CN115246695A - Sewage treatment pond with antibiotic function of degradation - Google Patents
Sewage treatment pond with antibiotic function of degradation Download PDFInfo
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- CN115246695A CN115246695A CN202210060730.5A CN202210060730A CN115246695A CN 115246695 A CN115246695 A CN 115246695A CN 202210060730 A CN202210060730 A CN 202210060730A CN 115246695 A CN115246695 A CN 115246695A
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- 239000010865 sewage Substances 0.000 title claims abstract description 24
- 230000003115 biocidal effect Effects 0.000 title description 10
- 230000015556 catabolic process Effects 0.000 title description 10
- 238000006731 degradation reaction Methods 0.000 title description 10
- 230000001699 photocatalysis Effects 0.000 claims abstract description 40
- 238000004062 sedimentation Methods 0.000 claims abstract description 38
- 238000001179 sorption measurement Methods 0.000 claims abstract description 35
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 30
- 239000003242 anti bacterial agent Substances 0.000 claims abstract description 29
- 229940088710 antibiotic agent Drugs 0.000 claims abstract description 29
- 230000000593 degrading effect Effects 0.000 claims abstract description 14
- 239000002127 nanobelt Substances 0.000 claims abstract description 13
- 239000002893 slag Substances 0.000 claims abstract description 11
- 238000005273 aeration Methods 0.000 claims abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 50
- 230000005540 biological transmission Effects 0.000 claims description 22
- 238000009826 distribution Methods 0.000 claims description 22
- 239000012528 membrane Substances 0.000 claims description 15
- 238000001223 reverse osmosis Methods 0.000 claims description 14
- 238000003756 stirring Methods 0.000 claims description 7
- 229920002492 poly(sulfone) Polymers 0.000 claims description 6
- 239000004760 aramid Substances 0.000 claims description 4
- 229920003235 aromatic polyamide Polymers 0.000 claims description 4
- 239000004745 nonwoven fabric Substances 0.000 claims description 4
- 238000005192 partition Methods 0.000 claims description 4
- 229920000728 polyester Polymers 0.000 claims description 4
- 230000003197 catalytic effect Effects 0.000 claims description 3
- 239000004744 fabric Substances 0.000 claims 1
- 239000002351 wastewater Substances 0.000 abstract description 30
- 230000000694 effects Effects 0.000 abstract description 5
- 238000000034 method Methods 0.000 description 14
- 239000000126 substance Substances 0.000 description 12
- 244000005700 microbiome Species 0.000 description 7
- 238000002156 mixing Methods 0.000 description 4
- 238000010170 biological method Methods 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 239000003814 drug Substances 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 238000005086 pumping Methods 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000003749 cleanliness Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- 230000004927 fusion Effects 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 238000007146 photocatalysis Methods 0.000 description 1
- 239000011941 photocatalyst Substances 0.000 description 1
- 238000013032 photocatalytic reaction Methods 0.000 description 1
- 238000000053 physical method Methods 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
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Abstract
本发明公开了一种具有降解抗生素功能的污水处理池,涉及污水处理技术领域,为解决现有的污水处理池对于废水中抗生素处理效果较差的问题。所述加药沉淀池,所述加药沉淀池的一侧设置有光催化池,所述光催化池的一侧设置有吸附过滤池,所述加药沉淀池的底部设置有斜壁,所述加药沉淀池底部的一侧设置有排污口,所述加药沉淀池内部的一侧安装有过滤筒,所述光催化池的内部设置有InTi纳米带,所述光催化池的底部安装有曝气管,且曝气管的一端延伸至光催化池的外部,所述吸附过滤池的内部由上至下依次设置有碎石层、卵石层和炉渣层,所述吸附过滤池内部的下端设置有活性炭层,所述吸附过滤池一侧的下端设置有排水口。
The invention discloses a sewage treatment tank with the function of degrading antibiotics, relates to the technical field of sewage treatment, and solves the problem that the existing sewage treatment tank has poor treatment effect on antibiotics in wastewater. In the dosing sedimentation tank, a photocatalytic pool is arranged on one side of the dosing sedimentation tank, an adsorption filter tank is arranged on one side of the photocatalytic pool, and an inclined wall is arranged at the bottom of the dosing sedimentation tank, so the One side of the bottom of the dosing sedimentation tank is provided with a sewage outlet, one side of the inside of the dosing sedimentation tank is installed with a filter cartridge, the interior of the photocatalytic pool is provided with InTi nanobelts, and the bottom of the photocatalytic pool is installed There is an aeration pipe, and one end of the aeration pipe extends to the outside of the photocatalytic pool. The inside of the adsorption filter tank is sequentially provided with a gravel layer, a pebble layer and a slag layer from top to bottom. An activated carbon layer is arranged at the lower end, and a drainage port is arranged at the lower end of one side of the adsorption filter tank.
Description
技术领域technical field
本发明涉及污水处理技术领域,具体为一种具有降解抗生素功能的污水处理池。The invention relates to the technical field of sewage treatment, in particular to a sewage treatment pool with the function of degrading antibiotics.
背景技术Background technique
目前,我国有抗生素生产企业300 多家,约占世界总产量的30%,年产抗生素原料约21 万吨,年排放抗生素废水在5000多万吨,抗生素是一类由微生物代谢产生的、在低浓度下能抑制或杀灭其他微生物的化学物质。抗生素废水色度高、含多种难降解及生物毒性物质,是一种高浓度有机废水。废水中残留的抗生素会对环境造成潜在的影响,抗生素废水的处理方法主要有物理法、化学法和生物法等。物理法主要有气浮法、吸附法和膜技术;化学法主要有臭氧氧化法、Fenton 氧化法和电化学技术;生物法主要有SBR法、MBR 法和上流式厌氧污泥床法。At present, there are more than 300 antibiotic production enterprises in my country, accounting for about 30% of the world's total production. The annual output of antibiotic raw materials is about 210,000 tons, and the annual discharge of antibiotic wastewater is more than 50 million tons. A chemical substance that inhibits or kills other microorganisms at low concentrations. Antibiotic wastewater has high chroma, contains various refractory and biotoxic substances, and is a kind of high-concentration organic wastewater. Antibiotic residues in wastewater will have a potential impact on the environment, and antibiotic wastewater treatment methods mainly include physical, chemical, and biological methods. Physical methods mainly include air flotation, adsorption and membrane technology; chemical methods mainly include ozone oxidation, Fenton oxidation and electrochemical technology; biological methods mainly include SBR method, MBR method and upflow anaerobic sludge bed method.
但是,现有的对于含有抗生素的废水处理方式较为单一,不能够从多方面进行深度处理,不仅废水处理过程效率较低,而且对于处理后的废水依旧存在抗生素残留,因此不满足现有的需求,对此我们提出了一种具有降解抗生素功能的污水处理池。However, the existing treatment method for wastewater containing antibiotics is relatively single, and it cannot carry out advanced treatment from multiple aspects. Not only is the efficiency of the wastewater treatment process low, but there are still antibiotic residues in the treated wastewater, so it does not meet the existing needs. , we proposed a sewage treatment pond with the function of degrading antibiotics.
发明内容SUMMARY OF THE INVENTION
本发明的目的在于提供一种具有降解抗生素功能的污水处理池,以解决上述背景技术中提出的污水处理池对于废水中抗生素处理效果较差的问题。The purpose of the present invention is to provide a sewage treatment tank with the function of degrading antibiotics, so as to solve the problem that the sewage treatment tank has a poor treatment effect on antibiotics in wastewater proposed in the background art.
为实现上述目的,本发明提供如下技术方案:一种具有降解抗生素功能的污水处理池,包括加药沉淀池,所述加药沉淀池的一侧设置有光催化池,所述光催化池的一侧设置有吸附过滤池,所述加药沉淀池的底部设置有斜壁,所述加药沉淀池底部的一侧设置有排污口,所述加药沉淀池内部的一侧安装有过滤筒,所述光催化池的内部设置有InTi纳米带,且InTi纳米带与光催化池通过卡槽限位,所述光催化池的底部安装有曝气管,且曝气管的一端延伸至光催化池的外部,所述吸附过滤池的内部由上至下依次设置有碎石层、卵石层和炉渣层,所述吸附过滤池内部的下端设置有活性炭层,所述吸附过滤池一侧的下端设置有排水口。In order to achieve the above object, the present invention provides the following technical solutions: a sewage treatment pond with the function of degrading antibiotics, comprising a dosing sedimentation pond, one side of the dosing and sedimentation pond is provided with a photocatalytic pond, the photocatalytic pond One side is provided with an adsorption filter tank, the bottom of the dosing sedimentation tank is provided with an inclined wall, one side of the bottom of the dosing sedimentation tank is provided with a sewage outlet, and one side of the dosing sedimentation tank is equipped with a filter cartridge , the inside of the photocatalytic pool is provided with an InTi nanobelt, and the InTi nanobelt and the photocatalytic pool are limited by a slot, and an aeration tube is installed at the bottom of the photocatalytic pool, and one end of the aeration tube extends to the photocatalytic pool. The outside of the catalytic pool, the interior of the adsorption filter pool is provided with gravel layer, pebble layer and slag layer from top to bottom in sequence, the lower end of the inside of the adsorption filter pool is provided with an activated carbon layer, and the side of the adsorption filter pool is The lower end is provided with a drainage port.
优选的,所述加药沉淀池和光催化池之间设置有第一连接管,且第一连接管的一端延伸至过滤筒的内部,所述第一连接管的中间位置处安装有抽泵,所述过滤筒的外壁缠卷有反渗透膜,且反渗透膜由交联芳香族聚酰胺、聚砜和聚酯无纺布复合而成。Preferably, a first connecting pipe is provided between the dosing sedimentation tank and the photocatalytic tank, and one end of the first connecting pipe extends to the inside of the filter cartridge, and a pump is installed in the middle of the first connecting pipe, so that The outer wall of the filter cartridge is wrapped with a reverse osmosis membrane, and the reverse osmosis membrane is composed of cross-linked aromatic polyamide, polysulfone and polyester non-woven fabric.
优选的,所述加药沉淀池的上端固定设置有第一固定板,所述第一固定板上端面的中间位置处安装有第一电机,所述第一电机的输出轴安装有旋转轴,且旋转轴延伸至加药沉淀池的内部,所述旋转轴的下端固定安装有搅拌叶片。Preferably, the upper end of the dosing sedimentation tank is fixedly provided with a first fixed plate, a first motor is installed at the middle position on the upper surface of the first fixed plate, and a rotating shaft is installed on the output shaft of the first motor, And the rotating shaft extends to the inside of the dosing sedimentation tank, and the lower end of the rotating shaft is fixedly equipped with stirring blades.
优选的,所述加药沉淀池的内壁上设置有刮板,刮板设置有若干个,且刮板依次等距设置,所述刮板的内部固定设置有分割条,所述分割条与刮板之间形成缝隙。Preferably, the inner wall of the dosing sedimentation tank is provided with a scraper, and there are several scrapers, and the scrapers are arranged equidistantly in sequence, and the inside of the scraper is fixedly provided with a partition bar, and the partition bar is connected with the scraper A gap is formed between the plates.
优选的,所述光催化池的上端固定设置有第二固定板,且第二固定板设置有两个,所述第二固定板的下端均安装有高压泵灯,且高压泵灯位于InTi纳米带的上方。Preferably, the upper end of the photocatalytic pool is fixedly provided with a second fixing plate, and there are two second fixing plates, and the lower ends of the second fixing plates are equipped with high-pressure pump lamps, and the high-pressure pump lamps are located at the InTi nano top of the belt.
优选的,所述吸附过滤池的上端设置有第三固定板,所述第三固定板的中间位置处设置有驱动箱,所述光催化池与吸附过滤池之间设置有第二连接管,所述第二连接管的中间位置处安装有水泵。Preferably, the upper end of the adsorption filter pool is provided with a third fixed plate, a driving box is provided at the middle position of the third fixed plate, and a second connecting pipe is provided between the photocatalytic pool and the adsorption filter pool, so that A water pump is installed at the middle position of the second connecting pipe.
优选的,所述驱动箱的内部固定安装有第二电机,所述第二电机的一侧设置有传动轴,传动轴与第三固定板旋转配合,且第二电机的输出端与传动轴通过传动带传动配合,所述第二连接管的一端与传动轴旋转配合,所述传动轴的下端固定安装有布水管,所述布水管的下端设置有五个对称分布的喷嘴。Preferably, a second motor is fixedly installed inside the drive box, a transmission shaft is provided on one side of the second motor, and the transmission shaft is rotatably matched with the third fixed plate, and the output end of the second motor passes through the transmission shaft. The transmission belt is driven and matched, and one end of the second connecting pipe is rotatably matched with the transmission shaft. The lower end of the transmission shaft is fixedly equipped with a water distribution pipe, and the lower end of the water distribution pipe is provided with five symmetrically distributed nozzles.
优选的,所述炉渣层与活性炭层之间设置有布水板,且布水板与吸附过滤池通过螺栓固定,所述布水板的内部设置有若干等距分布的凹槽,所述凹槽的底部均设置有流管。Preferably, a water distribution plate is arranged between the slag layer and the activated carbon layer, and the water distribution plate and the adsorption filter tank are fixed by bolts, and a number of equally spaced grooves are arranged inside the water distribution plate, and the grooves Flow tubes are provided at the bottom of the tanks.
与现有技术相比,本发明的有益效果是:Compared with the prior art, the beneficial effects of the present invention are:
1、本发明采用加药沉淀池、光催化池以及吸附过滤池的互相配合,实现对水中抗生素的深度处理,在加药沉淀池中工作人员可优先调节废水pH值,随后加药开启第一电机,其输出轴带动搅拌叶片进行转动,形成废水与药剂的快速混合,混合至设定时间后,静置废水,在与药剂的作用下,废水中有害物质逐渐与废水发生分离,形成絮状物,在斜壁上堆积沉淀,随后在抽泵的作用下将经过絮凝沉淀的废水输送至光催化池,通过与曝气管的互相配合形成对废水中抗生素的快速降解,最后将经过光催化及曝气的水体输送至吸附过滤池,吸附过滤池内部设置生物滤床,生物滤床由碎石层、卵石层、炉渣层以及活性炭层组成,利用较大的比表面积,有利于微生物的快速生长,利用微生物对通过废水中的抗生素等有害物质进行降解,环保且高效,最后经过活性炭过滤的清洁水通过排水口排出,通过这种方式,利用不同的降解方式对含有抗生素的废水进行多层级处理,在保证处理质量的同时提高对抗生素的降解效率。1. The present invention adopts the mutual cooperation of the dosing sedimentation tank, the photocatalytic pool and the adsorption filter pool to realize the advanced treatment of antibiotics in the water. In the dosing sedimentation tank, the staff can preferentially adjust the pH value of the wastewater, and then dosing to open the first The output shaft of the motor drives the stirring blades to rotate to form a rapid mixing of wastewater and chemicals. After mixing for a set time, the wastewater is left to stand. Under the action of the chemicals, the harmful substances in the wastewater are gradually separated from the wastewater to form flocs. Then, under the action of the pump, the flocculated and sedimented wastewater is transported to the photocatalytic tank, and the antibiotics in the wastewater are rapidly degraded by cooperating with the aeration tube, and finally the photocatalytic And the aerated water is sent to the adsorption filter tank, and the biological filter bed is set inside the adsorption filter tank. The biological filter bed is composed of gravel layer, pebble layer, slag layer and activated carbon layer. The large specific surface area is conducive to the rapid growth of microorganisms. Growth, using microorganisms to degrade harmful substances such as antibiotics in wastewater, which is environmentally friendly and efficient, and finally the clean water filtered by activated carbon is discharged through the drain. In this way, different degradation methods are used to perform multi-level degradation of wastewater containing antibiotics Treatment, to improve the degradation efficiency of antibiotics while ensuring the quality of treatment.
2、本发明通过设置过滤筒,过滤筒内部的反渗透膜由交联芳香族聚酰胺、聚砜和聚酯无纺布复合而成,对加药沉淀池中水体抽出的过程中,过滤筒的内部形成负压,将外部的水体逐渐通过反渗透膜吸入至内部,通过反渗透膜的过程中,不仅能够对水中杂质进行组合,避免絮凝物通过第一连接管进入至光催化池内部,同时利用聚砜能够对水中的微生物进行初步降解,有效提高整体的抗生素降解效率,在清洁上只需反向开启抽泵,将外部的水反冲至过滤筒内部,即可实现对反渗透膜的清洁,实用性有效得到提高。2. The present invention is provided with a filter cartridge, and the reverse osmosis membrane inside the filter cartridge is composed of cross-linked aromatic polyamide, polysulfone and polyester non-woven fabric. Negative pressure is formed inside, and the external water body is gradually sucked into the interior through the reverse osmosis membrane. During the process of passing through the reverse osmosis membrane, not only can the impurities in the water be combined, but also the flocs can be prevented from entering the photocatalytic pool through the first connecting pipe. At the same time, the use of polysulfone can degrade the microorganisms in the water initially, effectively improving the overall antibiotic degradation efficiency. In terms of cleaning, it is only necessary to turn on the pump in reverse and flush the external water into the filter cartridge to realize the reverse osmosis membrane. The cleanliness and practicability are effectively improved.
3、本发明通过选用In2Ti05纳米带作为光催化剂,进行光催化的过程中开启高压泵灯,逐渐形成光催化反应,由于In2Ti05纳米带的带电性质在中性或者弱碱性水中,对抗生素具有较大的吸附力,配合In2Ti05纳米带具有较大的比表面积,使得对抗生素的降解效果尤为明显,进一步提高了废水中抗生素的处理效率。3. The present invention selects In2Ti05 nanobelts as photocatalysts, turns on the high-pressure pump lamp in the process of photocatalysis, and gradually forms a photocatalytic reaction. Since the charging properties of In2Ti05 nanobelts are in neutral or weakly alkaline water, they have a relatively strong effect on antibiotics. The large adsorption force, combined with the large specific surface area of In2Ti05 nanobelts, makes the degradation effect on antibiotics particularly obvious, and further improves the treatment efficiency of antibiotics in wastewater.
4、本发明通过吸附过滤池的上端所设置有布水管,第二连接管上水泵开启的过程中同步启动第二电机,其输出轴通过传动带带动传动轴进行旋转,进而带动布水管进行转动,经过光催化的水体通过第二连接管进入至布水管,再由布水管上的喷头朝下方碎石层进行喷洒,在离心力的作用下,水体呈散射状分布,能够均匀地覆盖在碎石层的表面,从而提高吸附效率,另外在炉渣层的下方设置布水板,经过生物降解的水体落在布水板上,随后在凹槽上堆积,从流管中再次进入至活性炭层,这一过程能够进一步均化水体,令水体均匀地进入活性炭层,实现过滤,实用性得到进一步提升。4. In the present invention, the upper end of the adsorption filter tank is provided with a water distribution pipe, and the second motor is started synchronously during the opening process of the water pump on the second connecting pipe, and its output shaft drives the transmission shaft to rotate through the transmission belt, and then drives the water distribution pipe to rotate. The photocatalyzed water enters the water distribution pipe through the second connecting pipe, and then the nozzle on the water distribution pipe sprays towards the gravel layer below. Under the action of centrifugal force, the water body is scattered and can evenly cover the gravel layer. surface, so as to improve the adsorption efficiency. In addition, a water distribution board is set under the slag layer. The biodegraded water falls on the water distribution board, then accumulates on the groove, and enters the activated carbon layer again from the flow tube. This process It can further homogenize the water body, so that the water body evenly enters the activated carbon layer to achieve filtration, and the practicability is further improved.
附图说明Description of drawings
图1为本发明的立体图;Fig. 1 is a perspective view of the present invention;
图2为本发明的内部结构示意图;Fig. 2 is a schematic diagram of the internal structure of the present invention;
图3为本发明的过滤筒结构示意图;Fig. 3 is the structural representation of filter cartridge of the present invention;
图4为本发明的图2中A区域局部放大图;Fig. 4 is a partially enlarged view of area A in Fig. 2 of the present invention;
图5为本发明的图2中B区域局部放大图。Fig. 5 is a partially enlarged view of area B in Fig. 2 of the present invention.
图中:1、加药沉淀池;2、光催化池;3、吸附过滤池;4、第一固定板;5、第一电机;6、刮板;7、第一连接管;8、抽泵;9、第二固定板;10、In2Ti05纳米带;11、第二连接管;12、驱动箱;13、布水管;14、碎石层;15、排水口;16、排污口;17、旋转轴;18、搅拌叶片;19、斜壁;20、分割条;21、过滤筒;22、反渗透膜;23、曝气管;24、高压泵灯;25、卵石层;26、炉渣层;27、活性炭层;28、第三固定板;29、传动轴;30、第二电机;31、传动带;32、布水板;33、凹槽;34、流管。In the figure: 1. Dosing sedimentation tank; 2. Photocatalytic tank; 3. Adsorption filter tank; 4. The first fixed plate; 5. The first motor; 6. Scraper; 7. The first connecting pipe; 8. Pumping Pump; 9. Second fixed plate; 10. In2Ti05 nanobelt; 11. Second connecting pipe; 12. Drive box; 13. Water distribution pipe; 14. Gravel layer; 15. Drain outlet; 16. Sewage outlet; Rotary shaft; 18. Stirring blade; 19. Inclined wall; 20. Separation bar; 21. Filter cartridge; 22. Reverse osmosis membrane; 23. Aeration tube; 24. High-pressure pump lamp; 25. Pebble layer; 26.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only a part of the embodiments of the present invention, but not all of the embodiments.
请参阅图1-5,本发明提供的一种实施例:一种具有降解抗生素功能的污水处理池,包括加药沉淀池1,加药沉淀池1的一侧设置有光催化池2,光催化池2的一侧设置有吸附过滤池3,加药沉淀池1的底部设置有斜壁19,加药沉淀池1底部的一侧设置有排污口16,加药沉淀池1内部的一侧安装有过滤筒21,光催化池2的内部设置有In2Ti05纳米带10,且In2Ti05纳米带10与光催化池2通过卡槽限位,光催化池2的底部安装有曝气管23,且曝气管23的一端延伸至光催化池2的外部,吸附过滤池3的内部由上至下依次设置有碎石层14、卵石层25和炉渣层26,吸附过滤池3内部的下端设置有活性炭层27,吸附过滤池3一侧的下端设置有排水口15。Please refer to Fig. 1-5, a kind of embodiment provided by the present invention: a kind of sewage treatment tank with the function of degrading antibiotics, comprises dosing sedimentation tank 1, one side of dosing sedimentation tank 1 is provided with photocatalytic pool 2, photocatalytic tank 2 One side of the catalytic pool 2 is provided with an
进一步,加药沉淀池1和光催化池2之间设置有第一连接管7,且第一连接管7的一端延伸至过滤筒21的内部,第一连接管7的中间位置处安装有抽泵8,过滤筒21的外壁缠卷有反渗透膜22,且反渗透膜22由交联芳香族聚酰胺、聚砜和聚酯无纺布复合而成,利用聚砜能够对水中的微生物进行初步降解,有效提高整体的抗生素降解效率,在清洁上只需反向开启抽泵,将外部的水反冲至过滤筒内部,即可实现对反渗透膜的清洁,实用性有效得到提高。Further, a first connecting
进一步,加药沉淀池1的上端固定设置有第一固定板4,第一固定板4上端面的中间位置处安装有第一电机5,第一电机5的输出轴安装有旋转轴17,且旋转轴17延伸至加药沉淀池1的内部,旋转轴17的下端固定安装有搅拌叶片18,第一电机5带动搅拌叶片18进行转动,令药剂快速与废水进行混合。Further, the upper end of the dosing sedimentation tank 1 is fixedly provided with a first fixed plate 4, a first motor 5 is installed at the middle position of the upper end surface of the first fixed plate 4, and a rotating shaft 17 is installed on the output shaft of the first motor 5, and The rotating shaft 17 extends to the inside of the dosing sedimentation tank 1, and the lower end of the rotating shaft 17 is fixedly equipped with a stirring blade 18, and the first motor 5 drives the stirring blade 18 to rotate, so that the medicine is quickly mixed with the waste water.
进一步,加药沉淀池1的内壁上设置有刮板6,刮板6设置有若干个,且刮板6依次等距设置,刮板6的内部固定设置有分割条20,分割条20与刮板6之间形成缝隙,旋转的废水与刮板6接触时,因撞击产生絮流,从而在加药沉淀池1的内部形成复杂的运动,加速与药剂的快速融合。Further, the inner wall of the dosing sedimentation tank 1 is provided with a scraper 6, and there are several scrapers 6, and the scraper 6 is arranged equidistantly in sequence, and the inside of the scraper 6 is fixedly provided with a dividing
进一步,光催化池2的上端固定设置有第二固定板9,且第二固定板9设置有两个,第二固定板9的下端均安装有高压泵灯24,且高压泵灯24位于In2Ti05纳米带10的上方,In2Ti05纳米带10具有较大的比表面积,使得对抗生素的降解效果尤为明显,进一步提高了废水中抗生素的处理效率。Further, the upper end of the photocatalytic pool 2 is fixedly provided with a second fixed plate 9, and there are two second fixed plates 9, and the lower end of the second fixed plate 9 is equipped with a high-
进一步,吸附过滤池3的上端设置有第三固定板28,第三固定板28的中间位置处设置有驱动箱12,光催化池2与吸附过滤池3之间设置有第二连接管11,第二连接管11的中间位置处安装有水泵。Further, the upper end of the
进一步,驱动箱12的内部固定安装有第二电机30,第二电机30的一侧设置有传动轴29,传动轴29与第三固定板28旋转配合,且第二电机30的输出端与传动轴29通过传动带31传动配合,第二连接管11的一端与传动轴29旋转配合,传动轴29的下端固定安装有布水管13,布水管13的下端设置有五个对称分布的喷嘴,在离心力的作用下,水体呈散射状分布,能够均匀地覆盖在碎石层的表面,从而提高吸附效率。Further, the inside of
进一步,炉渣层26与活性炭层27之间设置有布水板32,且布水板32与吸附过滤池3通过螺栓固定,布水板32的内部设置有若干等距分布的凹槽33,凹槽33的底部均设置有流管34,令水体均匀地进入活性炭层27,实现过滤,实用性得到进一步提升。Further, a
工作原理:使用时,在加药沉淀池1中工作人员可优先调节废水pH值,随后加药开启第一电机5,其输出轴带动搅拌叶片18进行转动,形成废水与药剂的快速混合,混合至设定时间后,静置废水,在与药剂的作用下,废水中有害物质逐渐与废水发生分离,形成絮状物,在斜壁19上堆积沉淀,随后在抽泵8的作用下将经过絮凝沉淀的废水输送至光催化池2,对加药沉淀池1中水体抽出的过程中,过滤筒21的内部形成负压,将外部的水体逐渐通过反渗透膜22吸入至内部,通过反渗透膜22的过程中,不仅能够对水中杂质进行组合,避免絮凝物通过第一连接管7进入至光催化池2内部,同时利用聚砜能够对水中的微生物进行初步降解,通过与曝气管23的互相配合形成对废水中抗生素的快速降解,最后将经过光催化及曝气的水体输送至吸附过滤池3,吸附过滤池3内部设置生物滤床,生物滤床由碎石层14、卵石层25、炉渣层26以及活性炭层27组成,利用较大的比表面积,有利于微生物的快速生长,利用微生物对通过废水中的抗生素等有害物质进行降解,环保且高效,最后经过活性炭过滤的清洁水通过排水口15排出。Working principle: When in use, the staff in the dosing sedimentation tank 1 can give priority to adjusting the pH value of the wastewater, and then turn on the first motor 5 after dosing, and its output shaft drives the stirring blade 18 to rotate, forming a rapid mixing of wastewater and chemicals, mixing After the set time, the waste water is left to stand, and under the action of the chemical, the harmful substances in the waste water are gradually separated from the waste water to form flocs, which accumulate and precipitate on the
对于本领域技术人员而言,显然本发明不限于上述示范性实施例的细节,而且在不背离本发明的精神或基本特征的情况下,能够以其他的具体形式实现本发明。因此,无论从哪一点来看,均应将实施例看作是示范性的,而且是非限制性的,本发明的范围由所附权利要求而不是上述说明限定,因此旨在将落在权利要求的等同要件的含义和范围内的所有变化囊括在本发明内。不应将权利要求中的任何附图标记视为限制所涉及的权利要求。It will be apparent to those skilled in the art that the present invention is not limited to the details of the above-described exemplary embodiments, but that the present invention may be embodied in other specific forms without departing from the spirit or essential characteristics of the invention. Therefore, the embodiments are to be regarded in all respects as illustrative and not restrictive, and the scope of the invention is to be defined by the appended claims rather than the foregoing description, which are therefore intended to fall within the scope of the claims. All changes within the meaning and scope of the equivalents of , are included in the present invention. Any reference signs in the claims shall not be construed as limiting the involved claim.
Claims (8)
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| CN202210060730.5A CN115246695A (en) | 2022-01-19 | 2022-01-19 | Sewage treatment pond with antibiotic function of degradation |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN115974343A (en) * | 2023-03-17 | 2023-04-18 | 四川永沁环境工程有限公司 | Treatment system for sewage containing antibiotics |
| CN116253461A (en) * | 2023-02-23 | 2023-06-13 | 南通华新环保科技股份有限公司 | A multifunctional integrated underground sewage treatment equipment and its treatment method |
| CN119191622A (en) * | 2024-10-25 | 2024-12-27 | 江苏九仁环保科技有限公司 | A photocatalytic reaction device for multi-stage reverse osmosis concentrated brine degradation treatment |
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2022
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116253461A (en) * | 2023-02-23 | 2023-06-13 | 南通华新环保科技股份有限公司 | A multifunctional integrated underground sewage treatment equipment and its treatment method |
| CN115974343A (en) * | 2023-03-17 | 2023-04-18 | 四川永沁环境工程有限公司 | Treatment system for sewage containing antibiotics |
| CN115974343B (en) * | 2023-03-17 | 2023-05-12 | 四川永沁环境工程有限公司 | Treatment system for sewage containing antibiotics |
| CN119191622A (en) * | 2024-10-25 | 2024-12-27 | 江苏九仁环保科技有限公司 | A photocatalytic reaction device for multi-stage reverse osmosis concentrated brine degradation treatment |
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