CN104098240B - Sewage sludge treatment plant - Google Patents
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- CN104098240B CN104098240B CN201410381208.2A CN201410381208A CN104098240B CN 104098240 B CN104098240 B CN 104098240B CN 201410381208 A CN201410381208 A CN 201410381208A CN 104098240 B CN104098240 B CN 104098240B
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- 239000010801 sewage sludge Substances 0.000 title claims abstract description 15
- 238000001035 drying Methods 0.000 claims abstract description 57
- 238000007710 freezing Methods 0.000 claims abstract description 53
- 230000008014 freezing Effects 0.000 claims abstract description 53
- 239000010802 sludge Substances 0.000 claims description 140
- 230000007246 mechanism Effects 0.000 claims description 26
- 239000007788 liquid Substances 0.000 claims description 19
- 239000012530 fluid Substances 0.000 claims description 10
- 230000007306 turnover Effects 0.000 claims description 8
- 238000004108 freeze drying Methods 0.000 claims description 7
- 238000011085 pressure filtration Methods 0.000 claims description 4
- 238000000034 method Methods 0.000 abstract description 15
- 230000008569 process Effects 0.000 abstract description 7
- 239000000126 substance Substances 0.000 abstract description 6
- 238000003825 pressing Methods 0.000 abstract description 4
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- Treatment Of Sludge (AREA)
Abstract
Description
技术领域technical field
本发明涉及污水污泥处理领域,具体地说是一种污水污泥处理装置。The invention relates to the field of sewage sludge treatment, in particular to a sewage sludge treatment device.
背景技术Background technique
污水处理过程中产生大量的污泥,其数量约占处理水量的0.3%-0.5%,污泥的处理投资及运行成本非常巨大,用于污泥处理的费用一般占污水处理厂运行费用的20%-50%,给污水处理带来了沉重的负担。污泥脱水是污泥处理的关键环节,对于污泥后续的干燥、输送、填埋、资源化利用等都具有重要意义。污泥脱水的关键是改善污泥的脱水性能,当前传统的处理方法是通过投加絮凝剂先进行调理,然后压滤机进行机械脱水,形成含水率60%左右的污泥外运进行填埋、发酵制肥等。投加絮凝剂预处理方法是通过絮凝剂的絮凝作用,减小了污泥和水的亲和力,改变了污泥中水分的存在形式,中和污水中相反的电荷,压缩双电层,对已脱稳的凝聚颗粒起吸附架桥的作用,使其快速形成大的絮体,从而使胶体脱稳凝聚,实现固液分离。絮凝剂投加量以占污泥固体干重的百分比计,不同的絮凝剂投加量会有所区别。虽然通过投加絮凝剂的方法能显著改善污泥的脱水性能,但是由于需要大量的絮凝剂,不仅增加污泥处理的成本,而且大量的絮凝剂会增加到脱水后的污泥中,加大污泥的处理量。其他预处理方法如超声处理需要消耗的大量热量,且需要增设超声处理装置;采用生物法和热力学法需要消耗生物制剂及热量。A large amount of sludge is produced in the process of sewage treatment, which accounts for about 0.3%-0.5% of the treated water. The investment and operation cost of sludge treatment are very huge, and the cost of sludge treatment generally accounts for 20% of the operating cost of sewage treatment plants. %-50%, bringing a heavy burden to sewage treatment. Sludge dehydration is a key link in sludge treatment, and it is of great significance to the subsequent drying, transportation, landfill, and resource utilization of sludge. The key to sludge dewatering is to improve the dewatering performance of sludge. The current traditional treatment method is to condition it first by adding flocculant, and then perform mechanical dehydration by filter press to form sludge with a moisture content of about 60% and transport it to landfill. , fermented fertilizer, etc. The pretreatment method of adding flocculant is to reduce the affinity between sludge and water through the flocculation of flocculant, change the existence form of water in sludge, neutralize the opposite charge in sewage, compress the electric double layer, and The destabilized coagulated particles play the role of adsorption and bridging, making them quickly form large flocs, so that the colloids can be destabilized and coagulated to achieve solid-liquid separation. The dosage of flocculant is calculated as a percentage of the dry weight of sludge solids, and the dosage of different flocculants will be different. Although the dewatering performance of sludge can be significantly improved by adding flocculants, due to the need for a large amount of flocculants, not only the cost of sludge treatment will be increased, but also a large amount of flocculants will be added to the dehydrated sludge, increasing the sludge treatment volume. Other pretreatment methods, such as ultrasonic treatment, consume a lot of heat and need to add ultrasonic treatment devices; the use of biological methods and thermodynamic methods requires the consumption of biological agents and heat.
采用冷冻方法对污泥进行前期预处理,污泥经过反复冷冻后可破坏污泥与水的结合力和破坏胶体的结构(类似于冷冻后的内置豆腐),使胶体脱稳凝聚且细胞膜破裂,使得用机械方法难以去除的细胞内部水渗析出来形成机械方法易以去除的间隙水,污泥颗粒迅速沉降,脱水速度比冷冻前高几十倍,采用冷冻方法不要添加药剂,可节约药剂成本,且不会额外增加后期的污泥处理量,再结合污泥后续处理方法,完成污泥深度减量化处理。The freezing method is used to pre-treat the sludge. After the sludge is repeatedly frozen, it can destroy the binding force between the sludge and water and the structure of the colloid (similar to the built-in tofu after freezing), so that the colloid is destabilized and coagulated and the cell membrane is broken. The water inside the cells that is difficult to remove by mechanical means is dialyzed to form interstitial water that is easy to remove by mechanical means. The sludge particles settle rapidly, and the dehydration speed is dozens of times higher than that before freezing. Using the freezing method does not require adding chemicals, which can save the cost of chemicals. And it will not increase the amount of sludge treatment in the later stage, and combined with the subsequent treatment method of sludge, the deep reduction treatment of sludge will be completed.
然而,现有技术对污泥的冷冻主要依赖自然环境,即在寒冷的天气下将污泥置于室外依靠自然环境降温至-10℃左右进行冷冻和解冻,但该工艺存在效率低、耗时长的问题,且如果正在南方地区或者非冬天情况下无法操作,自然条件要求较为苛刻。另外,现有技术使用外力对污泥进行冷冻和解冻需要对污泥进行制冷和制热双重的能量,成本非常高,故难以推广应用。However, in the prior art, the freezing of sludge mainly relies on the natural environment, that is, the sludge is placed outdoors in cold weather and depends on the natural environment to cool down to about -10°C for freezing and thawing, but this process has low efficiency and takes a long time. problems, and if it is not possible to operate in the southern region or in non-winter conditions, the natural conditions are more demanding. In addition, in the prior art, using external force to freeze and thaw sludge requires dual energy for cooling and heating the sludge, and the cost is very high, so it is difficult to popularize and apply.
发明内容Contents of the invention
有鉴于此,本发明针对上述现有技术存在的增加絮凝剂会增加污泥处理量以及冷冻效率低、成本高的问题,提供了一种处理过程不会增加污泥处理量,冷冻效率高且能量利用率高的污水污泥处理装置。In view of this, the present invention aims at the problems in the above-mentioned prior art that increasing the flocculant will increase the sludge treatment capacity, low freezing efficiency and high cost, and provides a treatment process that does not increase the sludge handling capacity, has high freezing efficiency and Sewage sludge treatment device with high energy utilization rate.
本发明的技术解决方案是,提供一种以下结构的污水污泥处理装置,包括压滤装置、破碎装置和干燥装置,压滤装置对污泥进行压滤处理后由破碎装置进行破碎处理,污泥破碎后进入干燥装置进行干燥处理;The technical solution of the present invention is to provide a sewage sludge treatment device with the following structure, including a filter press device, a crushing device and a drying device. After the mud is crushed, it enters the drying device for drying treatment;
所述的污水污泥处理装置还包括污泥冷冻容器和冷冻干燥能量循环系统,所述的冷冻干燥能量循环系统包括压缩机、第一蒸发器、冷凝器以及设置于污泥冷冻容器中的第二蒸发器,压缩机的出气端与冷凝器连接,冷凝器经节流元件与第一蒸发器连接,第一蒸发器经第二蒸发器与压缩机的进气端连接;所述的冷凝器通过气体管道与干燥装置底部相连通,第一蒸发器通过气体管道与干燥装置顶部相连通,同时所述的冷凝器通过气体管道与第一蒸发器相连通。The sewage sludge treatment device also includes a sludge freezing container and a freeze-drying energy circulation system, and the freeze-drying energy circulation system includes a compressor, a first evaporator, a condenser, and a first Two evaporators, the outlet end of the compressor is connected to the condenser, the condenser is connected to the first evaporator through a throttling element, and the first evaporator is connected to the inlet end of the compressor through the second evaporator; the condenser The gas pipeline communicates with the bottom of the drying device, the first evaporator communicates with the top of the drying device through the gas pipeline, and the condenser communicates with the first evaporator through the gas pipeline.
采用以上结构,本发明与现有技术相比,具有以下优点:采用本发明,利用了冷冻干燥能量循环系统,同时实现了对污泥冷冻容器内污泥的冷冻和对干燥装置内的污泥的干燥,工质在压缩机作用下,输出高温高压气态工质,经过冷凝器,工质中的热量被空气吸收,将热量传递给空气,空气温度升高,工质温度降低,热空气通入干燥装置内对物料进行干燥,工质被冷凝变为高压液态,高压液态工质经过节流元件降压后变为低压液态工质,低压液态工质进入到第一蒸发器,吸收第一蒸发器内的空气热量(从物料顶部出来的空气),对空气降温,饱和空气降温后,其所能容纳的水分降低,多余的水分凝结成液态水通过第一蒸发器的积水盘排走,工质吸热后由低压液态变为低压气态(如果工质吸收空气的热量不够多的话,只能保证部分液态的工质蒸发成气态工质,而剩余部分的液态工质以及气态工质形成两相工质)进入到第二蒸发器,工质吸收第二蒸发器中污泥的热量,将污泥降温至所需要的冷冻温度-10℃~-15℃(此温度范围较佳,但不限于这一数值范围),此时液体工质则被气化成气态工质,气态工质进入到压缩机内。污泥冷冻容器内污泥经过多次冷冻解冻(解冻可自然解冻),破坏了污泥的结构,经解冻的污泥进入压滤装置,压滤装置将污泥压成大块饼状污泥,再送入破碎装置进行破碎形成污泥颗粒,污泥颗粒在干燥装置中进行干燥,实现了污泥的阶段性处理。由于污泥中不用加入化学制剂,故处理过程不会增加污泥处理量;工质能量的循环利用大大提高了污泥的冷冻效率,只需通过花费少量的压缩机能量,工质可将冷冻容器内数倍于压缩机能耗的热量“搬运”到干燥箱内,同时实现污泥的冷冻及污泥干燥,即解决了冷冻需要的冷量来源,又解决了干燥需要的热量来源,使得冷量及热量达到一个非常好的平衡,大大提高了热量使用效率,节能效果明显。With the above structure, compared with the prior art, the present invention has the following advantages: by adopting the present invention, the freeze-drying energy circulation system is utilized, and at the same time, the freezing of the sludge in the sludge freezing container and the drying of the sludge in the drying device are realized. Under the action of the compressor, the working medium outputs high-temperature and high-pressure gaseous working medium. After passing through the condenser, the heat in the working medium is absorbed by the air, and the heat is transferred to the air. The temperature of the air rises, the temperature of the working medium decreases, and the hot air passes through into the drying device to dry the material, the working medium is condensed into a high-pressure liquid, and the high-pressure liquid working medium becomes a low-pressure liquid working medium after being depressurized by the throttling element, and the low-pressure liquid working medium enters the first evaporator and absorbs the first The heat of the air in the evaporator (the air coming out from the top of the material) cools the air. After the saturated air cools down, the moisture it can hold decreases, and the excess moisture condenses into liquid water and is drained away through the water accumulation tray of the first evaporator. , the working fluid changes from a low-pressure liquid to a low-pressure gas after absorbing heat (if the working fluid does not absorb enough heat from the air, only part of the liquid working fluid can be evaporated into a gaseous working medium, and the remaining part of the liquid working medium and gaseous working medium Two-phase working fluid) enters the second evaporator, the working fluid absorbs the heat of the sludge in the second evaporator, and cools the sludge to the required freezing temperature -10°C ~ -15°C (this temperature range is better, But not limited to this numerical range), at this time, the liquid working medium is vaporized into a gaseous working medium, and the gaseous working medium enters the compressor. The sludge in the sludge freezing container has been frozen and thawed many times (thawing can be thawed naturally), which destroys the structure of the sludge, and the thawed sludge enters the filter press device, which presses the sludge into large cake-like sludge , and then sent to the crushing device for crushing to form sludge particles, and the sludge particles are dried in the drying device to realize the staged treatment of sludge. Since there is no need to add chemicals to the sludge, the treatment process will not increase the amount of sludge treated; the recycling of working medium energy greatly improves the freezing efficiency of sludge, and the working medium can freeze the sludge only by spending a small amount of compressor energy. The heat in the container that is several times the energy consumption of the compressor is "transferred" to the drying box, and the sludge is frozen and dried at the same time, which not only solves the source of cooling required for freezing, but also solves the source of heat required for drying, making cooling The energy and heat have reached a very good balance, greatly improving the efficiency of heat use, and the energy saving effect is obvious.
作为优选,所述的污泥冷冻容器为多个,第二蒸发器与污泥冷冻容器一一对应,多个污泥冷冻容器中的第二蒸发器的两端分别通过工质换向阀与第一蒸发器和压缩机连接,污泥冷冻容器的底部设有过滤结构,多个污泥冷冻容器的底部通过液体换向阀并经液体管道与压滤装置连通。这样,在一个污泥冷冻容器中的污泥进行冷冻之时,其它污泥冷冻容器的污泥进行自然解冻,已经解冻好的则直接输送至压滤装置中,从而提高处理效率,能够进行连续工作。Preferably, there are multiple sludge freezing containers, and the second evaporator corresponds to the sludge freezing container one by one, and the two ends of the second evaporator in the multiple sludge freezing containers are connected to The first evaporator is connected to the compressor, the bottom of the sludge freezing container is provided with a filter structure, and the bottoms of multiple sludge freezing containers are connected to the filter press device through a liquid reversing valve and a liquid pipeline. In this way, when the sludge in one sludge freezing container is frozen, the sludge in other sludge freezing containers will be thawed naturally, and the thawed ones will be directly transported to the filter press device, thereby improving the treatment efficiency and enabling continuous Work.
作为优选,所述的干燥装置包括干燥箱和污泥翻板机构,所述的污泥翻板机构,水平排布在干燥箱内的不同竖直高度上,所述的污泥翻板机构交错排布,最底部层的一个污泥翻板机构伸出干燥箱外。这样,污泥经破碎后进入干燥装置,首先落入污泥翻板机构最上层,随着污泥翻板机构的传动,污泥落在下一层的污泥翻板机构上,下一层的污泥翻板机构再换向传动至另外一端,如此往复,可实现热空气与污泥上下左右接触,全方位的干燥,提高干燥效果,当落至最底部层的一个污泥翻板机构时,由于其伸出干燥箱外,污泥被其传送至干燥箱外,进入下一步工序处理。Preferably, the drying device includes a drying box and a sludge turning mechanism, the sludge turning mechanisms are arranged horizontally at different vertical heights in the drying box, and the sludge turning mechanisms are staggered Arranged, a sludge turnover mechanism at the bottom layer protrudes out of the drying box. In this way, the sludge enters the drying device after being crushed, and first falls into the uppermost layer of the sludge turning mechanism. With the transmission of the sludge turning mechanism, the sludge falls on the sludge turning mechanism of the next layer, and The sludge turnover mechanism is then reversed and driven to the other end. This reciprocation can realize the contact between the hot air and the sludge up and down, all-round drying, and improve the drying effect. When it falls to the sludge turnover mechanism at the bottom layer, As it protrudes out of the drying box, the sludge is conveyed to the outside of the drying box and enters the next step of processing.
作为优选,所述的压滤装置为板框压滤机,板框压滤机包括多个板框,在板框下方设有拉板机构,所述的拉板机构包括多块牵引块和滑板,相邻两块牵引块之间设有铰接连杆,并在每块牵引块下均设有滚轮,所述的多块牵引块置于滑板上,并通过滚轮与滑板可滚动连接。这样,通过多块拉板机构进行抽拉,可以实现多个板框的抽拉,解决了当前只能同时抽拉一块板框的问题,缩短拉板时间,提高了压滤装置的压滤效率。Preferably, the filter press device is a plate and frame filter press, the plate and frame filter press includes a plurality of plate frames, and a plate pulling mechanism is provided under the plate frames, and the plate pulling mechanism includes a plurality of traction blocks and sliding plates A hinged link is provided between two adjacent traction blocks, and rollers are provided under each traction block. The multiple traction blocks are placed on the slide plate and are rotatably connected to the slide plate through the rollers. In this way, the pulling of multiple plates and frames can be achieved through the pulling of multiple plate pulling mechanisms, which solves the current problem that only one plate and frame can be pulled at the same time, shortens the time of plate pulling, and improves the filtration efficiency of the filter press device .
附图说明Description of drawings
图1为本发明的污水污泥处理装置示意图;Fig. 1 is the schematic diagram of sewage sludge treatment device of the present invention;
图2为拉板机构的结构示意图;Fig. 2 is the structural representation of drawing plate mechanism;
如图所示,1、压滤装置,1.1、板框,1.2、牵引块,1.3、滑板,1.4、铰接连杆,1.5、滚轮,2、破碎装置,3、干燥装置,3.1、干燥箱,3.2、污泥翻板机构,4、污泥冷冻容器,5、压缩机,6、第一蒸发器,7、冷凝器,8、第二蒸发器,9、节流元件,10、气体管道,11、工质换向阀,12、过滤结构,13、液体换向阀,14、液体管道,15、转子泵。As shown in the figure, 1. Filter press device, 1.1, plate frame, 1.2, traction block, 1.3, slide plate, 1.4, hinged connecting rod, 1.5, roller, 2, crushing device, 3, drying device, 3.1, drying box, 3.2. Sludge turning mechanism, 4. Sludge freezing container, 5. Compressor, 6. First evaporator, 7. Condenser, 8. Second evaporator, 9. Throttle element, 10. Gas pipeline, 11. Working medium reversing valve, 12. Filtration structure, 13. Liquid reversing valve, 14. Liquid pipeline, 15. Rotor pump.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明作进一步说明。The present invention will be further described below in conjunction with the accompanying drawings and specific embodiments.
如图所示,本发明的一种污水污泥处理装置,包括压滤装置1、破碎装置2和干燥装置3,压滤装置1对污泥进行压滤处理后由破碎装置2进行破碎处理,污泥破碎后进入干燥装置3进行干燥处理;As shown in the figure, a sewage sludge treatment device of the present invention includes a filter press device 1, a crushing device 2 and a drying device 3. The filter press device 1 carries out pressure filtration treatment on the sludge and is crushed by the crushing device 2. After the sludge is crushed, it enters the drying device 3 for drying treatment;
所述的污水污泥处理装置还包括污泥冷冻容器4和冷冻干燥能量循环系统,所述的冷冻干燥能量循环系统包括压缩机5、第一蒸发器6、冷凝器7以及设置于污泥冷冻容器4中的第二蒸发器8,压缩机5的出气端与冷凝器6连接,冷凝器7经节流元件9与第一蒸发器6连接,第一蒸发器6经第二蒸发器8与压缩机5的进气端连接;所述的冷凝器7通过气体管道10与干燥装置3底部相连通,第一蒸发器6与通过气体管道10与干燥装置3顶部相连通,同时所述的冷凝器7与第一蒸发器6通过气体管道10相连通。The sewage sludge treatment device also includes a sludge freezing container 4 and a freeze-drying energy circulation system, and the freeze-drying energy circulation system includes a compressor 5, a first evaporator 6, a condenser 7 and a sludge freezer. The second evaporator 8 in the container 4, the gas outlet end of the compressor 5 is connected with the condenser 6, the condenser 7 is connected with the first evaporator 6 through the throttling element 9, and the first evaporator 6 is connected with the second evaporator 8 The inlet end of the compressor 5 is connected; the condenser 7 communicates with the bottom of the drying device 3 through the gas pipeline 10, and the first evaporator 6 communicates with the top of the drying device 3 through the gas pipeline 10, while the condensing The device 7 communicates with the first evaporator 6 through a gas pipeline 10 .
以上技术构成了解决本发明技术问题的基本方案。The above technologies constitute the basic solution to solve the technical problems of the present invention.
所述的污泥冷冻容器4为多个,第二蒸发器8与污泥冷冻容器4一一对应,多个污泥冷冻容器4中的第二蒸发器8的两端分别通过工质换向阀11与第一蒸发器6和压缩机5连接,污泥冷冻容器4的底部设有过滤结构12,多个污泥冷冻容器4的底部通过液体换向阀13并经液体管道14与压滤装置1连通;解冻后的污泥从污泥冷冻容器4通过转子泵15泵入压滤装置1中。There are multiple sludge freezing containers 4, and the second evaporator 8 corresponds to the sludge freezing container 4 one by one. The valve 11 is connected with the first evaporator 6 and the compressor 5, the bottom of the sludge freezing container 4 is provided with a filter structure 12, and the bottoms of a plurality of sludge freezing containers 4 pass through the liquid reversing valve 13 and through the liquid pipeline 14 and press filter The device 1 is connected; the thawed sludge is pumped into the filter press device 1 from the sludge freezing container 4 through the rotor pump 15 .
所述的干燥装置3包括干燥箱3.1和污泥翻板机构3.2,所述的污泥翻板机构,水平排布在干燥箱3.1内的不同竖直高度上,所述的污泥翻板机3.2构交错排布,最底部层的一个污泥翻板机构3.2伸出干燥箱3.1外。The drying device 3 includes a drying box 3.1 and a sludge turning mechanism 3.2. The sludge turning mechanism is arranged horizontally at different vertical heights in the drying box 3.1. The sludge turning mechanism The 3.2 structures are arranged in a staggered manner, and a sludge turnover mechanism 3.2 at the bottom layer extends out of the drying box 3.1.
所述的压滤装置1为板框压滤机,板框压滤机包括多个板框1.1,在板框1.1下方设有拉板机构,所述的拉板机构包括多块牵引块1.2和滑板1.3,相邻两块牵引块1.2之间设有铰接连杆1.4,并在每块牵引块1.2下均设有滚轮1.5,所述的多块牵引块1.2置于滑板1.3上,并通过滚轮1.5与滑板1.3可滑动连接。The filter press device 1 is a plate and frame filter press, and the plate and frame filter press includes a plurality of plate frames 1.1, and a plate pulling mechanism is provided below the plate frames 1.1, and the plate pulling mechanism includes a plurality of traction blocks 1.2 and Skateboard 1.3, hinged connecting rod 1.4 is provided between two adjacent traction blocks 1.2, and roller 1.5 is provided under each traction block 1.2, and the multiple traction blocks 1.2 are placed on the slide plate 1.3, and pass through the rollers 1.5 is slidably connected with slide plate 1.3.
污泥深度处理方法流程为:The process flow of sludge advanced treatment method is as follows:
1)在冷冻温度-10℃~-15℃、冷冻时间72小时下进行反复冷冻;1) Repeated freezing at a freezing temperature of -10°C to -15°C and a freezing time of 72 hours;
2)在20-50℃之间进行解冻(可采用常温解冻),解冻时间约为6小时;2) Thaw at 20-50°C (normal temperature can be used for thawing), and the thawing time is about 6 hours;
3)在板框压滤机内进行机械脱水,首先是压滤阶段,压滤压力为1.0-1.2Mpa,压滤时间为1.5-2小时,此时污泥含水率65%-70%,再进入到压榨脱水阶段,压榨压力为1.5Mpa,压榨时间为1小时,此时污泥含水率约60%-65%;3) Carry out mechanical dehydration in the plate-and-frame filter press. First, it is the filter press stage. The filter press pressure is 1.0-1.2Mpa, and the filter press time is 1.5-2 hours. Entering the stage of pressing and dehydration, the pressing pressure is 1.5Mpa, and the pressing time is 1 hour. At this time, the moisture content of the sludge is about 60%-65%;
4)将板框压滤机出来的大块泥饼状污泥在污泥混合破碎装置中进行破碎,形成小的污泥颗粒,污泥颗粒尺寸一般在20mm左右;4) The large cake-like sludge from the plate and frame filter press is crushed in the sludge mixing and crushing device to form small sludge particles, and the size of the sludge particles is generally about 20mm;
5)将破碎后的污泥输送进入到干燥装置内进行干燥,干燥装置为多层翻板式,干燥时间为2小时,干燥温度50-60℃,经过干燥后污泥的含水率为10%-30%,此时第二蒸发器提供冷量给污泥冷冻容器;5) Transport the crushed sludge into the drying device for drying. The drying device is a multi-layer flap type, the drying time is 2 hours, the drying temperature is 50-60°C, and the moisture content of the sludge after drying is 10%- 30%, at this time the second evaporator provides cooling capacity to the sludge freezing container;
上述步骤仅为污泥处理的阶段性步骤,污泥经干燥后还可进行焚烧处理,并进行余热回收,并将余热用于污泥冷冻容器中冷冻污泥的解冻。The above steps are only staged steps of sludge treatment. The sludge can also be incinerated after being dried, and the waste heat can be recovered, and the waste heat can be used for thawing the frozen sludge in the sludge freezing container.
具体工作原理如下:The specific working principle is as follows:
污泥进入到污泥冷冻容器,首先在第二蒸发器作用下,制冷工质进入到第二蒸发器的内,工质对污泥吸热,使得污泥的冷冻温度达到规定温度,污泥在-10℃~-15℃、冷冻时间72小时下经过反复冷冻,破坏污泥与水的结合力和破坏胶体的结构,使胶体脱稳凝聚且细胞膜破裂,污泥颗粒迅速沉降,脱水性能大幅提高,脱水速度比冷冻前高几十倍,冷冻结束。此时,工质换向阀对工质流向进行换向,将工质流向变换到另一个污泥冷冻容器内,此时已经冷冻的污泥冷冻容器内通入具有一定温度的空气进行解冻,空气温度在20-50℃之间,解冻时间为6小时。The sludge enters the sludge freezing container. First, under the action of the second evaporator, the refrigerant enters the second evaporator, and the working fluid absorbs heat on the sludge, so that the freezing temperature of the sludge reaches the specified temperature, and the sludge Repeated freezing at -10°C to -15°C and a freezing time of 72 hours destroys the binding force between sludge and water and the structure of the colloid, causing the colloid to destabilize and coagulate and the cell membrane to rupture. The sludge particles settle rapidly and the dehydration performance is greatly improved. Increase, the dehydration speed is dozens of times higher than before freezing, and the freezing is over. At this time, the working fluid reversing valve reverses the flow direction of the working fluid, and changes the flow direction of the working fluid to another sludge freezing container. At this time, air with a certain temperature is passed into the frozen sludge freezing container for thawing. The air temperature is between 20-50°C, and the thawing time is 6 hours.
污泥解冻后通过液体管道,进入转子泵,在转子泵的加压下进入板框机(板框压滤机)开始压滤进行机械脱水,经过一段时间的压滤后,拉开板框,泥饼状的污泥掉落到物料输送装置内,经过物料输送装置输送到破碎机,破碎机对泥饼进行破碎,形成小的污泥颗粒,污泥颗粒尺寸保持在20mm左右,成小颗粒的污泥提高污泥的比表面积,利于在干燥中增大污泥和高温空气的接触面积,提高干燥速率和效果。After thawing, the sludge enters the rotor pump through the liquid pipeline. Under the pressure of the rotor pump, it enters the plate and frame machine (plate and frame filter press) to start pressure filtration for mechanical dehydration. After a period of pressure filtration, the plate and frame are pulled apart, The mud cake-like sludge falls into the material conveying device, and is transported to the crusher through the material conveying device. The crusher crushes the mud cake to form small sludge particles. The sludge increases the specific surface area of the sludge, which is beneficial to increase the contact area between the sludge and high-temperature air during drying, and improves the drying rate and effect.
小污泥颗粒进入到干燥机内的上层翻板中,自上往下一层层掉落,在掉落的过程中污泥会不断的翻转,使得各个表面都和空气充分接触。干燥空气自下而上和污泥接触,空气吸收了污泥的水分变为湿度很高的湿空气经过第一蒸发器后降到露点以下,析出水分,析出的水分经过积水盘排出,空气继续经过冷凝器后被加热,进入到干燥箱内对污泥进行干燥。污泥被加热干燥后经过最下一层翻板后离开干燥箱。Small sludge particles enter the upper flap in the dryer and fall from top to bottom layer by layer. During the falling process, the sludge will be turned over continuously, so that all surfaces are in full contact with the air. The dry air contacts the sludge from bottom to top. The air absorbs the moisture of the sludge and becomes moist air with high humidity. After passing through the first evaporator, it drops below the dew point and precipitates moisture. The precipitated moisture is discharged through the water storage pan, and the air After continuing to pass through the condenser, it is heated and enters the drying box to dry the sludge. After the sludge is heated and dried, it leaves the drying box after going through the bottom layer of flaps.
为了更好地处理污泥,在以上阶段性处理之后,污泥离开干燥箱后通过物料输送装置输送到焚烧炉,调节进入燃烧室的一次风,在匀料机作用下使其处于流化燃烧状态,由于流化床中的介质处于悬浮状态,气固能充分混合接触,整个炉内燃烧段的温度相对较为均匀,燃烧后产生的废气约850℃排出进入到余热锅炉。与此同时,余热锅炉内的导热油由220℃被加热至250℃,被加热后的导热油通过第二换热器对空气进行加热,加热后的空气进入到干燥系统和解冻装置对污泥干燥和解冻供热。气体净化装置有酸性气体的脱除和颗粒物捕集两大部分组成,气体净化可采用半干法,在烟气中喷入一定的氧化钙,使之与烟气中的酸性物质反应,并通过喷雾装置控制水分达到喷雾干燥的反应过程。脱酸反应物基本上为干固态,不会出现废水排放。烟气中颗粒物捕集可以通过过滤网结合旋风分离器或者布袋实现,之前喷入一定量的活性炭粒粉,吸附烟气中重金属和二恶英等有害物质。经过净化后的气体可以排出大气,对环境污染少。In order to better treat the sludge, after the above staged treatment, the sludge leaves the drying box and is transported to the incinerator through the material conveying device, and the primary air entering the combustion chamber is adjusted to make it in fluidized combustion under the action of the leveler. State, because the medium in the fluidized bed is in a suspended state, the gas and solid can be fully mixed and contacted, the temperature of the combustion section in the entire furnace is relatively uniform, and the exhaust gas generated after combustion is discharged into the waste heat boiler at about 850 °C. At the same time, the heat transfer oil in the waste heat boiler is heated from 220°C to 250°C. The heated heat transfer oil heats the air through the second heat exchanger, and the heated air enters the drying system and the thawing device to treat the sludge. Dry and thaw with heat. The gas purification device consists of two parts: acid gas removal and particle capture. Gas purification can be done by semi-dry method, spraying a certain amount of calcium oxide into the flue gas to make it react with the acidic substances in the flue gas, and pass through The spray device controls the moisture to reach the reaction process of spray drying. The deacidification reactant is basically a dry solid, and there will be no waste water discharge. The capture of particulate matter in the flue gas can be achieved through a filter combined with a cyclone separator or a cloth bag. A certain amount of activated carbon powder is sprayed before to absorb harmful substances such as heavy metals and dioxins in the flue gas. The purified gas can be discharged into the atmosphere with less pollution to the environment.
以上仅就本发明较佳的实施例作了说明,但不能理解为是对权利要求的限制。本发明不仅局限于以上实施例,其具体结构允许有变化。总之,凡在本发明独立权利要求的保护范围内所作的各种变化均在本发明的保护范围内。The above is only an illustration of the preferred embodiments of the present invention, but should not be construed as a limitation on the claims. The present invention is not limited to the above embodiments, and its specific structure is allowed to vary. In a word, all kinds of changes made within the protection scope of the independent claims of the present invention are within the protection scope of the present invention.
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