系统空气维持真空和排除运行过程中不凝气体。可再生活性炭过滤器410用于对真空泵400少量排气的除臭过滤。The extrusion slitting machine 140 is a sludge extrusion equipment with a mesh of holes. The sludge from the sludge outlet 134 in the thin-layer evaporator 130 is extruded and chopped into "stripes" under the action of the extrusion slitting machine 140 and then scattered on the conveyor belt of the mesh belt dryer 150 superior. The solid pushing force in the extrusion slitting machine 140 can ensure that the cavities of the thin-layer evaporator 130 and the mesh belt dryer 150 are sealed without air. The mesh belt dryer 150 is a closed structure, with a circulating fan 151 with steam inside and a second external heat source heater 152 . Further, the circulating fan 151 of the mesh belt dryer 150 is located in the jacket heat exchanger 121 . The external heat source heaters 152 and 122 preferably have a heat source of electric heating, a high-temperature heat pump, or high-temperature steam directly introduced from the outside. Further, the mesh belt dryer 150 transports the circulating heated superheated steam to the steam compressor 220 for compression to form water vapor with temperature and pressure, which is the secondary steam from the evaporation of the sludge in the thin-layer evaporator 130 . The superheated steam is forced to circulate under the action of the circulating fan 151, and convectively exchanges heat with the sludge on the mesh belt to dry the sludge moisture. The dry sludge bin 160 is used to store the dry sludge produced by the mesh belt dryer 150 and the cyclone dust collector 230 . The granulator 161 extrudes and granulates the dry mud in the dry mud bin 160 before discharging. The solid pushing and extruding force in the granulator 161 can ensure that the granulator 161 and the external atmospheric environment are sealed without air. The first and second filters 210 and 250 are high-efficiency air filters for filtering fine dust in the gas. The steam compressor 220 is a steam compressor, preferably a twin-screw steam compressor, with a compression ratio of 2.0-4.5. The high temperature condensate water from the condensate water buffer tank 310 is injected into the inlet of the steam compressor 220 to reduce the superheat degree of the exhaust gas. The cyclone 230 is used to separate secondary steam and sludge dust from the chamber of the mesh belt dryer 150 . The secondary steam enters the water washing dust collector 240 , and the sludge dust enters the dry sludge bin 160 . The water washing dust collector 240 is used to wash and clean the secondary steam and reduce its superheat. The system replenishment water of the water-washing dust collector 240 comes from the high-temperature condensed water of the condensed water buffer tank 310 . Under the action of the circulating pump 244 , the secondary steam for washing is sprayed by the upper condensed water spray head 241 of the washing dust collector 240 . The dosing device 243 adds organic acid to the circulating water for cleaning and removing free ammonia in the secondary steam. There is a sewage outlet at the bottom of the water-washing dust remover 240 , which is returned to the sludge storage tank 110 through the sewage pump 245 . The demister 242 is used to separate the gas and water of the secondary steam after water washing, and the secondary steam enters the second filter 250 after dust removal and ammonia removal. The clean and saturated secondary steam is returned to the steam jacket of the thin layer evaporator 130 . The condensed water buffer tank 310 is used to store the condensed water of the thin-layer evaporator 130 . The upper part of the condensed water buffer tank 310 is gas, and the lower part is liquid water. The condensation water tank 320 is a water storage tank with a closed structure, the upper part is gas, and the lower part is liquid water. Further, there is an electrochemical oxidation descaling instrument 321 in the condensed water pool 320, which is used to reduce volatile organic compounds in the condensed water, reduce the COD of the condensed water, and discharge or reuse the condensed water. The vacuum pump 400 is used to suck system air to maintain vacuum and to remove non-condensable gas during operation. The regenerable activated carbon filter 410 is used for deodorizing and filtering a small amount of exhaust gas from the vacuum pump 400 .

本实施例还提供了MVR低温真空联合过热蒸汽干燥方法,利用上述相关结构和装置进行干燥工作,具体包括如下步骤:This embodiment also provides an MVR low-temperature vacuum combined superheated steam drying method, which utilizes the above-mentioned related structures and devices to perform drying work, and specifically includes the following steps:

S1:湿污泥通过传输装置污泥注射泵120,从污泥存储池110传输至薄层蒸发干燥器130。过程中湿污泥和冷凝水在夹套式换热器121换热,由入口的5-35℃加热至65-80℃,热量不足部分由第一外部热源加热器122补充。冷凝水由进口的80-98℃冷却至出口的25-55℃,再进入换热盘管111,冷却至15-45℃后排入冷凝水罐320;S1: The wet sludge is transported from the sludge storage tank 110 to the thin layer evaporative dryer 130 through the sludge injection pump 120 of the transport device. During the process, the wet sludge and the condensed water exchange heat in the jacket heat exchanger 121 , which is heated to 65-80° C. from 5-35° C. at the inlet, and the insufficient heat is supplemented by the first external heat source heater 122 . The condensed water is cooled from 80-98°C at the inlet to 25-55°C at the outlet, and then enters the heat exchange coil 111, and is cooled to 15-45°C and then discharged into the condensed water tank 320;

S2:预热后的污泥在薄层蒸发干燥器130中,在旋转刮板叶片的作用下形成薄层黏附于蒸发器筒体内表面。筒体内为负压系统,压力设定为25-47.5KPa,对应的水份蒸发温度为65-80℃。污泥和筒壁传导换热,筒体夹套内为来自步骤S4的饱和蒸汽,优选的换热温差设定为18-33℃。污泥在真空负压环境开始蒸发,通过刮板叶片旋转的推动下完成在筒壁的移动并富集在污泥出口134处;污泥在薄层蒸发器130内是“真空低温干燥”过程,污泥含水率由80%-95%降低至55%-65%时,完成薄层蒸发器130内干燥过程;薄层蒸发器130的夹套内饱和蒸汽换热后成为液态冷凝水进入冷凝水缓冲罐310;S2: The preheated sludge forms a thin layer and adheres to the inner surface of the evaporator cylinder under the action of the rotating scraper blade in the thin-layer evaporation dryer 130. There is a negative pressure system in the cylinder, the pressure is set to 25-47.5KPa, and the corresponding water evaporation temperature is 65-80℃. The sludge and the cylinder wall conduct heat exchange, the cylinder jacket is filled with saturated steam from step S4, and the preferred heat exchange temperature difference is set to 18-33°C. The sludge starts to evaporate in the vacuum negative pressure environment, and is moved on the cylinder wall by the rotation of the scraper blade and is enriched at the sludge outlet 134; the sludge in the thin-layer evaporator 130 is a "vacuum low temperature drying" process When the moisture content of the sludge is reduced from 80%-95% to 55%-65%, the drying process in the thin-layer evaporator 130 is completed; the saturated steam in the jacket of the thin-layer evaporator 130 becomes liquid condensed water after heat exchange and enters the condensation Water buffer tank 310;

S3:挤压分条成型机140将污泥出口134处含水率55%-65%的污泥挤压分条为直径2-5mm的粘稠条状污泥再进入网带干燥机150;S3: The extrusion slitting forming machine 140 extrudes and slits the sludge with a moisture content of 55%-65% at the sludge outlet 134 into viscous sticky sludge with a diameter of 2-5mm, and then enters the mesh belt dryer 150;

S4:进入网带干燥机150内的污泥在网带传输过程中,和过热蒸汽对流换热,进一步蒸发干燥后进入干泥仓160后,由造粒机161挤压造粒后出料。污泥在网带干燥机150内是“过热蒸汽干燥”过程,污泥含水率由55%-65%进一步蒸发干燥为含水率20%-45%污泥,完成网带干燥机150内干燥过程。压缩机220出口的饱和蒸汽进入网带干燥机150后,通过加热器152加热提升过热度20-50℃后,由循环风机151强制循环和污泥对流换热。富裕的过热蒸汽进入旋风分离器230、水洗除尘器240、和过滤器250成为洁净的饱和蒸汽再次进入步骤S2;S4: The sludge entering the mesh belt dryer 150 exchanges heat with the superheated steam during the conveying process of the mesh belt. After further evaporation and drying, the sludge enters the dry sludge bin 160, and is extruded and granulated by the granulator 161 before discharging. The sludge in the mesh belt dryer 150 is a process of "superheated steam drying", the moisture content of the sludge is further evaporated from 55%-65% to the sludge with a moisture content of 20%-45%, and the drying process in the mesh belt dryer 150 is completed. . After the saturated steam at the outlet of the compressor 220 enters the mesh belt dryer 150, it is heated by the heater 152 to raise the superheat to 20-50°C, and then is forcedly circulated by the circulating fan 151 to exchange heat with the sludge by convection. The rich superheated steam enters the cyclone separator 230, the water washing dust collector 240, and the filter 250 to become clean saturated steam and enters step S2 again;

S5:步骤S2蒸发过程中产生的二次蒸汽经过过滤器210过滤后,进入压缩机220压缩后进入步骤S4。来自冷凝水缓冲罐310的冷凝水喷入蒸汽压缩机220吸气入口,用于降低压缩机转子温度和出口水蒸气过热度。优选的压缩比为2.0-4.5,蒸汽温升18-33℃;S5: After the secondary steam generated in the evaporation process in step S2 is filtered by the filter 210, it enters the compressor 220 for compression, and then proceeds to step S4. The condensed water from the condensed water buffer tank 310 is injected into the suction inlet of the steam compressor 220 to reduce the compressor rotor temperature and the outlet steam superheat. The preferred compression ratio is 2.0-4.5, and the steam temperature rise is 18-33°C;

S6:冷凝水缓冲罐310中冷凝水温度为80~98℃。一部份进入步骤S5用于降低压缩机排气过热度;一部分进入步骤S4中的水洗除尘器240后,排入污泥池110;大部分冷凝水通过步骤S1中换热器121和111换热后进入冷凝水罐320,通过电化学氧化除垢仪321去除微量有机物后排放或回用;S6: The temperature of the condensed water in the condensed water buffer tank 310 is 80-98°C. A part enters step S5 to reduce the superheat degree of the compressor exhaust gas; a part enters the water washing dust collector 240 in step S4, and then is discharged into the sludge tank 110; most of the condensed water is exchanged through the heat exchangers 121 and 111 in step S1 After being heated, it enters the condensed water tank 320, and is discharged or reused after removing trace organic matter by the electrochemical oxidation descaling instrument 321;

S7:由真空泵400排除冷凝水缓冲罐310和冷凝水罐320中不凝气体保障系统真空度和蒸发压力;少量不凝气体通过可再生活性炭过滤器410除臭后排放。S7: The vacuum pump 400 removes the non-condensable gas in the condensed water buffer tank 310 and the condensed water tank 320 to ensure the vacuum degree and evaporation pressure of the system; a small amount of non-condensable gas is deodorized through the renewable activated carbon filter 410 and then discharged.

本发明的优点:Advantages of the present invention:

基于干燥工艺特点,结合MVR技术在水份蒸发领域的最优节能性,采用“低温真空蒸发”干燥处理污泥的“恒速段”干燥过程,采用“过热蒸汽”干燥处理含水固体物料的“降速段”干燥过程。“过热蒸汽”来源于“低温真空蒸发”过程的被再次加热的二次蒸汽;“过热蒸汽”蒸发后的蒸汽再次进入“低温真空蒸发”干燥器释放全部水蒸汽的潜热后成为高温冷凝水,高温冷凝水的显热由含水固体物料预热来回收。Based on the characteristics of the drying process, combined with the optimal energy saving of MVR technology in the field of water evaporation, the "constant speed section" drying process of "low temperature vacuum evaporation" is used to dry the sludge, and the "superheated steam" is used to dry the water-containing solid materials. Slow down section" drying process. The "superheated steam" comes from the reheated secondary steam in the "low temperature vacuum evaporation" process; the evaporated steam of the "superheated steam" enters the "low temperature vacuum evaporation" dryer again to release the latent heat of all the water vapor and becomes high temperature condensed water. The sensible heat of the high temperature condensate is recovered by preheating the water-containing solid material.

整个蒸发过程中,热量消耗最大的部分,即水份蒸发过程中二次蒸汽全部的潜热得到回收利用;“降速段”干燥过程中,蒸汽升温仅是显热增加或释放的过程,明显提升了对流换热温差,缩短干燥时间的同时热量需求最小。对流换热过程的所有的蒸汽的来源均是间接传导加热污泥产生的二次蒸汽,即整个蒸发过程在蒸汽潜热回收时没有浪费,同时补充热源的加热过程中,能源的高品位也没有浪费。In the whole evaporation process, the part with the largest heat consumption, that is, all the latent heat of the secondary steam in the process of water evaporation is recycled; in the drying process of the "speed reduction section", the steam heating is only the process of increasing or releasing the sensible heat, which is obviously improved. The convective heat transfer temperature difference is reduced, and the drying time is shortened while the heat requirement is minimized. The source of all the steam in the convective heat transfer process is the secondary steam generated by indirect conduction heating of the sludge, that is, the entire evaporation process is not wasted in the recovery of steam latent heat, and the high-grade energy is not wasted in the heating process of the supplementary heat source. .

“过热蒸汽干燥”产生的二次蒸汽经过旋风除尘、高效过滤和水洗清洗后与“真空低温干燥”污泥间接换热生成冷凝水。水洗过程设置自动加药装置,清洗和消除大部分游离氨生成铵盐溶解于污水。清洗水源来自系统冷凝水,水洗清洗的污水排入污泥存储池,回收其全部热量和污染物。少量的醇类、酯类等挥发性有机物随水蒸气冷凝后进入冷凝水,冷凝水通过“电化学氧化”方式清除冷凝水中微量挥发有机物后,达标排放或回用。整个干燥过程冷凝水无污染物排放。通过水洗清洗后的“过热蒸汽”,降低了蒸汽中的污染物,同时又提升了蒸汽的饱和度。饱和蒸汽有利于提升间接传热效率并节省间接换热的“低温真空蒸发”阶段干燥时间。The secondary steam generated by "superheated steam drying" is subjected to cyclone dust removal, high-efficiency filtration and washing and washing, and then indirectly heat-exchanges with the "vacuum low temperature drying" sludge to generate condensate water. In the washing process, an automatic dosing device is set to clean and eliminate most of the free ammonia to form ammonium salts that dissolve in the sewage. The cleaning water source comes from the system condensate water, and the washed and cleaned sewage is discharged into the sludge storage tank to recover all its heat and pollutants. A small amount of volatile organic compounds such as alcohols and esters are condensed with water vapor and then enter the condensed water. The condensed water in the whole drying process is free of pollutants. Through the "superheated steam" after washing with water, the pollutants in the steam are reduced, and the saturation of the steam is improved at the same time. Saturated steam is beneficial to improve the efficiency of indirect heat transfer and save the drying time of the "low temperature vacuum evaporation" stage of indirect heat transfer.

“过热蒸汽干燥”过程蒸发水量占污泥干燥总水量比例10%-25%,系统补充热量全部用于“二次蒸汽”的显热提升,同样的补充热量可带来更高的过热度和对流换热温差。The amount of evaporated water in the process of "superheated steam drying" accounts for 10%-25% of the total water in sludge drying, and the system supplementary heat is all used to increase the sensible heat of "secondary steam". The same supplementary heat can bring higher superheat and Convective heat transfer temperature difference.

通过刮板或网带的速度调节和匹配控制出口污泥的含水率,“真空低温干燥”和“过热蒸汽干燥”联合的方式提升了污泥整体干燥速度。Through the speed adjustment and matching of the scraper or mesh belt to control the moisture content of the sludge at the outlet, the combination of "vacuum low temperature drying" and "superheated steam drying" improves the overall drying speed of the sludge.

整个干燥过程产生的全部二次蒸汽在“真空低温干燥”和污泥预热阶段,回收其全部潜热和大部分显热。相对于传统蒸汽加热干燥蒸发方式,无需设置冷却水系统。All the secondary steam generated in the whole drying process recovers all its latent heat and most of its sensible heat in the stage of "vacuum low temperature drying" and sludge preheating. Compared with the traditional steam heating drying evaporation method, there is no need to set up a cooling water system.

低温蒸发可以避免污染物迁移至冷凝水系统。冷凝水系统污染物含量低,主要成分为挥发性有机物的醇类和酯类,通过简单低成本处理即可达标排放或回用。相对于传统高温干燥蒸发方式,冷凝水不用再次返回污水处理厂或在现场进行复杂的处理。Low temperature evaporation prevents contaminants from migrating to the condensate system. The condensate water system has low pollutant content, and the main components are alcohols and esters of volatile organic compounds, which can be discharged or reused according to the standard through simple and low-cost treatment. Compared with the traditional high-temperature drying and evaporation method, the condensed water does not need to be returned to the sewage treatment plant or complex treatment on site.

系统冷凝压力小于100KPa,系统非“压力容器”。相对于传统高温干燥蒸发方式,提升了系统安全性,降低了设备制造成本和系统维护费用。采用过热蒸汽的对流换热方式,气体中氧含量极低,避免了系统爆炸的和火灾隐患。The condensing pressure of the system is less than 100KPa, and the system is not a "pressure vessel". Compared with the traditional high-temperature drying and evaporation method, the system safety is improved, and the equipment manufacturing cost and system maintenance cost are reduced. The convection heat transfer method of superheated steam is adopted, and the oxygen content in the gas is extremely low, which avoids the system explosion and fire hazard.

对这些实施例的多种修改对本领域的专业技术人员来说将是显而易见的,本文中所定义的一般原理可以在不脱离发明的精神或范围的情况下,在其它实施例中实现。因此,本发明将不会被限制于本文所示的这些实施例,而是要符合与本文所公开的原理和新颖特点相一致的最宽的范围。Various modifications to these embodiments will be readily apparent to those skilled in the art, and the generic principles defined herein may be implemented in other embodiments without departing from the spirit or scope of the invention. Thus, the present invention is not intended to be limited to the embodiments shown herein, but is to be accorded the widest scope consistent with the principles and novel features disclosed herein.

Claims (7)

1. A mechanical steam recompression drying system is characterized by comprising a sludge storage tank (110) which stores normal-temperature sludge incoming materials and is internally provided with a condensed water heat exchange coil (111), a sludge injection pump (120) which is connected with the output of the sludge storage tank (110) and is provided with a jacketed heat exchanger (121), a thin-layer evaporation dryer (130) which is connected with the output of the sludge injection pump (120), an extrusion slitting forming machine (140) which is connected with the output of the thin-layer evaporation dryer (130), a mesh belt dryer (150) which is connected with the output of the extrusion slitting forming machine (140), a dry sludge bin (160) which is connected with the output of the mesh belt dryer (150), a steam compressor (220) which is arranged between the thin-layer evaporation dryer (130) and the mesh belt dryer (150), a cyclone dust collector (230) which is connected with the mesh belt dryer (150) and is used for separating secondary steam and sludge dust, and a cyclone dust collector (230, A water washing dust collector (240) connected with the output of the cyclone dust collector 230 and used for washing and cleaning secondary steam, a condensed water buffer tank (310) connected with the thin layer evaporation dryer (130) and used for collecting condensed water, and a vacuum pump (400) connected with the condensed water buffer tank (310) and used for pumping system air to maintain vacuum and discharging non-condensable gas.
2. The mechanical vapor recompression drying system as recited in claim 1, wherein: the thin-layer evaporation dryer (130) comprises at least one cylindrical heating bin, a scraper rotor, a motor, a steam inlet (131), a steam and condensed water outlet (132), a sludge feeding hole (133) and a sludge outlet (134), wherein the scraper rotor is positioned on the inner side of the cylindrical heating bin, a plurality of scrapers are uniformly distributed on the surface of the scraper rotor, the motor is positioned on the outer side of the cylindrical heating bin and drives the scraper rotor to rotate, the steam inlet (131) is connected with the output of a water washing dust collector (240), the steam and condensed water outlet (132) is connected with the input of a condensed water buffer tank (310), the sludge feeding hole (133) is connected with the output.
3. The mechanical vapor recompression drying system as recited in claim 2, wherein: the mesh belt dryer (150) is of a closed structure, and a steam circulating fan (151) and a heater (152) are arranged in the mesh belt dryer.
4. The mechanical vapor recompression drying system as recited in claim 1, wherein: the water washing dust remover (240) comprises a condensed water spray head (241), a demister (242) positioned above the condensed water spray head (241), a dosing device (243) connected with the condensed water spray head (241), a first circulating pump (244) connected with the condensed water spray head (241), and a sewage pump (245) for returning sludge to the sludge storage tank (110).
5. The mechanical steam recompression drying system as claimed in claim 1, further comprising a granulator (161) for extruding and granulating the dry sludge in the dry sludge bin (160) and discharging the dry sludge, a second circulation pump (311) between the sludge injection pump (120) and the water scrubber (240), and a condensed water tank (320) connected to the sludge storage tank (110) and having an electrochemical oxidation descaler (321) therein.
6. The mechanical vapor recompression drying system as claimed in claim 1, further comprising a first filter (210) disposed between the thin layer evaporation dryer (130) and the vapor compressor (220), and a second filter (250) disposed between the thin layer evaporation dryer (130) and the water scrubber (240).
7. A mechanical vapor recompression drying method, comprising:
s1: wet sludge is transmitted from a sludge storage tank to a thin-layer evaporation dryer through a transmission device, in the process, the wet sludge and condensed water exchange heat in a heat exchanger, and the wet sludge and the condensed water are heated to 65-80 ℃ from 5-35 ℃ at an inlet; cooling the condensed water from 80-98 deg.C at the inlet to 15-45 deg.C at the outlet;
s2: forming a thin layer of preheated sludge in a thin layer evaporation dryer under the action of a rotary scraper blade and adhering to the inner surface of a cylinder of the evaporation dryer, wherein a negative pressure system is arranged in the cylinder, the pressure is set to be 25-47.5KPa, and the corresponding water evaporation temperature is 65-80 ℃; wherein the heat source for conducting heat exchange between the sludge and the cylinder wall comes from the steam in the step S4, the heat exchange temperature difference is 18-33 ℃, and the water content of the sludge is reduced from 80-95% to 55-65%;
s3: extruding and stripping sludge with the water content of 55-65% into thick strip sludge with the width of 2-5mm, and then feeding the thick strip sludge into a mesh belt dryer;
s4: the sludge entering the mesh belt dryer is subjected to heat convection with superheated steam in the mesh belt transmission process, further evaporated and dried, enters a dry sludge bin, is extruded and granulated by a granulator, and is discharged, wherein the water content of the sludge is further evaporated and dried from 55-65% to form sludge with the water content of 20-45%, and the drying process in the mesh belt dryer is completed; after saturated steam at the outlet of the compressor enters a mesh belt dryer, the degree of superheat is raised by heating through a heater to 20-50 ℃, and forced circulation and sludge convection heat exchange are carried out through a circulating fan; the surplus superheated steam enters cyclone separation, water washing for dedusting and filtering to become clean saturated steam and then enters step S2 again;
s5: filtering the secondary steam generated in the evaporation process in the step S2 by using a filter, compressing the secondary steam by using a steam compressor, and then performing the step S4, wherein condensed water from a condensed water buffer tank is sprayed into a suction inlet of the steam compressor, the compression ratio is 2.0-4.5, and the temperature of the steam is raised by 18-33 ℃;
s6: a part of the condensed water enters step S5 to reduce the superheat degree of the compressor exhaust; after a part of the sludge enters the water washing dust remover in the step S4, discharging the part of the sludge into a sludge tank; the rest part of condensed water enters a condensed water tank after heat exchange through the heat exchanger in the step S1, and is discharged or recycled after trace organic matters are removed through an electrochemical oxidation descaler;
s7: and exhausting the non-condensable gas in the condensed water buffer tank and the condensed water tank by using a vacuum pump until the process is finished.
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