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CN114873853A - Sewage treatment system of garbage compression transfer station - Google Patents

Sewage treatment system of garbage compression transfer station Download PDF

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CN114873853A
CN114873853A CN202210523723.4A CN202210523723A CN114873853A CN 114873853 A CN114873853 A CN 114873853A CN 202210523723 A CN202210523723 A CN 202210523723A CN 114873853 A CN114873853 A CN 114873853A
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sewage
transfer station
tank
treatment system
compression transfer
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CN114873853B (en
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赵增立
王小波
刘安琪
祝京旭
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Guangzhou Institute of Energy Conversion of CAS
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F2001/007Processes including a sedimentation step
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/14NH3-N
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/04Flow arrangements
    • C02F2301/046Recirculation with an external loop
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/06Sludge reduction, e.g. by lysis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

本发明公开了一种垃圾压缩中转站污水处理系统,包括第一沉淀池、缓冲池、粗滤池、污水反应器、第二沉淀池以及回用水池;垃圾压缩中转站产生的污水经过第一沉淀池除去杂物及可沉淀杂质后进入缓冲池暂存;所述污水处理系统设置有高负荷运行模式和低负荷运行模式;发明与现有技术相比,本发明适用于较高含水率的市政污水处理产生的污泥与煤的共气化资源化/能源化利用。相较于现有技术利用垃圾压缩中转站现有设施,充分考虑垃圾压缩站作业、污水产生及用水特点,有助于垃圾压缩中转站污水的达标排放及中水的循环回用。

Figure 202210523723

The invention discloses a sewage treatment system of a garbage compression transfer station, comprising a first sedimentation tank, a buffer tank, a coarse filter tank, a sewage reactor, a second sedimentation tank and a reuse tank; the sewage generated by the garbage compression transfer station passes through the first sedimentation tank. The sedimentation tank removes impurities and precipitable impurities and enters the buffer tank for temporary storage; the sewage treatment system is provided with a high-load operation mode and a low-load operation mode; compared with the prior art, the present invention is suitable for higher water content. Co-gasification of sludge and coal from municipal sewage treatment for resource/energy utilization. Compared with the existing technology of using the existing facilities of the waste compression transfer station, fully considering the operation of the waste compression station, the characteristics of sewage production and water use, it is helpful for the standard discharge of sewage and the recycling of reclaimed water in the waste compression transfer station.

Figure 202210523723

Description

垃圾压缩中转站污水处理系统Wastewater Compression Transfer Station Sewage Treatment System

技术领域technical field

本发明涉及环境工程技术领域,具体涉及一种垃圾压缩中转站污水处理及回用系统。The invention relates to the technical field of environmental engineering, in particular to a sewage treatment and reuse system of a waste compression transfer station.

背景技术Background technique

截止2020年我国城市生活垃圾年清运量为2.35亿吨,人均垃圾产生量约0.8kg/(人·天)。生活垃圾在产生端到最终处理(焚烧、填埋等)中间通常会经过压缩中转过程,以降低垃圾转运费用。生活垃圾中转压缩过程中大约会产生垃圾重量3%~5%的压滤液,在不同的场景下有时也被称作垃圾渗滤液。同时压缩中转站垃圾车清洗、地面冲洗、设备冲洗等过程也会产生一定的污水。上述几部分构成了生活垃圾压缩中转站污水的主要部分。生活压缩中转站通常只在白天连续作业,作业时间不超过8小时。由于生活压缩中转站污水来源及生活压缩中转站作业的特点,生活压缩中转站污水具有污染物浓度大、水质变化剧烈、排放集中、不溶性杂质含量高等特点。但目前大多数生活压缩中转站仅对污水设置了沉淀池,大量的压缩站污水没有得到妥善的处理及回用。As of 2020, the annual removal and transportation of urban domestic waste in my country is 235 million tons, and the per capita waste generation is about 0.8 kg/(person·day). Domestic waste usually undergoes a compression transfer process from the production end to the final treatment (incineration, landfill, etc.) to reduce waste transfer costs. About 3% to 5% of the garbage weight will be produced during the transfer compression process of domestic garbage, which is sometimes called landfill leachate in different scenarios. At the same time, certain sewage will also be generated during the process of garbage truck cleaning, ground flushing, and equipment flushing in the compression transfer station. The above-mentioned parts constitute the main part of the sewage in the domestic waste compression transfer station. The life compression transfer station usually only operates continuously during the day, and the operation time does not exceed 8 hours. Due to the source of sewage in the domestic compression transfer station and the characteristics of the operation of the domestic compression transfer station, the sewage of the domestic compression transfer station has the characteristics of high pollutant concentration, drastic changes in water quality, concentrated discharge, and high content of insoluble impurities. However, at present, most domestic compression transfer stations only set sedimentation tanks for sewage, and a large amount of sewage from compression stations has not been properly treated and reused.

专利文献CN112939339A提供一种垃圾渗滤液处理系统及其应用方法,其中,垃圾渗滤液处理系统,包括上层区和下层区,所述上层区设有加药装置、混凝反应池、清水池、气浮装置以及活性炭过滤器,下层区设有生化池;混凝反应池通过进液管抽取垃圾渗滤液,进液管上设有垃圾渗滤液抽取泵,加药装置连通至混凝反应池内,混凝反应池设有桨式搅拌机;气浮装置与混凝反应池连通;生化池与气浮装置连通;生化池与活性炭过滤器连通;但上述专利均未涉及如何针对压缩站污水的水质及排水特点,针对性的进行开发适用于压缩中转站污水达标处理及回用系统。Patent document CN112939339A provides a landfill leachate treatment system and an application method thereof, wherein the landfill leachate treatment system includes an upper layer area and a lower layer area, and the upper layer area is provided with a dosing device, a coagulation reaction tank, a clean water tank, a gas Floating device and activated carbon filter, and a biochemical tank is arranged in the lower area; the coagulation reaction tank extracts the landfill leachate through the liquid inlet pipe, and the liquid inlet pipe is provided with a landfill leachate extraction pump, and the dosing device is connected to the coagulation reaction tank. The coagulation reaction tank is equipped with a paddle mixer; the air flotation device is connected to the coagulation reaction tank; the biochemical tank is connected to the air flotation device; It is suitable for the standard sewage treatment and reuse system of the compression transfer station.

发明内容SUMMARY OF THE INVENTION

为了解决上述背景技术所存在的至少一技术问题,本发明提供一种垃圾压缩中转站污水处理系统。In order to solve at least one technical problem existing in the above-mentioned background art, the present invention provides a sewage treatment system for a waste compression transfer station.

为实现上述目的,本发明的技术方案是:For achieving the above object, the technical scheme of the present invention is:

垃圾压缩中转站污水处理系统,包括第一沉淀池、缓冲池、粗滤池、污水反应器、第二沉淀池以及回用水池;The sewage treatment system of the garbage compression transfer station includes a first sedimentation tank, a buffer tank, a coarse filter, a sewage reactor, a second sedimentation tank and a reuse tank;

垃圾压缩中转站产生的污水经过第一沉淀池除去杂物及可沉淀杂质后进入缓冲池暂存;The sewage generated by the garbage compression transfer station is removed by the first sedimentation tank to remove impurities and precipitated impurities, and then enters the buffer tank for temporary storage;

所述污水处理系统设置有高负荷运行模式和低负荷运行模式;The sewage treatment system is provided with a high-load operation mode and a low-load operation mode;

所述高负荷运行模式为:缓冲池中的污水以系统设计正常流量的70%~130%进入粗滤池去除污水中的不溶性杂质,然后进入污水反应器进行生化处理,处理后的污水进入第二沉淀池去除污水中的污泥,然后达标排放;The high-load operation mode is as follows: the sewage in the buffer tank enters the coarse filter at 70% to 130% of the normal flow of the system design to remove insoluble impurities in the sewage, and then enters the sewage reactor for biochemical treatment, and the treated sewage enters the first stage. The second sedimentation tank removes the sludge in the sewage, and then discharges up to the standard;

所述低负荷运行模式为:缓冲池中的污水以系统设计正常流量的20%~70%进入粗滤池去除污水中的不溶性杂质,然后进入污水反应器进行生化处理,处理后的污水进入第二沉淀池去除污水中的污泥,得到的清液进入回用水池作为再生水使用。The low-load operation mode is as follows: the sewage in the buffer tank enters the coarse filter at 20% to 70% of the normal flow of the system design to remove insoluble impurities in the sewage, and then enters the sewage reactor for biochemical treatment, and the treated sewage enters the first stage. The second sedimentation tank removes the sludge in the sewage, and the obtained clear liquid enters the reuse tank for use as reclaimed water.

进一步地,垃圾压缩中转站正常作业时段,且污水处理系统剩余未处理量大于回用水需求量150%~200%时,污水处理系统以高负荷模式运行;垃圾压缩中转站低负荷运行或停止作业时段,且污水处理系统剩余未处理量小于回用水需求量150%~200%时,污水处理系统以低负荷模式运行。Further, during the normal operation period of the garbage compression transfer station, and the remaining untreated amount of the sewage treatment system is greater than 150% to 200% of the demand for reuse water, the sewage treatment system operates in a high-load mode; the garbage compression transfer station operates at a low load or stops operation. During the period, and the remaining untreated amount of the sewage treatment system is less than 150% to 200% of the demand for reuse water, the sewage treatment system operates in a low-load mode.

进一步地,所述污水反应器为MBBR反应器。Further, the sewage reactor is an MBBR reactor.

进一步地,所述MBBR反应器为流化床反应器或固定床反应器。Further, the MBBR reactor is a fluidized bed reactor or a fixed bed reactor.

进一步地,所述缓冲池、粗滤池、污水反应器、第二沉淀池以及回用水池中产生的污泥定时排至第一沉淀池中,第一沉淀中的累积的不溶性杂质定时清理并送至垃圾压缩装置压缩脱水。Further, the sludge generated in the buffer tank, the coarse filter tank, the sewage reactor, the second sedimentation tank and the reuse tank is regularly discharged into the first sedimentation tank, and the accumulated insoluble impurities in the first sedimentation are regularly cleaned and removed. Send to the garbage compression device for compression and dehydration.

进一步地,所述不溶性杂质与生活垃圾混合后一起压缩脱水。Further, the insoluble impurities are compressed and dehydrated together after being mixed with the household garbage.

进一步地,在所述回用水池中设置灭菌装置。Further, a sterilization device is arranged in the recycle pool.

进一步地,当所述的垃圾压缩中转站产生的污水污染物浓度大于设计值150%时,污水处理系统全天以高负荷模式运行。Further, when the concentration of sewage pollutants produced by the waste compression transfer station is greater than 150% of the design value, the sewage treatment system operates in a high-load mode throughout the day.

本发明与现有技术相比,其有益效果在于:Compared with the prior art, the present invention has the following beneficial effects:

本发明利用垃圾压缩中转站现有设施,充分考虑垃圾压缩站作业、污水产生及用水特点,有助于垃圾压缩中转站污水的达标排放及中水的循环回用。The present invention utilizes the existing facilities of the garbage compression transfer station, fully considers the operation of the garbage compression station, the characteristics of sewage production and water use, and is helpful for the standard discharge of sewage in the garbage compression transfer station and the recycling of reclaimed water.

附图说明Description of drawings

图1为本发明实施例提供的污水处理系统高负荷运行模式流程图;1 is a flowchart of a high-load operation mode of a sewage treatment system provided by an embodiment of the present invention;

图2为本发明实施例提供的污水处理系统低负荷运行模式流程图;2 is a flowchart of a low-load operation mode of a sewage treatment system provided by an embodiment of the present invention;

图中:1、第一沉淀池;2、缓冲池;3、粗滤池;4、污水反应器;5、第二沉淀池;6、回用水池。In the figure: 1. The first sedimentation tank; 2. The buffer tank; 3. The coarse filter tank; 4. The sewage reactor; 5. The second sedimentation tank; 6. The reuse tank.

具体实施方式Detailed ways

下面结合附图和实施例对本发明的技术方案做进一步的说明。The technical solutions of the present invention will be further described below with reference to the accompanying drawings and embodiments.

实施例1:Example 1:

本实施例提供了一种垃圾压缩中转站污水处理系统,该系统包括如下装置:第一沉淀池1、缓冲池2、粗滤池3、污水反应器4、第二沉淀池5以及回用水池6。This embodiment provides a sewage treatment system for a waste compression transfer station. The system includes the following devices: a first sedimentation tank 1, a buffer tank 2, a coarse filter tank 3, a sewage reactor 4, a second sedimentation tank 5 and a reuse tank 6.

生活垃圾压缩站产生的污水经过第一沉淀池1除去大块杂物及可沉淀杂质,然后进入缓冲池暂存。污水处理系统有高负荷运行模式和低负荷运行模式。利用垃圾压缩站现有沉淀池(即第一沉淀池1)用于沉淀污水中的可沉淀及漂浮杂质,并配备专人定时清理沉淀池中的杂质。该垃圾压缩站通常作业时间为:6:00~14:00,在8小时就会完成一整天的压缩作业,会在短时间内产生大量的压缩污水,其他时段基本没用污水产生。缓冲池2能存储3天垃圾压缩中转站产生的污水,用于缓存短时间产生的大量垃圾压滤液并平衡不同来源污水(不同种类垃圾压滤液以及车辆/路面冲洗污水)的污染物浓度(COD、NH3-N等),从而达到进水量及污染物负荷的相对平稳,避免给污水系统照成过大的冲击。污水反应器优选采用MBBR反应器4,该类反应器采用固定化生物膜,污泥循环和水循环分离可以较好的适应污水污染物负荷及水量变化频繁的处理场景。The sewage generated by the domestic waste compression station passes through the first sedimentation tank 1 to remove large debris and precipitable impurities, and then enters the buffer tank for temporary storage. The sewage treatment system has a high-load operation mode and a low-load operation mode. The existing sedimentation tank (ie the first sedimentation tank 1) of the garbage compression station is used to settle the sedimentable and floating impurities in the sewage, and a special person is arranged to clean the impurities in the sedimentation tank regularly. The garbage compression station usually operates from 6:00 to 14:00. It will complete a whole day of compression in 8 hours, and will generate a large amount of compressed sewage in a short period of time, and basically no sewage is generated during other periods. The buffer pool 2 can store the sewage generated by the garbage compression transfer station for 3 days, which is used to buffer a large amount of garbage press filtrate produced in a short time and balance the pollutant concentration (COD) of sewage from different sources (different types of garbage press filtrate and vehicle/road washing sewage). , NH3-N, etc.), so as to achieve a relatively stable water intake and pollutant load, and avoid excessive impact on the sewage system. The sewage reactor preferably adopts the MBBR reactor 4. This type of reactor adopts immobilized biofilm, and the sludge circulation and water circulation separation can better adapt to the treatment scenarios where the sewage pollutant load and the water volume change frequently.

1)高负荷模式:高负荷模式生活垃圾压缩中转站污水处理以污水达到纳管标准为目标。缓冲池中的污水以系统设计正常流量的70%~130%进入粗滤池3去除污水中的不溶性杂质,然后进入MBBR反应器4进行生化处理,处理后的污水进入第二沉淀池5去除污水中的污泥,最后排放,如市政污水系统。1) High-load mode: In the high-load mode, the sewage treatment of the domestic waste compression transfer station aims to meet the management standard of sewage. The sewage in the buffer tank enters the coarse filter 3 to remove the insoluble impurities in the sewage at 70% to 130% of the normal flow of the system design, and then enters the MBBR reactor 4 for biochemical treatment, and the treated sewage enters the second sedimentation tank 5 to remove the sewage Sludge in the final discharge, such as the municipal sewage system.

2)低负荷模式:低负荷模式生活垃圾压缩中转站污水处理以污水回用为目标。缓冲,2中的污水以系统设计正常流量的20%~70%进入粗滤池3去除污水中的不溶性杂质,然后进入MBBR反应器进行生化处理,处理后的污水进入第二沉淀池5去除污水中的污泥,得到的清液进入回用水池6作为再生水使用。优选地,在回用水池6中还设置有灭菌装置。2) Low-load mode: In low-load mode, the sewage treatment of the domestic waste compression transfer station aims to reuse sewage. The sewage in buffer, 2 enters the coarse filter 3 at 20% to 70% of the normal flow of the system design to remove insoluble impurities in the sewage, and then enters the MBBR reactor for biochemical treatment, and the treated sewage enters the second sedimentation tank 5 to remove sewage Sludge in the sludge, the obtained clear liquid enters the reuse pool 6 and is used as reclaimed water. Preferably, a sterilization device is also provided in the recycling pool 6 .

生活垃圾压缩站正常作业时段,且污水处理系统剩余未处理量大于回用水需求量150%~200%时,污水处理系统以高负荷模式运行。生活垃圾压缩站低负荷运行或停止作业时段,且污水处理系统剩余未处理量小于回用水需求量150%~200%时,污水处理系统以低负荷During the normal operation period of the domestic waste compression station, and the remaining untreated amount of the sewage treatment system is greater than 150% to 200% of the demand for reused water, the sewage treatment system operates in a high-load mode. During the period of low-load operation or stop operation of the domestic waste compression station, and the remaining untreated amount of the sewage treatment system is less than 150% to 200% of the demand for reuse water, the sewage treatment system will operate at a low load.

在一具体实施例中,所述的MBBR反应器4为流化床反应器。可以更好的适应压缩站污水COD浓度大的特点,较快的实现生物膜的动态平衡实现自动脱膜,并可有效的减少污泥产生量。In a specific embodiment, the MBBR reactor 4 is a fluidized bed reactor. It can better adapt to the characteristics of high COD concentration in the sewage of the compression station, quickly realize the dynamic balance of the biofilm, realize automatic stripping, and effectively reduce the amount of sludge produced.

在一具体实施例中,所述的缓冲池2、粗滤池3、污水反应器4、第二沉淀池5以及回用水池6中产生的污泥及杂质定时排放到第一沉淀池1中。沉第一淀池1中的累积的不溶性杂质定时清理并送至垃圾压缩装置压缩脱水。优选的所述不溶性杂质可以与生活垃圾混合后一起压缩脱水。压缩站污水由于COD较高,污泥出率远高于生活污水的污泥产率是,约为100t DS/万m3。但因为污水总量较少,污泥的产量不多。以广州最常见的100t/d压缩规模的垃圾压缩中转站为例,每天产生污水总量约5吨,污水处理产生的污泥约250kg(以80%含水率计),建设单独的污泥脱水、存储、运输设备会照成较多的资源及投资浪费。采用垃圾压缩中转站现有的垃圾压缩设备进行污泥脱水并与垃圾一起运送至生活垃圾终端处理设施是最经济合理的处理方式。In a specific embodiment, the sludge and impurities generated in the buffer tank 2, the coarse filter tank 3, the sewage reactor 4, the second sedimentation tank 5 and the reuse tank 6 are regularly discharged into the first sedimentation tank 1 . The accumulated insoluble impurities in the first sedimentation tank 1 are cleaned regularly and sent to the garbage compression device for compression and dehydration. Preferably, the insoluble impurities can be compressed and dehydrated together after being mixed with household waste. Due to the high COD of the sewage in the compression station, the sludge output rate is much higher than that of the domestic sewage, which is about 100t DS/10,000 m3. However, because the total amount of sewage is small, the output of sludge is not much. Taking the most common 100t/d compression transfer station in Guangzhou as an example, the total amount of sewage produced is about 5 tons per day, and the sludge produced by sewage treatment is about 250kg (calculated at 80% moisture content), and a separate sludge dewatering station is constructed. , storage, and transportation equipment will result in more waste of resources and investment. It is the most economical and reasonable treatment method to use the existing garbage compression equipment in the garbage compression transfer station to dewater the sludge and transport it to the domestic garbage terminal treatment facility together with the garbage.

所述的生活垃圾压缩站产生的污水污染物浓度大于设计值150%时,生活垃圾压缩中转站废水处理系统可全天以高负荷模式运行。生活垃圾压缩中转站由于天气及压缩处理的垃圾种类的变化,垃圾压缩产生的污水COD浓度可能会出现大幅的变化,其日平均浓度有时会出现2~3倍的变化,在进水浓度过高时污水处理实施通过优先高负荷模式运行确保污水的达标排放。When the concentration of sewage pollutants produced by the domestic waste compression station is greater than 150% of the design value, the waste water treatment system of the domestic waste compression transfer station can operate in a high-load mode throughout the day. Due to changes in the weather and the type of garbage to be compressed in the domestic garbage compression transfer station, the COD concentration of sewage generated by garbage compression may change significantly, and the daily average concentration may sometimes change by 2 to 3 times. When the sewage treatment is implemented, the high-load mode operation is prioritized to ensure the discharge of sewage up to the standard.

Figure BDA0003643154980000041
Figure BDA0003643154980000041

Figure BDA0003643154980000051
Figure BDA0003643154980000051

上表给出了采用本系统处理某垃圾压缩中转站污水的水质情况。垃圾压缩中转站污水中污染物TCOD在6640~8100mg/L,NH3-N在78~97mg/L之间变化,经过本发明的系统处理后,高负荷模式下污水出水水质可稳定到达GB T 31962-2015所规定的污水排入城镇下水道水质相关要求;在低负荷处理模式下出水水质可稳定达到GBT18920-2020城市污水再生利用中所规定的道路、车辆冲洗用水水质要求。The above table shows the water quality of a waste compression transfer station treated by this system. The TCOD of pollutants in the sewage of the waste compression transfer station is 6640-8100 mg/L, and the NH3-N is between 78-97 mg/L. After the system treatment of the present invention, the quality of the sewage effluent in the high-load mode can stably reach GB T 31962. - The relevant requirements for the water quality of sewage discharged into urban sewers stipulated in 2015; the water quality of the effluent can stably meet the water quality requirements for road and vehicle washing stipulated in GBT18920-2020 urban sewage recycling and utilization in the low-load treatment mode.

实施例2:Example 2:

参考实施实例1,不同之处在于:所述的MBBR反应器4为固定床反应器。可以更好的适应压缩站污水COD浓度大的特点,并可有效的减少污泥产生量。当反应器内阻力增大时反应器固定化膜组件需定期脱膜。Referring to Example 1, the difference is that the MBBR reactor 4 is a fixed bed reactor. It can better adapt to the large concentration of COD in the sewage of the compression station, and can effectively reduce the amount of sludge produced. When the resistance in the reactor increases, the immobilized membrane module of the reactor needs to be removed periodically.

上述实施例只是为了说明本发明的技术构思及特点,其目的是在于让本领域内的普通技术人员能够了解本发明的内容并据以实施,并不能以此限制本发明的保护范围。凡是根据本发明内容的实质所做出的等效的变化或修饰,都应涵盖在本发明的保护范围内。The above-mentioned embodiments are only to illustrate the technical concept and characteristics of the present invention, and the purpose thereof is to enable those of ordinary skill in the art to understand the content of the present invention and implement them accordingly, and not to limit the protection scope of the present invention. All equivalent changes or modifications made according to the essence of the present invention shall be included within the protection scope of the present invention.

Claims (8)

1. The sewage treatment system of the garbage compression transfer station is characterized by comprising a first sedimentation tank, a buffer tank, a rough filtration tank, a sewage reactor, a second sedimentation tank and a reuse water tank;
the sewage generated by the garbage compression transfer station enters a buffer tank for temporary storage after impurities and precipitable impurities are removed by a first sedimentation tank;
the sewage treatment system is provided with a high-load operation mode and a low-load operation mode;
the high-load operation mode is as follows: sewage in the buffer tank enters a coarse filtration tank to remove insoluble impurities in the sewage at 70-130% of the normal flow of the system design, then enters a sewage reactor to carry out biochemical treatment, and the treated sewage enters a second sedimentation tank to remove sludge in the sewage and then reaches the standard to be discharged;
the low-load operation mode is as follows: sewage in the buffer tank enters a coarse filtration tank to remove insoluble impurities in the sewage by 20-70% of the normal flow of the system design, then enters a sewage reactor to carry out biochemical treatment, the treated sewage enters a second sedimentation tank to remove sludge in the sewage, and the obtained clear liquid enters a reuse water tank to be used as reclaimed water.
2. The waste compression transfer station sewage treatment system of claim 1, wherein when the waste compression transfer station is in a normal operation period and the remaining untreated amount of the sewage treatment system is 150% to 200% greater than the demand of the reuse water, the sewage treatment system operates in a high-load mode; and when the garbage compression transfer station runs in a low-load mode or stops working, and the residual untreated capacity of the sewage treatment system is 150-200% smaller than the demand of the reuse water, the sewage treatment system runs in a low-load mode.
3. The waste compression transfer station sewage treatment system of claim 1, wherein the sewage reactor is an MBBR reactor.
4. The waste compression transfer station sewage treatment system of claim 3, wherein the MBBR reactor is a fluidized bed reactor or a fixed bed reactor.
5. The waste water treatment system of the waste compression transfer station as claimed in claim 1, wherein the sludge generated in the buffer tank, the coarse filtration tank, the waste water reactor, the second sedimentation tank and the reuse water tank is discharged into the first sedimentation tank at regular time, and the insoluble impurities accumulated in the first sedimentation tank are cleaned at regular time and sent to the waste compression device for compression and dehydration.
6. The sewage treatment system of the garbage compression transfer station as claimed in claim 5, wherein the insoluble impurities are compressed and dehydrated together with the domestic garbage after being mixed.
7. The sewage treatment system of the garbage compression transfer station as claimed in claim 1, wherein a sterilization device is provided in the reuse water tank.
8. The waste water treatment system of the waste compression transfer station of claim 1, wherein when the concentration of the waste water pollutants generated by the waste compression transfer station is greater than 150% of a designed value, the waste water treatment system is operated in a high-load mode all day.
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110066067A (en) * 2019-03-13 2019-07-30 杭州电子科技大学 The processing unit of leachate in garbage transfer station
CN210030276U (en) * 2018-12-21 2020-02-07 湖南北控威保特环境科技股份有限公司 Leachate treatment device for garbage transfer station
CN211664918U (en) * 2020-01-15 2020-10-13 上海丽臻环保科技有限公司 Leachate treatment equipment for garbage transfer station
CN113860637A (en) * 2021-09-24 2021-12-31 物产中大公用环境投资有限公司 Method and system for treating leachate of refuse transfer station in southern region

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN210030276U (en) * 2018-12-21 2020-02-07 湖南北控威保特环境科技股份有限公司 Leachate treatment device for garbage transfer station
CN110066067A (en) * 2019-03-13 2019-07-30 杭州电子科技大学 The processing unit of leachate in garbage transfer station
CN211664918U (en) * 2020-01-15 2020-10-13 上海丽臻环保科技有限公司 Leachate treatment equipment for garbage transfer station
CN113860637A (en) * 2021-09-24 2021-12-31 物产中大公用环境投资有限公司 Method and system for treating leachate of refuse transfer station in southern region

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