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CN101186420A - Odor Control System of Sludge Drying Project - Google Patents

Odor Control System of Sludge Drying Project Download PDF

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CN101186420A
CN101186420A CNA2007101571768A CN200710157176A CN101186420A CN 101186420 A CN101186420 A CN 101186420A CN A2007101571768 A CNA2007101571768 A CN A2007101571768A CN 200710157176 A CN200710157176 A CN 200710157176A CN 101186420 A CN101186420 A CN 101186420A
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sludge
sludge drying
mud
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drying
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CN100575284C (en
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翁焕新
苏闽华
陈海燕
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Zhejiang University ZJU
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Abstract

本发明公开了一种污泥干化工程的臭气控制系统。该系统的高能离子发生器通过通风管道分别与污泥储存系统和混气室相连接,混气室与污泥干化和成粒装置、水膜麻石除尘除气装置、烟囱相连接,污泥储存系统与生物土壤滤床相连接,并与独立热源、温度调节器、污泥干化和成粒装置相连接,污泥干化车间通过封闭式输送带分别与污泥储存系统和干化污泥成品库相连接,干化污泥成品库和污泥干化车间通过通风管道与生物土壤滤床相连接。本发明集成了化学、物理和生物除臭方法,并运用了离子脱臭新技术,不仅臭气去除率高,而且具有应急功能,实践表明,采用该项技术臭气排放含量远远低于国家的排放标准,污泥干化工程的周边环境与生产现场均无臭气味,使污泥干化实现清洁生产。

Figure 200710157176

The invention discloses an odor control system for a sludge drying project. The high-energy ion generator of the system is respectively connected with the sludge storage system and the air mixing chamber through the ventilation pipe, and the air mixing chamber is connected with the sludge drying and granulation device, the water film granite dedusting and degassing device, and the chimney. The storage system is connected with the biological soil filter bed, and connected with the independent heat source, temperature regulator, sludge drying and granulation device, and the sludge drying workshop is respectively connected with the sludge storage system and the drying sewage The sludge finished product warehouse is connected, and the dried sludge finished product warehouse and the sludge drying workshop are connected with the biological soil filter bed through ventilation pipes. The invention integrates chemical, physical and biological deodorization methods, and uses the new technology of ion deodorization, which not only has a high odor removal rate, but also has an emergency function. Practice shows that the odor emission content of this technology is far lower than the national standard. Discharge standards, the surrounding environment of the sludge drying project and the production site have no odor, so that the sludge drying can achieve clean production.

Figure 200710157176

Description

污泥干化工程的臭气控制系统 Odor Control System of Sludge Drying Project

技术领域technical field

本发明涉及一种污泥干化工程的臭气控制系统。The invention relates to an odor control system of a sludge drying project.

背景技术Background technique

城市生活污水和工业废水必须经过处理,达标才能排放,这是现代环境保护的重要措施,然而城市污水在得到净化处理的同时,会产生相当于污水体积0.3%~0.5%或污水质量1%~2%的污泥。根据有关资料,到2010年和2020年我国城市污水的排放量将分别达到440×108m3/日和536×108m3/日,随着国家经济的快速发展和城市人口的迅速增长,城市污水的数量在不断地增加,与此同时人们对环境质量的要求也越来越高,工业废水和城市生活污水的处理率也将不断提高,污水处理厂产生的污泥数量将与日俱增。Urban domestic sewage and industrial wastewater must be treated to meet the standards before they can be discharged. This is an important measure for modern environmental protection. However, when urban sewage is purified, it will produce an amount equivalent to 0.3% to 0.5% of the volume of sewage or 1% to 1% of the quality of sewage. 2% sludge. According to relevant data, by 2010 and 2020, the discharge of urban sewage in China will reach 440×10 8 m 3 /day and 536×10 8 m 3 /day respectively. With the rapid development of the national economy and the rapid growth of urban population , the amount of urban sewage is constantly increasing, and at the same time, people's requirements for environmental quality are getting higher and higher. The treatment rate of industrial wastewater and urban domestic sewage will also continue to increase, and the amount of sludge produced by sewage treatment plants will increase day by day.

污水处理厂污泥是一种由有机残片、细菌菌体、无机颗粒和胶体等组成的极其复杂的非均质体,由于污水中绝大部分污染物转移到污泥中,这就决定了污水处理厂产生的污泥具有含水率高和数量大,且富集高浓度污染物的特点,如果这种城市污泥得不到妥善的处理,将会带来二次污染,给生态环境造成严重的威胁,因此,城市污泥的安全处置是全世界共同面临的难题,对污泥进行无害化、减量化和资源化处理成为国内外彻底消除城市污泥二次污染的共同目标。Sewage treatment plant sludge is an extremely complex heterogeneous body composed of organic debris, bacterial cells, inorganic particles and colloids. Since most of the pollutants in the sewage are transferred to the sludge, this determines the quality of the sewage. The sludge produced by the treatment plant has the characteristics of high water content, large quantity, and enrichment of high-concentration pollutants. If this urban sludge is not properly treated, it will cause secondary pollution and cause serious damage to the ecological environment. Therefore, the safe disposal of municipal sludge is a common problem faced by the whole world, and the harmless, reduction and resource treatment of sludge has become the common goal of completely eliminating the secondary pollution of municipal sludge at home and abroad.

多年来,国内外专家与技术人员通过对各种污泥处理方法的实践,得出的共识是污泥干化首先使污泥达到减量化,是最终实现污泥无害化和资源化处理的必要过程和关键一环。从污水处理厂产生的污泥,通过机械脱水,含水率一般在75%~85%之间,通过干化过程,如果将污泥的含水率降到40%以下,体积可以减少三分之二以上,我们已经发明了利用独立热源或利用烟气余热干化污泥的方法,并建立了行之有效的工艺与研制了与工艺相配套的机械设备,从而使污泥干化能在较低的运行成本下连续地进行,既能使污泥得到显著的减量,又能使污泥90%以上的原始热值得以保存,使污泥成为可利用的资源。Over the years, experts and technicians at home and abroad, through the practice of various sludge treatment methods, have reached a consensus that sludge drying first reduces the amount of sludge, and finally realizes the harmless and resourceful treatment of sludge. The necessary process and key link. The sludge produced from the sewage treatment plant, through mechanical dehydration, generally has a moisture content between 75% and 85%. Through the drying process, if the moisture content of the sludge is reduced to below 40%, the volume can be reduced by two-thirds Above, we have invented the method of using independent heat source or waste heat of flue gas to dry sludge, and established an effective process and developed mechanical equipment matching the process, so that the sludge drying energy can be reduced It can be carried out continuously at a low operating cost, which can not only reduce the amount of sludge significantly, but also preserve more than 90% of the original heat value of the sludge, making the sludge a usable resource.

由于污泥中含有大量的有机污染物,在微生物的作用下,污泥会产生大量的臭气,臭气的物质组成可以分为4类,第一类是含硫化合物,如硫化氢、硫醇类、硫醚类和噬吩类等;第二类是含氮化合物,如氨、胺类、酞胺类以及吲哚类等;第三类是烃类化合物,如烷烃、烯烃、炔烃以及芳香烃等;第四类是含氧有机物,如醇、醛、酮、酚以及有机酸等,其中浓度比较高和影响比较大的臭气有氨气、硫化氢、甲硫醇、丙硫醇、甲基硫等。在污泥干化工程中,污泥储存预处理阶段是这些臭气主要的释放源,在污泥干化和成粒阶段,以及干化污泥冷却阶段,尽管因为污泥中的微生物几乎已经为零,不具备产生新臭气的条件,但是,污泥中原有的臭气物质会在这时大量释放。臭气的扩散会严重破坏空气环境质量,直接影响人体健康和工作效率,既使是微量的恶臭物质进入环境,都会使人感到不适,出现头痛、头昏、恶心、呕吐、食欲不振和精神不集中等症状,长期在受臭气污染的空气环境下工作,各种炎症的发病率增高,并对呼吸系统、循环系统、消化系统和生殖系统也有影响。为了彻底消除污泥干化工程中释放的臭气,我们针对污泥干化工程不同阶段臭气释放的特点,结合具体的工艺情况,建立了污泥干化工程中的臭气控制系统,从而使污泥干化能在清洁生产的工作环境下进行。Because the sludge contains a large amount of organic pollutants, under the action of microorganisms, the sludge will produce a large amount of odor. The material composition of the odor can be divided into 4 categories. The first category is sulfur-containing compounds, such as hydrogen sulfide, sulfur Alcohols, thioethers, and phagephages, etc.; the second category is nitrogen-containing compounds, such as ammonia, amines, phthalamines, and indoles; the third category is hydrocarbon compounds, such as alkanes, alkenes, and alkynes and aromatic hydrocarbons, etc.; the fourth category is oxygen-containing organic compounds, such as alcohols, aldehydes, ketones, phenols, and organic acids, among which odors with relatively high concentrations and relatively large impacts include ammonia, hydrogen sulfide, methyl mercaptan, and propyl sulfide. Alcohol, methyl sulfide, etc. In the sludge drying project, the sludge storage pretreatment stage is the main release source of these odors. In the sludge drying and granulation stage, as well as the drying sludge cooling stage, although the microorganisms in the sludge have almost It is zero, and there is no condition for generating new odor, but the original odor substances in the sludge will be released in large quantities at this time. The spread of odor will seriously damage the quality of the air environment and directly affect human health and work efficiency. Even if a small amount of odorous substances enter the environment, it will make people feel uncomfortable, headache, dizziness, nausea, vomiting, loss of appetite and listlessness Concentration and other symptoms, long-term work in the air environment polluted by odor, the incidence of various inflammations increases, and it also affects the respiratory system, circulatory system, digestive system and reproductive system. In order to completely eliminate the odor released in the sludge drying project, we have established an odor control system in the sludge drying project according to the characteristics of the odor release in different stages of the sludge drying project, combined with the specific process conditions, so that The sludge drying can be carried out in a clean production working environment.

发明内容Contents of the invention

本发明的目的是提供一种污泥干化工程的臭气控制系统。The object of the present invention is to provide an odor control system for sludge drying engineering.

污泥干化工程的臭气控制系统具有高能离子发生器,高能离子发生器通过第一通风管道与污泥储存罐相连接,或者高能离子发生器通过第二通风管道与封闭式污泥储存库相连接,高能离子发生器通过第三通风管道与混气室相连接,混气室通过第八通风管道与污泥干化和成粒装置相连接,混气室与水膜麻石除尘除气装置、第五引风机、烟囱相连接,污泥储存罐或封闭式污泥储存库构成污泥储存系统,污泥储存系统经第二引风机通过第五通风管道与生物土壤滤床相连接,或者污泥储存系统经第一引风机通过第四通风管道与独立热源相连接,独立热源通过温度调节器与污泥干化和成粒装置相连接,烟气余热与污泥干化和成粒装置相连接,污泥干化和成粒装置、第一封闭式输送带、第二封闭式输送带构成污泥干化车间,污泥干化车间经第二封闭式输送带与污泥储存系统相连接,污泥干化车间经第四引风机通过第七通风管道与生物土壤滤床相连接,污泥干化和成粒装置经第一封闭式输送带与干化污泥成品库相连接,干化污泥成品库经第三引风机通过第六通风管道与生物土壤滤床相连接。The odor control system of the sludge drying project has a high-energy ion generator. The high-energy ion generator is connected to the sludge storage tank through the first ventilation duct, or the high-energy ion generator is connected to the closed sludge storage tank through the second ventilation duct. The high-energy ion generator is connected to the air mixing chamber through the third ventilation pipe, the air mixing chamber is connected to the sludge drying and granulation device through the eighth ventilation pipe, and the air mixing chamber is connected to the water film granite dedusting and degassing device , the fifth induced draft fan and the chimney are connected, the sludge storage tank or the closed sludge storage tank constitutes the sludge storage system, and the sludge storage system is connected to the biological soil filter bed through the second induced draft fan and the fifth ventilation pipe, or The sludge storage system is connected to the independent heat source through the first induced draft fan through the fourth ventilation pipe, the independent heat source is connected to the sludge drying and granulating device through the temperature regulator, and the waste heat of the flue gas is connected to the sludge drying and granulating device The sludge drying and granulating device, the first closed conveyor belt, and the second closed conveyor belt constitute the sludge drying workshop, and the sludge drying workshop is connected with the sludge storage system through the second closed conveyor belt connection, the sludge drying workshop is connected to the biological soil filter bed through the fourth induced draft fan and the seventh ventilation pipe, and the sludge drying and granulation device is connected to the dried sludge finished product warehouse through the first closed conveyor belt. The finished product warehouse of dried sludge is connected with the biological soil filter bed through the third induced draft fan and the sixth ventilation pipe.

在污泥储存罐内设有第一紫外灯,在封闭式污泥储存库设有第二紫外灯,A first ultraviolet lamp is provided in the sludge storage tank, and a second ultraviolet lamp is provided in the closed sludge storage tank,

本发明具有的有益效果是:1)在整个污泥干化工程中,从污泥储存到污泥干化,直至干化污泥冷却均在封闭和负压条件下进行,避免了臭气的外溢;2)集成了化学、物理和生物除臭方法,特别是运用了离子脱臭的高新技术,不仅使除臭效果大大提高,而且具有占地面积小、安装调试简单、运行成本低等特点;3)本臭气控制系统不仅臭气去除率高,而且具有应急功能,因此,即使在污泥干化过程中出现意外事故而停止生产,仍不影响除臭系统的正常运行。本发明已在多个污泥干化工程投入实际运用,实践表明,采用该项技术臭气排放含量远远低于国家的排放标准,污泥干化工程的周边环境与生产现场均无臭气味,实现了污泥干化的清洁生产。The present invention has the beneficial effects: 1) In the whole sludge drying project, from sludge storage to sludge drying, until the cooling of dried sludge is carried out under closed and negative pressure conditions, avoiding the foul smell Spillover; 2) Integrate chemical, physical and biological deodorization methods, especially the use of high-tech ion deodorization, which not only greatly improves the deodorization effect, but also has the characteristics of small footprint, simple installation and commissioning, and low operating costs; 3) The odor control system not only has a high odor removal rate, but also has an emergency function. Therefore, even if an accident occurs during the sludge drying process and the production is stopped, the normal operation of the deodorization system will not be affected. The present invention has been put into practical use in many sludge drying projects. Practice shows that the odor emission content of this technology is far lower than the national emission standard, and the surrounding environment and production site of the sludge drying project have no odor. , Realized the clean production of sludge drying.

附图说明Description of drawings

附图是污泥干化工程的臭气控制系统结构示意图;The attached drawing is a schematic structural diagram of the odor control system of the sludge drying project;

图中:高能离子发生器1、污泥储存罐2、封闭式污泥储存库3、独立热源4、烟气余热5、污泥干化和成粒装置6、干化污泥成品库7、生物土壤滤床8、水膜麻石除尘除气装置9、烟囱10、第一引风机11、第二引风机12、第三引风机13、第四引风机14、温度调节器15、混气室16、第一通风管道17、第二通风管道18、第三通风管道19、第四通风管道20、第五通风管道21、第六通风管道22、第七通风管道23、第八通风管道24、第五引风机25、第一紫外灯26、第二紫外灯27、第一封闭式输送带28、第二封闭式输送带29、污泥储存系统30、污泥干化车间31。In the figure: high-energy ion generator 1, sludge storage tank 2, closed sludge storage 3, independent heat source 4, flue gas waste heat 5, sludge drying and granulation device 6, dried sludge finished product warehouse 7, Biological soil filter bed 8, water film granite dedusting and degassing device 9, chimney 10, first induced draft fan 11, second induced draft fan 12, third induced draft fan 13, fourth induced draft fan 14, temperature regulator 15, air mixing chamber 16. The first ventilation duct 17, the second ventilation duct 18, the third ventilation duct 19, the fourth ventilation duct 20, the fifth ventilation duct 21, the sixth ventilation duct 22, the seventh ventilation duct 23, the eighth ventilation duct 24, The fifth induced draft fan 25 , the first ultraviolet lamp 26 , the second ultraviolet lamp 27 , the first enclosed conveyor belt 28 , the second enclosed conveyor belt 29 , the sludge storage system 30 , and the sludge drying workshop 31 .

具体实施方式Detailed ways

如附图所示,污泥干化工程的臭气控制系统,其特征在于具有高能离子发生器1,高能离子发生器1通过第一通风管道17与污泥储存罐2相连接,或者高能离子发生器1通过第二通风管道18与封闭式污泥储存库3相连接,高能离子发生器1通过第三通风管道19与混气室16相连接,混气室16通过第八通风管道24与污泥干化和成粒装置6相连接,混气室16与水膜麻石除尘除气装置9、第五引风机25、烟囱10相连接,污泥储存罐2或封闭式污泥储存库3构成污泥储存系统30,在污泥储存罐2内设有第一紫外灯26,在封闭式污泥储存库3设有第二紫外灯27,污泥储存系统30经第二引风机12通过第五通风管道21与生物土壤滤床8相连接,或者污泥储存系统30经第一引风机11通过第四通风管道20与立热源4相连接,独立热源4通过温度调节器15与污泥干化和成粒装置6相连接,烟气余热5与污泥干化和成粒装置6相连接,污泥干化和成粒装置6、第一封闭式输送带28、第二封闭式输送带29构成污泥干化车间31,污泥干化车间31经第二封闭式输送带29与污泥储存系统30相连接,污泥干化车间31经第四引风机14通过第七通风管道23与生物土壤滤床8相连接,污泥干化和成粒装置6经第一封闭式输送带28与干化污泥成品库7相连接,干化污泥成品库7经第三引风机13通过第六通风管道22与生物土壤滤床8相连接。As shown in the accompanying drawings, the odor control system of the sludge drying project is characterized in that it has a high-energy ion generator 1, and the high-energy ion generator 1 is connected to the sludge storage tank 2 through the first ventilation pipe 17, or the high-energy ion generator 1 The generator 1 is connected to the closed sludge storage 3 through the second ventilation duct 18, the high-energy ion generator 1 is connected to the air mixing chamber 16 through the third ventilation duct 19, and the air mixing chamber 16 is connected to the air mixing chamber 16 through the eighth ventilation duct 24. The sludge drying and granulation device 6 is connected, the air mixing chamber 16 is connected with the water film granite dedusting and degassing device 9, the fifth induced draft fan 25, and the chimney 10, the sludge storage tank 2 or the closed sludge storage 3 To form a sludge storage system 30, a first ultraviolet lamp 26 is provided in the sludge storage tank 2, a second ultraviolet lamp 27 is provided in the closed sludge storage 3, and the sludge storage system 30 passes through the second induced draft fan 12. The fifth ventilation pipe 21 is connected with the biological soil filter bed 8, or the sludge storage system 30 is connected with the vertical heat source 4 through the first induced draft fan 11 through the fourth ventilation pipe 20, and the independent heat source 4 is connected with the sludge through the temperature regulator 15. The drying and granulating device 6 is connected, the flue gas waste heat 5 is connected with the sludge drying and granulating device 6, the sludge drying and granulating device 6, the first closed conveyor belt 28, the second closed conveyor The belt 29 constitutes a sludge drying workshop 31, the sludge drying workshop 31 is connected with the sludge storage system 30 through the second closed conveyor belt 29, and the sludge drying workshop 31 passes through the seventh ventilation duct through the fourth induced draft fan 14 23 is connected with the biological soil filter bed 8, the sludge drying and granulating device 6 is connected with the dried sludge finished product warehouse 7 through the first closed conveyor belt 28, and the dried sludge finished product warehouse 7 is passed through the third induced draft fan 13 is connected with the biological soil filter bed 8 through the sixth ventilation pipe 22.

高能离子发生器1产生的可控浓度的正、负氧离子空气,通过第一通风管道17送入污泥储存罐2,或者通过第二通风管道18送入封闭式污泥储存库3,污泥储存罐2或封闭式污泥储存库3中释放的臭气分子在与离子空气的相互作用下,最终形成二氧化碳和水,高能离子发生器1产生的可控浓度的正、负氧离子空气通过第三通风管道19送入混气室16,与通过第八通风管道24来自污泥干化和成粒装置6排放的尾气混合,离子空气一方面与尾气中的臭气分子发生反应,从而降低臭气分子的浓度,另一方面使尾气中的微小颗粒荷电产生凝聚效应,从而降低尘埃的浓度,来自污泥干化和成粒装置6排放的尾气在混气室16与来自高能离子发生器1的离子空气相互作用后,进入水膜麻石除尘除气装置9,进一步除尘和经过药液洗脱除臭气后,通过第五引风机25,送入烟囱10完全达标排放。The positive and negative oxygen ion air with controllable concentration produced by the high-energy ion generator 1 is sent into the sludge storage tank 2 through the first ventilation duct 17, or is sent into the closed sludge storage tank 3 through the second ventilation duct 18, and the sewage The odor molecules released in the mud storage tank 2 or the closed sludge storage 3 will eventually form carbon dioxide and water under the interaction with the ionic air, and the positive and negative oxygen ion air with controllable concentration generated by the high-energy ion generator 1 Send into the air mixing chamber 16 through the third ventilation duct 19, mix with the tail gas discharged from the sludge drying and granulation device 6 through the eighth ventilation duct 24, and the ionized air reacts with the odor molecules in the tail gas on the one hand, thereby Reduce the concentration of odor molecules, and on the other hand, charge the tiny particles in the tail gas to produce agglomeration effect, thereby reducing the concentration of dust. After the ionized air in the generator 1 interacts, it enters the water film granite dedusting and degassing device 9, and after further dedusting and deodorization through the elution of the liquid medicine, it passes through the fifth induced draft fan 25 and is sent to the chimney 10 for discharge that is completely up to standard.

污泥储存是污泥干化工程中一个重要的组成部分,也是污泥臭气产生和释放的重要阶段,在污泥干化工程中,污泥的储存通常采用污泥储存罐或封闭式污泥储存库,所述的污泥储存罐2或封闭式污泥储存库3构成污泥干化工程中的污泥储存系统30,在污泥储存罐2内分别安装有第一紫外灯26,在封闭式污泥储存库3安装有第二紫外灯27,紫外灯起灭菌作用,遏制污泥在储存过程中因微生物的活动继续产生臭气,污泥储存系统30与生物土壤滤床8相连接,第二引风机12将从污泥储存罐2或封闭式污泥储存库3排出的气体,通过第五通风管道21送入生物土壤滤床8,排出气体中的残余臭气由微生物消除,如果高能离子发生器1因故障暂时停止工作,生物土壤滤床8能够净化污泥储存系统30排出气体中的全部臭气。污泥干化的能源可以来自独立热源,也可以利用烟气余热,独立热源4产生的热量通过温度调节器15,进入污泥干化和成粒装置6干化污泥,烟气余热5直接进入污泥干化和成粒装置6干化污泥,当污泥干化的能源来自独立热源时,污泥储存系统30可以与独立热源4相连接,第一引风机11将从污泥储存罐2或封闭式污泥储存库3排出的气体,通过第四通风管道20送入独立热源4,排出气体中的残余臭气由高温消除,如果高能离子发生器1因故障暂时停止工作,独立热源4能够消除污泥储存系统30排出气体中的全部臭气。Sludge storage is an important part of the sludge drying project, and it is also an important stage for the generation and release of sludge odor. In the sludge drying project, sludge storage tanks or closed sewage tanks are usually used for sludge storage. The sludge storage tank, the sludge storage tank 2 or the closed sludge storage tank 3 constitutes the sludge storage system 30 in the sludge drying project, and the first ultraviolet lamp 26 is respectively installed in the sludge storage tank 2, A second ultraviolet lamp 27 is installed in the closed sludge storage warehouse 3, and the ultraviolet lamp plays a role in sterilization to prevent the sludge from continuing to generate odor due to the activities of microorganisms during the storage process. The sludge storage system 30 is connected with the biological soil filter bed 8 connected, the second induced draft fan 12 sends the gas discharged from the sludge storage tank 2 or the closed sludge storage 3 through the fifth ventilation pipe 21 into the biological soil filter bed 8, and the residual odor in the discharged gas is produced by microorganisms. Eliminate, if the high-energy ion generator 1 temporarily stops working due to failure, the biological soil filter bed 8 can purify all odors in the sludge storage system 30 discharge gas. The energy for sludge drying can come from an independent heat source, or waste heat from the flue gas can be used. The heat generated by the independent heat source 4 passes through the temperature regulator 15 and enters the sludge drying and granulation device 6 to dry the sludge. The waste heat of the flue gas 5 directly Enter the sludge drying and granulating device 6 to dry the sludge. When the energy for sludge drying comes from an independent heat source, the sludge storage system 30 can be connected with the independent heat source 4, and the first induced draft fan 11 will store the sludge from the sludge. The gas discharged from the tank 2 or the closed sludge storage 3 is sent to the independent heat source 4 through the fourth ventilation duct 20, and the residual odor in the discharged gas is eliminated by high temperature. If the high-energy ion generator 1 temporarily stops working due to failure, the independent The heat source 4 can eliminate all odors in the exhaust gas from the sludge storage system 30 .

第二封闭式输送带29将来自具有污泥储存罐2或封闭式污泥储存库3的污泥储存系统30的污泥送入污泥干化和成粒装置6,利用独立热源4或烟气余热5对污泥进行干化,具有污泥干化和成粒装置6、第一封闭式输送带28、第二封闭式输送带29的污泥干化车间31空气中可能存在的臭气,由第四引风机14通过第七通风管道23送入生物土壤滤床8,由微生物消除。通过污泥干化和成粒装置6的干化污泥颗粒,由第一封闭式输送带28送入干化污泥成品库7,干化污泥颗粒在冷却过程释放的少量残余臭气,由第三引风机13通过第六通风管道22送入生物土壤滤床8,由微生物消除。The second closed conveyor belt 29 sends the sludge from the sludge storage system 30 with the sludge storage tank 2 or the closed sludge storage 3 into the sludge drying and granulating device 6, and utilizes the independent heat source 4 or smoke Gas waste heat 5 dries the sludge, and there is a sludge drying workshop 31 with sludge drying and granulation device 6, the first closed conveyor belt 28, and the second closed conveyor belt 29. Odor that may exist in the air , sent into the biological soil filter bed 8 by the fourth induced draft fan 14 through the seventh ventilation duct 23, and eliminated by microorganisms. The dried sludge particles passing through the sludge drying and granulating device 6 are sent to the dried sludge product warehouse 7 by the first closed conveyor belt 28, and a small amount of residual odor released by the dried sludge particles during the cooling process, It is sent into the biological soil filter bed 8 by the third induced draft fan 13 through the sixth ventilation pipe 22, and is eliminated by microorganisms.

Claims (2)

1. the stench control system of a sludge drying engineering, it is characterized in that having energetic ion producer 1, energetic ion producer 1 is connected with mud hold-up vessel 2 by first ventilator trunk 17, perhaps be connected with closed mud storage vault 3 by second ventilator trunk 18, energetic ion producer 1 is connected with mixing chamber 16 by the 3rd vent-pipe road 19, mixing chamber 16 is connected with granulating apparatus 6 with sludge drying by the 8th ventilator trunk 24, mixing chamber 16 and moisture film fiber crops stone dedusting degasifying device 9, the 5th induced draft fan 25, chimney 10 is connected, mud hold-up vessel 2 or closed mud storage vault 3 constitute mud stocking system 30, mud stocking system 30 is connected with biological soil filter bed 8 by five-way airduct road 21 through second induced draft fan 12, perhaps mud stocking system 30 is connected with independent thermal source 4 by four-way airduct road 20 through first induced draft fan 11, independent thermal source 4 is connected with granulating apparatus 6 with sludge drying by thermoswitch 15, fume afterheat 5 is connected with granulating apparatus 6 with sludge drying, sludge drying and granulating apparatus 6, the first closed conveying belt 28, the second closed conveying belt 29 constitutes sludge drying workshop 31, sludge drying workshop 31 is connected with mud stocking system 30 through the second closed conveying belt 29, sludge drying workshop 31 is connected with biological soil filter bed 8 by the 7th ventilator trunk 23 through the 4th induced draft fan 14, sludge drying is connected with dewatered sludge stockyard 7 through the first closed conveying belt 28 with granulating apparatus 6, and dewatered sludge stockyard 7 is connected with biological soil filter bed 8 by the 6th ventilator trunk 22 through the 3rd induced draft fan 13.
2. mud hold-up vessel 2 according to claim 1 or closed mud storage vault 3 is characterized in that, are provided with first ultraviolet lamp 26 in the mud hold-up vessel 2, are provided with second ultraviolet lamp 27 in the closed mud storage vault 3.
CN200710157176A 2007-11-27 2007-11-27 The stench control system of sludge drying engineering Expired - Fee Related CN100575284C (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104971606A (en) * 2015-06-26 2015-10-14 汤雄跃 Artificial stone waste gas processing system
CN105967488A (en) * 2016-06-21 2016-09-28 普利资环境科技(苏州)有限公司 Sludge drying treatment system with deodorization function
CN108298791A (en) * 2018-03-22 2018-07-20 天津五洲同创空调制冷设备有限公司 A kind of novel multi-functional sludge heat pump desiccation machine
CN111795398A (en) * 2020-06-19 2020-10-20 壹智控(北京)科技有限公司 Novel process and system for blending and burning muddy combustible materials in circulating fluidized bed boiler
CN112851064A (en) * 2021-03-04 2021-05-28 天津科技大学 Method for reducing odor release of sludge dried finished product

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104971606A (en) * 2015-06-26 2015-10-14 汤雄跃 Artificial stone waste gas processing system
CN104971606B (en) * 2015-06-26 2017-07-28 广西利升石业有限公司 Artificial hilllock stone exhaust treatment system
CN105967488A (en) * 2016-06-21 2016-09-28 普利资环境科技(苏州)有限公司 Sludge drying treatment system with deodorization function
CN108298791A (en) * 2018-03-22 2018-07-20 天津五洲同创空调制冷设备有限公司 A kind of novel multi-functional sludge heat pump desiccation machine
CN111795398A (en) * 2020-06-19 2020-10-20 壹智控(北京)科技有限公司 Novel process and system for blending and burning muddy combustible materials in circulating fluidized bed boiler
CN112851064A (en) * 2021-03-04 2021-05-28 天津科技大学 Method for reducing odor release of sludge dried finished product

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