CN100450940C - High-concentration biochemical aerator - Google Patents
High-concentration biochemical aerator Download PDFInfo
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- CN100450940C CN100450940C CNB2006100250110A CN200610025011A CN100450940C CN 100450940 C CN100450940 C CN 100450940C CN B2006100250110 A CNB2006100250110 A CN B2006100250110A CN 200610025011 A CN200610025011 A CN 200610025011A CN 100450940 C CN100450940 C CN 100450940C
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- Prior art keywords
- pipe
- air
- biochemical
- water
- sludge
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- 238000005276 aerator Methods 0.000 title claims abstract description 8
- 239000010802 sludge Substances 0.000 claims abstract description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 28
- 230000006835 compression Effects 0.000 claims abstract description 10
- 238000007906 compression Methods 0.000 claims abstract description 10
- 238000009792 diffusion process Methods 0.000 claims description 10
- 238000005086 pumping Methods 0.000 claims description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 9
- 239000001301 oxygen Substances 0.000 abstract description 9
- 229910052760 oxygen Inorganic materials 0.000 abstract description 9
- 238000012423 maintenance Methods 0.000 abstract description 6
- 230000000694 effects Effects 0.000 abstract description 3
- 239000007788 liquid Substances 0.000 abstract description 3
- 239000010865 sewage Substances 0.000 description 9
- 238000006213 oxygenation reaction Methods 0.000 description 6
- 239000000203 mixture Substances 0.000 description 5
- 238000005273 aeration Methods 0.000 description 3
- 230000008602 contraction Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 230000007547 defect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 239000011499 joint compound Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
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Classifications
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- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
Description
一、技木领域:1. Technical field:
本发明高浓度生化曝气器,涉及的污水处理技术领域,特别涉及充氧装置技术领域,应用于污水处理工程,生化池、调节池等充氧。The high-concentration biochemical aerator of the present invention relates to the technical field of sewage treatment, in particular to the technical field of oxygenation devices, and is applied to sewage treatment projects, biochemical pools, regulating pools, etc. for oxygenation.
二、背景技术2. Background technology
目前,污水处理工程生化充氧装置均采用鼓风机装置,普遍存在着:该鼓风机充氧一般水位均在4m~5m,如风机压力不够,它的充氧行程短,由于微气泡上升中,在水压下若干个拼合在一起形成大气泡,比重更轻,充氧中的氧分子很快浮出水面,形成能源浪费;若不提高供氧量,则生化就开不好,势必在提高供氧耗电量,使运行成本成倍提高;由于采用鼓风机,它必须要配有曝气头,进行大面积供气,曝气头易阻塞,造成气流断路,供氧不均,维修时,必需抽去污水池内液情况下进行,造成管路修理时间长,维修成本高,维修技术要求高,直接影响了使用效率。At present, the biochemical oxygenation devices in sewage treatment projects all use blower devices, which generally exist: the general water level of the blower oxygenation is 4m~5m. If the pressure of the blower is not enough, its oxygenation stroke is short. Press down several pieces and put them together to form large bubbles with lighter specific gravity. The oxygen molecules in the oxygenation will quickly surface, resulting in waste of energy; Power consumption doubles the operating cost; due to the use of a blower, it must be equipped with an aeration head to supply air to a large area. It is carried out under the condition of removing the liquid in the sewage tank, resulting in long pipeline repair time, high maintenance cost and high maintenance technical requirements, which directly affects the use efficiency.
三、发明内容:3. Contents of the invention:
本发明的目的在于克服上述缺陷,采用气水混合、气水压缩、气水扩散的方法,设计一种以泵作为动力源的高浓度生化曝气器。其技术方案是这样实现的:包括污泥泵、进口设在生化池底的污泥泵进管、污泥泵出管,其特征在于:还包括自上而下按顺序固定连接的负压室、气水混合管、一次压缩管、二次扩缩管、气水扩散管、池底喷口,所述气水扩散管的下端设有喷口,污泥泵出管的输出口连接负压室的顶端。气水扩散管下端设有4~15只喷口,呈梅花状排列,池底喷口在1-3只范围内,一次压缩管、二次扩缩管的中间收缩,两端呈喇叭口的结构。实施该技术后的明显效果是:生化池的液位一般均在8m以上,增加了生化池容积,使空气微泡行程增加一倍,达到氧的利用率增加,使水与气形成初级溶气状,使空气中氧穿透在活性污泥层里,达到泥、水、气分离慢,充分提高溶解氧均匀,提高了氧的转移率和利用率可达45%,是现有鼓风曝气的4倍以上,由于设置喷口器射和一个对池底,形成生化污泥全部在池中翻动,不需在池底设纵、横、管道和曝气头,节约投资。确保生化池上、中、下,无污泥因缺氧造成膨胀恶劣现象。由于采用水泵作动力,噪声低,不需严密的隔声的设置,操作方便,维修成本低,维修期比鼓风机少90%,对水体中CODcr、BOD5等去除率高,并且去除效果稳定。The object of the present invention is to overcome above-mentioned defect, adopt the method of air-water mixing, air-water compression, air-water diffusion, design a kind of high-concentration biochemical aerator with pump as power source. Its technical solution is realized as follows: it includes a sludge pump, a sludge pump inlet pipe and a sludge pump outlet pipe whose inlet is located at the bottom of the biochemical tank, and is characterized in that it also includes negative pressure chambers that are fixedly connected in sequence from top to bottom , air-water mixing pipe, primary compression pipe, secondary expansion pipe, air-water diffusion pipe, nozzle at the bottom of the pool, the lower end of the air-water diffusion pipe is provided with a nozzle, and the output port of the sludge pumping pipe is connected to the negative pressure chamber top. There are 4 to 15 nozzles at the lower end of the air-water diffusion pipe, which are arranged in a plum blossom shape. The nozzles at the bottom of the pool are within the range of 1 to 3 nozzles. The obvious effect after the implementation of this technology is: the liquid level of the biochemical pool is generally above 8m, which increases the volume of the biochemical pool, doubles the stroke of air microbubbles, increases the utilization rate of oxygen, and makes water and air form primary dissolved air. shape, so that the oxygen in the air penetrates into the activated sludge layer, achieves the slow separation of mud, water and gas, fully improves the uniformity of dissolved oxygen, and improves the transfer rate and utilization rate of oxygen up to 45%. The gas is more than 4 times that of the tank. Due to the installation of the nozzle jet and a counter to the bottom of the pool, all the biochemical sludge is turned in the pool. There is no need to set up vertical, horizontal, pipes and aeration heads at the bottom of the pool, saving investment. Make sure that the upper, middle and lower parts of the biochemical pool are free from bad expansion of sludge due to lack of oxygen. Due to the use of water pumps as power, low noise, no need for strict sound insulation settings, easy operation, low maintenance costs, maintenance period is 90% less than that of blowers, high removal rate of CODcr, BOD 5 in water, and stable removal effect.
四、附图说明:4. Description of drawings:
图1为本发明的剖视结构示意图,Fig. 1 is the sectional structure schematic diagram of the present invention,
其中,1-负压室、1-1-空气通道、2-气水混合管、3-一次压缩管4-二次扩缩管、5-气水扩散管、6-喷口、7-池底喷口、8-污泥层、9-生化池、10-污泥泵、10-1-污泥泵进管、10-2-污泥泵出管。Among them, 1-negative pressure chamber, 1-1-air channel, 2-air-water mixing tube, 3-primary compression tube, 4-secondary expansion tube, 5-air-water diffusion tube, 6-nozzle, 7-pool bottom Nozzle, 8-sludge layer, 9-biochemical pool, 10-sludge pump, 10-1-sludge pump inlet pipe, 10-2-sludge pump outlet pipe.
五、具体实施方式:5. Specific implementation methods:
以下结合附图以8m池为例,对本发明作进一步描述:Take the 8m pool as an example below in conjunction with accompanying drawing, the present invention will be further described:
见图1,高浓度生化曝气器设在8m深的生化池9,污泥泵10污泥泵进管10-1进入生化池9污泥层8,污泥泵10的污泥泵出管10-2连接负压室1,负压室1侧面设有空气通道1-1,负压室1下端按气水混合管2、一次压缩管3、二次压缩管4、气水扩散管5的顺序固定连接,气水扩散管5的下端侧面设有4只按圆周均匀排列的喷口6,1只池底喷口7面向池底。As shown in Figure 1, the high-concentration biochemical aerator is installed in the 8m-deep
见图1,通电,污泥泵10启动,不断抽取的污泥与污水的混合物经污泥泵进管10-1,污泥泵10、污泥泵出管10-2进入负压室1,污泥与污水的混合物在负压室1内被扩散,形成负压,空气经空气通道1-1进入负压室1,污泥与污水的混合物与空气进入气水混合管2进行混合,混合后的混合物进入一次压缩管3进行缩、扩膨胀,再进入二次扩缩管4进行二次缩、扩膨胀,缩、扩膨胀的混合物进入气水扩散管5进行散曝,由4只喷口6、1只池底喷口7均匀喷出,池底喷口7对污泥层8的污泥进行不沉淀的翻滚,作循环工作;使污泥与污水的混合物与吸入空气经8m管线扩缩,散曝扩散在池底喷出,喷距达2m,喷出的水与气形成初级溶气状,使空气中氧穿透在活性污泥层里,达到泥、水、气慢分离,充分提高氧的转移率和利用率,达到污水处理的目的。As shown in Fig. 1, power on,
Claims (3)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2006100250110A CN100450940C (en) | 2006-03-23 | 2006-03-23 | High-concentration biochemical aerator |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2006100250110A CN100450940C (en) | 2006-03-23 | 2006-03-23 | High-concentration biochemical aerator |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101037263A CN101037263A (en) | 2007-09-19 |
| CN100450940C true CN100450940C (en) | 2009-01-14 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2006100250110A Expired - Fee Related CN100450940C (en) | 2006-03-23 | 2006-03-23 | High-concentration biochemical aerator |
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| CN (1) | CN100450940C (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101549930B (en) * | 2008-04-03 | 2012-08-15 | 上海百峰环保工程有限公司 | System and method for processing high-concentration printing and dyeing wastewater |
| CN103917289B (en) * | 2011-11-11 | 2017-03-08 | 伊莱克斯家用产品公司 | Mixing device, carbonator, appliance comprising carbonator and method for producing carbonated beverages |
| CN109368824B (en) * | 2018-12-08 | 2024-09-20 | 中国二十二冶集团有限公司 | High-efficiency jet aerator |
| CN109851042A (en) * | 2019-04-12 | 2019-06-07 | 广州易能克科技有限公司 | Water oxygenation equipment |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55128700A (en) * | 1979-03-23 | 1980-10-04 | Aimu Denki Kogyo Kk | Ejector for deep tank |
| JPS6460367A (en) * | 1987-08-31 | 1989-03-07 | Kubota Ltd | Microorganism treating device |
| CN1266379A (en) * | 1998-04-28 | 2000-09-13 | 生活国际产品有限公司 | Oxygenating apparatus, method for oxygenating a liquid therewith, and applications thereof |
| CN2436502Y (en) * | 2000-06-28 | 2001-06-27 | 黄超 | Hydraulic automatic air pumping mixing aerator |
| US20050133456A1 (en) * | 2003-12-17 | 2005-06-23 | Beretta David Iii | System and method for in-well aeration |
| CN2918401Y (en) * | 2006-03-23 | 2007-07-04 | 上海百峰环保工程有限公司 | High concentration biochemical aerator |
-
2006
- 2006-03-23 CN CNB2006100250110A patent/CN100450940C/en not_active Expired - Fee Related
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55128700A (en) * | 1979-03-23 | 1980-10-04 | Aimu Denki Kogyo Kk | Ejector for deep tank |
| JPS6460367A (en) * | 1987-08-31 | 1989-03-07 | Kubota Ltd | Microorganism treating device |
| CN1266379A (en) * | 1998-04-28 | 2000-09-13 | 生活国际产品有限公司 | Oxygenating apparatus, method for oxygenating a liquid therewith, and applications thereof |
| CN2436502Y (en) * | 2000-06-28 | 2001-06-27 | 黄超 | Hydraulic automatic air pumping mixing aerator |
| US20050133456A1 (en) * | 2003-12-17 | 2005-06-23 | Beretta David Iii | System and method for in-well aeration |
| CN2918401Y (en) * | 2006-03-23 | 2007-07-04 | 上海百峰环保工程有限公司 | High concentration biochemical aerator |
Non-Patent Citations (1)
| Title |
|---|
| US2005/0133456A1 2005.06.23 |
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| Publication number | Publication date |
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| CN101037263A (en) | 2007-09-19 |
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Granted publication date: 20090114 Termination date: 20190323 |