CN111233290A - Sludge treatment system for sewage treatment plant - Google Patents
Sludge treatment system for sewage treatment plant Download PDFInfo
- Publication number
- CN111233290A CN111233290A CN202010076200.0A CN202010076200A CN111233290A CN 111233290 A CN111233290 A CN 111233290A CN 202010076200 A CN202010076200 A CN 202010076200A CN 111233290 A CN111233290 A CN 111233290A
- Authority
- CN
- China
- Prior art keywords
- sludge
- pipeline
- pool
- steam
- fermentation tank
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 84
- 239000010865 sewage Substances 0.000 title claims abstract description 16
- 238000000855 fermentation Methods 0.000 claims abstract description 30
- 239000007789 gas Substances 0.000 claims abstract description 28
- 239000011229 interlayer Substances 0.000 claims abstract description 8
- 239000007788 liquid Substances 0.000 claims abstract description 5
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 18
- 230000008719 thickening Effects 0.000 claims description 13
- 239000002918 waste heat Substances 0.000 claims description 10
- 239000000779 smoke Substances 0.000 claims description 8
- 238000001035 drying Methods 0.000 claims description 7
- 239000002002 slurry Substances 0.000 claims description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 5
- 239000010410 layer Substances 0.000 claims description 4
- 238000009413 insulation Methods 0.000 claims 1
- 230000004151 fermentation Effects 0.000 abstract description 7
- 239000002028 Biomass Substances 0.000 abstract description 6
- 230000009467 reduction Effects 0.000 abstract description 5
- 239000003337 fertilizer Substances 0.000 abstract description 4
- 238000000034 method Methods 0.000 abstract description 4
- 230000006641 stabilisation Effects 0.000 abstract description 4
- 238000011105 stabilization Methods 0.000 abstract description 4
- 238000010248 power generation Methods 0.000 abstract description 3
- 230000008569 process Effects 0.000 abstract description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 2
- 239000001301 oxygen Substances 0.000 abstract description 2
- 229910052760 oxygen Inorganic materials 0.000 abstract description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 8
- 230000029087 digestion Effects 0.000 description 4
- 230000007613 environmental effect Effects 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 230000005611 electricity Effects 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- XLYOFNOQVPJJNP-ZSJDYOACSA-N Heavy water Chemical compound [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000000397 acetylating effect Effects 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 244000052616 bacterial pathogen Species 0.000 description 1
- 239000000149 chemical water pollutant Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 239000004020 conductor Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 235000013601 eggs Nutrition 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 244000045947 parasite Species 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
- C02F11/04—Anaerobic treatment; Production of methane by such processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/122—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/13—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/001—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/10—Energy recovery
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Mechanical Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Organic Chemistry (AREA)
- General Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Treatment Of Sludge (AREA)
Abstract
本发明公开了一种用于污水处理厂的污泥处理系统,它包括有污泥浓缩池,污泥浓缩池分为A池和B池,A池通过管路污泥焚烧炉;B池通过管路依次连接厌氧发酵罐,污泥焚烧炉的一部分蒸汽通过管道输送至热交换器,热交换器的低温液体经管道与厌氧发酵罐的夹层和太阳能集热装置的管道循环相通;厌氧发酵罐的出气口通过管道接入热电联产装置,污泥焚烧炉的另一部分蒸汽通过管道输送至热电联产装置,热电联产装置电连接电力输出装置。本发明能处理大量剩余污泥,污泥中的生物质能能用于发电,污泥处理后的残渣作为肥料,实现污泥“减量化”“稳定化”和“资源化”的目的。
The invention discloses a sludge treatment system for a sewage treatment plant, which comprises a sludge concentration tank. The sludge concentration tank is divided into A pool and B pool. A pool passes through a pipeline sludge incinerator; B pool passes through a sludge incinerator. The pipeline is connected to the anaerobic fermentation tank in turn, part of the steam of the sludge incinerator is transported to the heat exchanger through the pipeline, and the low temperature liquid of the heat exchanger is circulated through the pipeline with the interlayer of the anaerobic fermentation tank and the pipeline of the solar heat collector; The gas outlet of the oxygen fermentation tank is connected to the cogeneration device through a pipeline, and another part of the steam from the sludge incinerator is transported to the cogeneration device through a pipeline, and the cogeneration device is electrically connected to the power output device. The invention can process a large amount of excess sludge, the biomass energy in the sludge can be used for power generation, and the residue after sludge treatment can be used as fertilizer to achieve the purposes of sludge "reduction", "stabilization" and "resource utilization".
Description
技术领域technical field
本发明属于环保技术领域,具体涉及一种用于污水处理厂的污泥处理系统。The invention belongs to the technical field of environmental protection, and in particular relates to a sludge treatment system for a sewage treatment plant.
背景技术Background technique
近年来, 我国城市污水处理厂的数目和处理能力迅速增长,但普遍存在运行费用偏高问题,其中主要是电耗大,一般约占整个运行费用的 50 %左右 。In recent years, the number and treatment capacity of urban sewage treatment plants in my country have increased rapidly, but there is a common problem of high operating costs, mainly due to high power consumption, which generally accounts for about 50% of the entire operating costs.
由于我国长期存在“重水轻泥”的现象,对污泥处理的重视程度不够,有大量的污泥未经过稳定化处理处置,造成环境污染,危害了人类的健康。如何合理地处置污泥,经济有效地实现污泥减量化、无害化和资源化是世界各国政府、企业和环保工作者面临的一项重要课题。污水处理厂的建设投运伴随产生大量的剩余污泥,以含水率80%计,全国年污泥总产生量很快将突破3000万吨。按照预测,到2020年污泥产量将突破年6000万吨。Due to the phenomenon of "heavy water and light mud" in my country for a long time, insufficient attention has been paid to sludge treatment. A large amount of sludge has not been stabilized and disposed of, causing environmental pollution and endangering human health. How to dispose of sludge reasonably and realize the reduction, harmlessness and resource utilization of sludge economically and effectively is an important issue faced by governments, enterprises and environmental protection workers all over the world. The construction and operation of the sewage treatment plant is accompanied by the production of a large amount of excess sludge. Based on the moisture content of 80%, the total annual sludge production in the country will soon exceed 30 million tons. According to the forecast, the sludge production will exceed 60 million tons per year by 2020.
随着政府和公民对环保的重视,人们开始注意到生物质能的潜力,污水处理厂每天产生大量污泥,污泥中含有有机质,在厌氧微生物的作用下,大分子有机物分解成稳定物质,比照消化前污泥能大量减容,同时能够得到以甲烷为主的沼气。厌氧消化后的残渣中仍有养分,也可作为肥料或土壤改良剂,能做到最大资源化,达到“减量化”“稳定化”和“资源化”的目标。但如何利用污水处理厂的可再生资源来实现高效发电是本领域技术的难题。As the government and citizens attach importance to environmental protection, people begin to notice the potential of biomass energy. Sewage treatment plants produce a large amount of sludge every day. The sludge contains organic matter. Under the action of anaerobic microorganisms, macromolecular organic matter is decomposed into stable substances. , compared with the sludge before digestion, the volume can be greatly reduced, and at the same time, methane-based biogas can be obtained. There are still nutrients in the residue after anaerobic digestion, and it can also be used as fertilizer or soil conditioner, which can maximize resource utilization and achieve the goals of "reduction", "stabilization" and "resource utilization". However, how to utilize the renewable resources of the sewage treatment plant to achieve high-efficiency power generation is a technical problem in the art.
发明内容SUMMARY OF THE INVENTION
针对现有技术存在的问题,本发明所要解决的技术问题就是提供一种用于污水处理厂的污泥处理系统,它能处理大量剩余污泥,污泥中的生物质能能用于发电,污泥处理后的残渣作为肥料,实现污泥“减量化”“稳定化”和“资源化”的目的。In view of the problems existing in the prior art, the technical problem to be solved by the present invention is to provide a sludge treatment system for a sewage treatment plant, which can process a large amount of excess sludge, and the biomass energy in the sludge can be used for power generation, The residue after sludge treatment is used as fertilizer to achieve the purpose of "reduction", "stabilization" and "resource utilization" of sludge.
本发明所要解决的技术问题是通过这样的技术方案实现的,它包括有污泥浓缩池、太阳能集热装置、热交换器、厌氧发酵罐和热电联产装置,污泥浓缩池分为A池和B池,A池通过管路依次连接板框压滤机、污泥干燥间和污泥焚烧炉;B池通过管路依次连接厌氧发酵罐、沼液沼渣收集器和分离器;污泥焚烧炉的一部分蒸汽通过管道输送至热交换器,热交换器的低温液体经管道与厌氧发酵罐的夹层和太阳能集热装置的管道循环相通;厌氧发酵罐的出气口通过管道依次连通储气室、沼气脱硫器、沼气提纯器和甲烷压缩器接入热电联产装置的燃气轮机,污泥焚烧炉的另一部分蒸汽通过管道输送至热电联产装置的蒸汽轮机发电器,热电联产装置电连接电力输出装置。The technical problem to be solved by the present invention is achieved through such a technical solution, which includes a sludge thickening tank, a solar heat collector, a heat exchanger, an anaerobic fermentation tank and a cogeneration device. The sludge thickening tank is divided into A Pool and Pool B, Pool A is connected to the plate and frame filter press, sludge drying room and sludge incinerator in sequence through pipelines; Pool B is connected to the anaerobic fermentation tank, biogas slurry and biogas residue collector and separator in sequence through pipelines; Part of the steam of the sludge incinerator is transported to the heat exchanger through the pipeline, and the low-temperature liquid of the heat exchanger is circulated through the pipeline with the interlayer of the anaerobic fermentation tank and the pipeline of the solar heat collector; the gas outlet of the anaerobic fermentation tank is successively connected through the pipeline. The gas storage chamber, biogas desulfurizer, biogas purifier and methane compressor are connected to the gas turbine of the cogeneration unit. Another part of the steam from the sludge incinerator is transported to the steam turbine generator of the cogeneration unit through pipelines. The device is electrically connected to the power output device.
与现有技术相比,本发明的技术效果是:Compared with the prior art, the technical effect of the present invention is:
能处理污水处理厂的大量剩余污泥,利用生物质能所产生的能源再供给板框压滤机,实现以废治废的目的;本发明实现污水处理厂污泥和臭气的同时处理,处理效率高,节能环保,大幅降低剩余污泥的处理及排放压力;污泥厌氧消化所产生沼气不仅满足自身发酵所需能量,还能供给热电联产装置;另外污泥厌氧消化所产生的沼液沼渣,经过发酵已杀死病原菌和寄生虫卵,可以作为有机农肥;污泥干化焚烧所产生的能量可以供给热交换器和热电联产装置,实现了剩余污泥 “减量化”“稳定化”和“资源化”的目的。It can treat a large amount of excess sludge in the sewage treatment plant, and use the energy generated by biomass energy to supply the plate and frame filter press to achieve the purpose of treating waste with waste; the invention realizes the simultaneous treatment of sludge and odor in the sewage treatment plant, High treatment efficiency, energy saving and environmental protection, greatly reducing the treatment and discharge pressure of excess sludge; the biogas produced by the anaerobic digestion of sludge not only meets the energy required for self-fermentation, but can also be supplied to the cogeneration unit; in addition, the anaerobic digestion of sludge produces The biogas slurry and biogas residues have been fermented to kill pathogenic bacteria and parasite eggs, and can be used as organic fertilizer; the energy generated by sludge drying and incineration can be supplied to heat exchangers and cogeneration devices, realizing the “reduction of excess sludge”. The purpose of "stabilization", "resourceization" and "resourceization".
附图说明Description of drawings
本发明的附图说明如下:The accompanying drawings of the present invention are described as follows:
图1为本发明一种实施方式的技术路线图;FIG. 1 is a technical roadmap of an embodiment of the present invention;
图2为本发明一个实施例结构示意图;2 is a schematic structural diagram of an embodiment of the present invention;
图3为图2中的热电联产装置的结构示意图。FIG. 3 is a schematic structural diagram of the cogeneration device in FIG. 2 .
图中,1、污泥浓缩池;2、板框压滤机;3、污泥干燥间;4、污泥焚烧炉;5、太阳能集热装置;6、热交换器;7、厌氧发酵罐;8、储气室;9、沼气脱硫器;10、沼气提纯器;11、甲烷压缩器;12、燃气轮机;13、电机;14、排烟器;15、余热锅炉;16、蒸汽轮机发电器;17、电力输出装置;18、沼液沼渣收集器;19、分离器;20、热电联产装置。In the figure, 1, sludge thickening tank; 2, plate and frame filter press; 3, sludge drying room; 4, sludge incinerator; 5, solar heat collector; 6, heat exchanger; 7, anaerobic fermentation Tank; 8. Gas storage chamber; 9. Biogas desulfurizer; 10. Biogas purifier; 11. Methane compressor; 12. Gas turbine; 13. Motor; 14. Smoke exhauster; 15. Waste heat boiler; 16. Steam turbine generator Electrical appliances; 17. Power output device; 18. Biogas slurry and residue collector; 19. Separator; 20. Cogeneration device.
具体实施方式Detailed ways
下面结合附图和实施例对本发明作进一步说明:Below in conjunction with accompanying drawing and embodiment, the present invention will be further described:
如图1所示,本发明的技术路线是,整个系统分为污泥资源化模块和生物质发电供电模块两部分:污泥资源化模块包括污泥浓缩池,污泥浓缩池通过一条管路依次相连板框压滤机、污泥干燥间和污泥焚烧炉,并通过另一条管路依次相连的厌氧发酵罐、沼液沼渣收集器和分离器,热交换器和太阳能集热装置均与厌氧发酵罐相连,为发酵罐提供发酵所需热量。生物质发电供电模块包括储气室、沼气脱硫器、沼气提纯器、甲烷压缩器、热交换器、热电联产装置和蓄电池。As shown in Figure 1, the technical route of the present invention is that the entire system is divided into two parts: a sludge resource utilization module and a biomass power supply module: the sludge resource utilization module includes a sludge thickening tank, and the sludge thickening tank passes through a pipeline The plate and frame filter press, the sludge drying room and the sludge incinerator are connected in sequence, and the anaerobic fermentation tank, the biogas slurry and residue collector and separator, the heat exchanger and the solar heat collector are connected in sequence through another pipeline. Both are connected to the anaerobic fermenter to provide the fermenter with the heat required for fermentation. The biomass power supply module includes a gas storage chamber, a biogas desulfurizer, a biogas purifier, a methane compressor, a heat exchanger, a cogeneration device and a battery.
污泥浓缩池由挡墙划分为A池和B池,A池污泥占30%,B池污泥占70%。污泥浓缩池A池与板框压滤机通过管道相连,污泥厌氧发酵罐与污泥浓缩池B池通过管道相连;污泥浓缩池A池中的剩余污泥经板框压滤机压滤脱水后,进入污泥干燥间的转筒式干燥器,污泥在转筒炒板的搅拌下与热气流充分接触,将污泥的含水率控制在40%以下,再运至污泥焚烧炉,焚烧所产生热量的提供给热交换器和热电联产系统。污泥浓缩池B池与厌氧发酵罐相连,厌氧发酵罐产生的沼气进入储气室储存,沼气运送入沼气脱硫器中经高压水洗工艺脱硫, 再经沼气提纯器提纯及甲烷压缩器压缩,最后输送至热电联产装置发电。同时厌氧发酵罐中的沼液及沼渣经收集器收集,由分离器分离出液体肥料和沼渣。The sludge thickening tank is divided into A pool and B pool by the retaining wall, A pool sludge accounts for 30%, B pool sludge accounts for 70%. The sludge thickening tank A pool is connected with the plate and frame filter press through the pipeline, and the sludge anaerobic fermentation tank is connected with the sludge thickening tank B pool through the pipeline; the excess sludge in the sludge thickening tank A pool is passed through the plate and frame filter press. After filter press and dehydration, it enters the rotary drum dryer in the sludge drying room. The sludge is fully contacted with the hot air under the stirring of the rotary drum frying plate, and the moisture content of the sludge is controlled below 40%, and then transported to the sludge. Incinerators, the heat generated by incineration is supplied to heat exchangers and cogeneration systems. The sludge thickening tank B is connected to the anaerobic fermentation tank. The biogas generated by the anaerobic fermentation tank enters the gas storage room for storage, and the biogas is transported to the biogas desulfurizer to be desulfurized by the high-pressure water washing process, and then purified by the biogas purifier and compressed by the methane compressor. , and finally sent to the cogeneration unit to generate electricity. At the same time, the biogas slurry and biogas residue in the anaerobic fermentation tank are collected by the collector, and the liquid fertilizer and biogas residue are separated by the separator.
B池中有由污水处理厂剩余污泥和少量垃圾渗滤液按比例混合成C/N为10~20:1的混合污泥;该混合污泥中投加50~150mg/gVS的Fe3O4和30~50mg/gVS ZVI(零价铁),促进污泥中有机物水解的同时,降低后续发酵系统氧化还原电位,还能作为导电材料促进乙酸化微生物和产甲烷菌之间的种间电子传递过程;所述ZVI(零价铁)直径约为0.15mm,纯度大于80%;所述Fe3O4直径约为0.15mm,纯度以铁计算含量大于62%。In pool B, the residual sludge of the sewage treatment plant and a small amount of landfill leachate are mixed in proportion to form a mixed sludge with a C/N ratio of 10-20:1; Fe 3 O of 50-150 mg/g VS is added to the mixed sludge. 4 and 30~50mg/g VS ZVI (zero-valent iron), while promoting the hydrolysis of organic matter in the sludge, reducing the redox potential of the subsequent fermentation system, and also acting as a conductive material to promote the interspecific electrons between acetylating microorganisms and methanogens The transfer process; the diameter of the ZVI (zero-valent iron) is about 0.15mm, and the purity is greater than 80%; the diameter of the Fe 3 O 4 is about 0.15mm, and the purity is greater than 62% in terms of iron content.
厌氧发酵罐采用双层蛋型结构,蛋型结构受力条件好,同时搅拌充分无死角,污泥不易在池底固结,池子总表面积比圆柱形小,散热面积小易保温。双层蛋型的厌氧发酵罐夹层充有加热保温水。双层蛋型的厌氧发酵罐采用中温发酵时,有机负荷一般为1.6~6.4kgVSS/(m3•d)左右,水力停留时间较长,停留时间为10~15d。双层蛋型的厌氧发酵罐采用太阳能集热装置和热交换器为中温发酵提供所需热量。The anaerobic fermentation tank adopts a double-layer egg-shaped structure. The egg-shaped structure has good stress conditions, and at the same time, the stirring is sufficient and there is no dead angle. The sludge is not easy to consolidate at the bottom of the tank. The interlayer of the double-egg-shaped anaerobic fermenter is filled with heated and insulated water. When the double-egg type anaerobic fermenter adopts medium temperature fermentation, the organic load is generally about 1.6-6.4kgVSS/(m 3 •d), and the hydraulic retention time is longer, and the residence time is 10-15d. The double-egg-shaped anaerobic fermenter uses solar collectors and heat exchangers to provide the required heat for mesophilic fermentation.
太阳能集热装置由全玻璃镜面反射镜、太阳能集热板、温度传感器等组成。由太阳能集热装置吸收热量,输送到双层蛋型的发酵罐夹层内调节温度,保证在外部气温较低的条件下正常产气。聚光器反射采用全玻璃镜面反射镜反射,具有较高的光学效率。太阳能集热装置采用强制循环,光热效率高,系统效率可达60%~80%。The solar collector is composed of all-glass mirrors, solar collectors, temperature sensors, etc. The heat is absorbed by the solar heat collector and transported to the interlayer of the double-layer egg-shaped fermentation tank to adjust the temperature to ensure normal gas production under the condition of low external air temperature. Condenser reflection adopts all-glass specular mirror reflection, which has high optical efficiency. The solar collector adopts forced circulation, with high photothermal efficiency, and the system efficiency can reach 60% to 80%.
污泥焚烧炉所产生热量将水煮沸,5%~10%的蒸汽提供给热交换器,90%~95%的蒸汽提供给热电联产装置。The heat generated by the sludge incinerator boils the water, 5% to 10% of the steam is supplied to the heat exchanger, and 90% to 95% of the steam is supplied to the cogeneration unit.
热电联产装置包括燃气轮机、发电机、排烟器、余热锅炉和蒸汽轮机发电器。燃气轮机的进气口与甲烷压缩器的出气口通过管路相连。经压缩后的甲烷及空气进入燃气轮机,在燃烧室内混合燃烧,之后在汽轮机里膨胀,驱动叶轮转动,使其驱动发电机发电。燃气轮机的尾气温度很高(一般在500℃以上),是优良的驱动热源,高温尾气经过排烟器排烟后进行余热回收,经余热锅炉产生蒸汽,并使蒸汽在蒸汽轮机发电器中继续做功发电。污泥焚烧炉产生的蒸汽也将进入蒸汽轮机发电器中做功发电。热电联产装置总热效率可达75%-82%。Cogeneration units include gas turbines, generators, smoke extractors, waste heat boilers and steam turbine generators. The air inlet of the gas turbine is connected with the air outlet of the methane compressor through a pipeline. The compressed methane and air enter the gas turbine, mix and burn in the combustion chamber, and then expand in the steam turbine to drive the impeller to rotate, so that it drives the generator to generate electricity. The exhaust gas temperature of the gas turbine is very high (generally above 500 ℃), which is an excellent driving heat source. The high temperature exhaust gas is exhausted through the smoke exhauster for waste heat recovery, and the waste heat boiler generates steam, which makes the steam continue to do work in the steam turbine generator. generate electricity. The steam generated by the sludge incinerator will also enter the steam turbine generator to generate power. The total thermal efficiency of the cogeneration unit can reach 75%-82%.
热电联产装置与电力输出装置相连,产生电能经电力输出装置向电网或用电器供电,为板框压滤机、园区照明系统、臭气吸收处理装置等提供所需电力。The cogeneration device is connected to the power output device, and the generated electrical energy is supplied to the power grid or electrical appliances through the power output device to provide the required power for the plate and frame filter press, the park lighting system, and the odor absorption and treatment device.
如图2所示,本实施例包括有污泥浓缩池1、太阳能集热装置5、热交换器6、厌氧发酵罐7和热电联产装置20,污泥浓缩池1分为A池和B池,A池通过管路依次连接板框压滤机2、污泥干燥间3和污泥焚烧炉4;B池通过管路依次连接厌氧发酵罐7、沼液沼渣收集器18和分离器19;污泥焚烧炉4的一部分蒸汽通过管道输送至热交换器6,热交换器6的低温液体经管道与厌氧发酵罐7的夹层和太阳能集热装置5的管道循环相通;厌氧发酵罐7的出气口通过管道依次连通储气室8、沼气脱硫器9、沼气提纯器10和甲烷压缩器11,向热电联产装置20的燃气轮机12供气,污泥焚烧炉4的另一部分蒸汽通过管道输送至热电联产装置20的蒸汽轮机发电器16,热电联产装置20电连接电力输出装置17。As shown in FIG. 2 , this embodiment includes a
厌氧发酵罐7为双层蛋型结构,厌氧发酵罐7的中间夹层充满加热保温水。The
如图3所示,热电联产装置20包括燃气轮机12、发电机13、排烟器14、余热锅炉15和蒸汽轮机发电器16,燃气轮机转轴连接发电机13主轴,燃气轮机12的排气口连通排烟器14,排烟器14接入余热锅炉15,余热锅炉15的蒸汽经管道送至蒸汽轮机发电器16。As shown in FIG. 3 , the
Claims (3)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010076200.0A CN111233290A (en) | 2020-01-23 | 2020-01-23 | Sludge treatment system for sewage treatment plant |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010076200.0A CN111233290A (en) | 2020-01-23 | 2020-01-23 | Sludge treatment system for sewage treatment plant |
Publications (1)
Publication Number | Publication Date |
---|---|
CN111233290A true CN111233290A (en) | 2020-06-05 |
Family
ID=70876331
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202010076200.0A Pending CN111233290A (en) | 2020-01-23 | 2020-01-23 | Sludge treatment system for sewage treatment plant |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN111233290A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112344350A (en) * | 2020-10-30 | 2021-02-09 | 上海市政工程设计研究总院(集团)有限公司 | Sludge reduction treatment system and method |
Citations (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004284917A (en) * | 2003-03-25 | 2004-10-14 | Kurita Water Ind Ltd | Organic waste treatment method and treatment device |
CN101012095A (en) * | 2007-01-29 | 2007-08-08 | 清华大学 | Low consumption highly effective sludge drying method |
JP2007260538A (en) * | 2006-03-28 | 2007-10-11 | Toshiba Corp | Organic waste treatment system |
CN101056968A (en) * | 2004-11-10 | 2007-10-17 | 环境能量技术股份有限公司 | Method of slurry dewatering and conversion of biosolids to a renewable fuel |
KR100835964B1 (en) * | 2007-07-26 | 2008-06-10 | 고성호 | Sludge Drying System Using Waste Heat of Cogeneration Generator |
JP2008221142A (en) * | 2007-03-13 | 2008-09-25 | Kawasaki Plant Systems Ltd | Treatment method of waste and treatment equipment thereof |
JP2009028672A (en) * | 2007-07-30 | 2009-02-12 | Nippon Steel Engineering Co Ltd | Treatment method of high water-content waste and treatment apparatus |
JP2009045612A (en) * | 2007-07-20 | 2009-03-05 | Chugoku Electric Power Co Inc:The | Waste recycling method and facility |
CN101575163A (en) * | 2008-05-09 | 2009-11-11 | 北京博朗环境工程技术股份有限公司 | Power generation by mixed combustion of sludge-prepared methane and garbage and comprehensive utilization method thereof |
WO2010010071A2 (en) * | 2008-07-22 | 2010-01-28 | Nuova M.A.I.P. Macchine Agricole Industriali Pieralisi Societa' Per Azioni | Treatment system of sewage sludge and relevant energetic utilization for cogeneration. |
CN101885573A (en) * | 2009-05-11 | 2010-11-17 | 沈阳禹华环保有限公司 | Sludge treatment device using waste heat of boiler and treatment process thereof |
CN203668381U (en) * | 2013-11-19 | 2014-06-25 | 河南桑达能源环保有限公司 | Biogas circulating-type anaerobic fermentation, burning, power generation and organic fertilizer production system |
CN104628237A (en) * | 2015-01-23 | 2015-05-20 | 广东电网有限责任公司电力科学研究院 | Sludge drying incineration system based on thermal power plant |
CN107708882A (en) * | 2015-08-10 | 2018-02-16 | 日立造船株式会社 | It is attached to the high efficiency of energy Application way of the castoff burning facility of ethanol manufacturing equipment |
CN110386739A (en) * | 2019-08-14 | 2019-10-29 | 南昌航空大学 | A kind of aquaculture sewage sludge modularized treatment system and its treatment process |
-
2020
- 2020-01-23 CN CN202010076200.0A patent/CN111233290A/en active Pending
Patent Citations (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004284917A (en) * | 2003-03-25 | 2004-10-14 | Kurita Water Ind Ltd | Organic waste treatment method and treatment device |
CN101056968A (en) * | 2004-11-10 | 2007-10-17 | 环境能量技术股份有限公司 | Method of slurry dewatering and conversion of biosolids to a renewable fuel |
JP2007260538A (en) * | 2006-03-28 | 2007-10-11 | Toshiba Corp | Organic waste treatment system |
CN101012095A (en) * | 2007-01-29 | 2007-08-08 | 清华大学 | Low consumption highly effective sludge drying method |
JP2008221142A (en) * | 2007-03-13 | 2008-09-25 | Kawasaki Plant Systems Ltd | Treatment method of waste and treatment equipment thereof |
JP2009045612A (en) * | 2007-07-20 | 2009-03-05 | Chugoku Electric Power Co Inc:The | Waste recycling method and facility |
KR100835964B1 (en) * | 2007-07-26 | 2008-06-10 | 고성호 | Sludge Drying System Using Waste Heat of Cogeneration Generator |
JP2009028672A (en) * | 2007-07-30 | 2009-02-12 | Nippon Steel Engineering Co Ltd | Treatment method of high water-content waste and treatment apparatus |
CN101575163A (en) * | 2008-05-09 | 2009-11-11 | 北京博朗环境工程技术股份有限公司 | Power generation by mixed combustion of sludge-prepared methane and garbage and comprehensive utilization method thereof |
WO2010010071A2 (en) * | 2008-07-22 | 2010-01-28 | Nuova M.A.I.P. Macchine Agricole Industriali Pieralisi Societa' Per Azioni | Treatment system of sewage sludge and relevant energetic utilization for cogeneration. |
CN101885573A (en) * | 2009-05-11 | 2010-11-17 | 沈阳禹华环保有限公司 | Sludge treatment device using waste heat of boiler and treatment process thereof |
CN203668381U (en) * | 2013-11-19 | 2014-06-25 | 河南桑达能源环保有限公司 | Biogas circulating-type anaerobic fermentation, burning, power generation and organic fertilizer production system |
CN104628237A (en) * | 2015-01-23 | 2015-05-20 | 广东电网有限责任公司电力科学研究院 | Sludge drying incineration system based on thermal power plant |
CN107708882A (en) * | 2015-08-10 | 2018-02-16 | 日立造船株式会社 | It is attached to the high efficiency of energy Application way of the castoff burning facility of ethanol manufacturing equipment |
CN110386739A (en) * | 2019-08-14 | 2019-10-29 | 南昌航空大学 | A kind of aquaculture sewage sludge modularized treatment system and its treatment process |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112344350A (en) * | 2020-10-30 | 2021-02-09 | 上海市政工程设计研究总院(集团)有限公司 | Sludge reduction treatment system and method |
CN112344350B (en) * | 2020-10-30 | 2021-08-27 | 上海市政工程设计研究总院(集团)有限公司 | Sludge reduction treatment system and method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN101251045B (en) | Biomass energy circulating power generation process and power generation system thereof | |
CN102500604B (en) | Household solid garbage recycling and renewable biological carbon circulating technology | |
CN103087901B (en) | Distributed biological fermentation energy supply system | |
CN103471286B (en) | The distributed energy resource system of multiple renewable energy sources complementation | |
CN107524485B (en) | Renewable energy source energy supply system | |
CN106630135A (en) | A UASB reactor system and method based on compression heat pump | |
CN110283623A (en) | A kind of novel biomass-distributed solar polygenerations systeme | |
CN208282120U (en) | Coal cooperates with combustion power generation system with rubbish | |
CN112856563B (en) | A combined geothermal, solar and biogas power generation and heating system | |
CN111233290A (en) | Sludge treatment system for sewage treatment plant | |
CN106007285A (en) | Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method | |
CN207451916U (en) | A kind of new energy recycling sludge system | |
CN110822442B (en) | Biomass energy-based comprehensive heat supply system for life and coordination method | |
CN206156991U (en) | Device of methane is produced to municipal waste water treatment plant excess sludge | |
CN207568668U (en) | A kind of regenerative resource energy supplying system | |
CN217709199U (en) | Vacuum efficient drying equipment for sludge fuel | |
CN203906087U (en) | Power generation system utilizing fermented straws | |
CN202730116U (en) | Multi-energy coupling system for producing biogas by renewable energy | |
CN210858829U (en) | A biomass organic Rankine cycle power generation system controlled by pumped storage | |
CN115200257A (en) | Heat pump heat and cold electricity supply system of ecological zero-carbon-emission gas engine | |
CN203430632U (en) | Biomass distributive energy supply station | |
CN202199578U (en) | Kitchen waste treatment system | |
CN209065710U (en) | Quick processing system is combined in sludge pyrohydrolysis solar low-temperature film anaerobic digestion | |
CN207485487U (en) | Distributed biomass direct-fired co-generation unit | |
CN220624987U (en) | Waste heat recycling device for biogas power generation |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
WD01 | Invention patent application deemed withdrawn after publication | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20200605 |