CN115818854A - Aeration head, aeration equipment and aeration method for generating reinforced micro bubbles - Google Patents
Aeration head, aeration equipment and aeration method for generating reinforced micro bubbles Download PDFInfo
- Publication number
- CN115818854A CN115818854A CN202211639294.3A CN202211639294A CN115818854A CN 115818854 A CN115818854 A CN 115818854A CN 202211639294 A CN202211639294 A CN 202211639294A CN 115818854 A CN115818854 A CN 115818854A
- Authority
- CN
- China
- Prior art keywords
- aeration
- pipe
- air
- water
- gas
- 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.)
- Granted
Links
Images
Classifications
-
- 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
Abstract
Description
技术领域technical field
本发明涉及废水处理领域,具体涉及一种产生强化微气泡的曝气头、曝气设备以及曝气方法。The invention relates to the field of wastewater treatment, in particular to an aeration head for generating enhanced microbubbles, an aeration device and an aeration method.
背景技术Background technique
生物法具有环境友好,去除效率高,对难降解的污染物去除能力强的优点,目前常被用于生活污水、各类工业污水处理中。生物法包括好氧法、厌氧法和生物酶法等,其中,好氧法因具有处理效率高、限制少、应用广泛的优点被应用于各类水体的处理。好氧法的核心是曝气,通过曝气提高废水中的溶解氧含量,进而提高水中微生物的活性,提供分解有机物的条件。曝气过程还可以起到扰动作用,从而使有机物、微生物以及溶解氧充分混合,以便提高去除效率。现有的传统曝气设备一般通过单一的直接鼓气的方式曝气,通过控制孔径大小和鼓风机功率来控制曝气量大小及气泡大小,长时间曝气容易造成部分曝气孔堵塞,污染物在管内部沉积,使得曝气量不均匀且产生的气泡较大,进而导致传质效率低、溶解氧含量低,曝气过程能耗高、效率低,去除效果较差等问题,长时间使用后曝气设备容易老化堵塞,设备使用成本较高。The biological method has the advantages of environmental friendliness, high removal efficiency, and strong ability to remove refractory pollutants. It is currently often used in the treatment of domestic sewage and various industrial sewage. Biological methods include aerobic methods, anaerobic methods, and biological enzyme methods. Among them, aerobic methods are applied to the treatment of various water bodies due to their advantages of high treatment efficiency, less restrictions, and wide application. The core of the aerobic method is aeration, which increases the dissolved oxygen content in wastewater, thereby increasing the activity of microorganisms in the water and providing conditions for decomposing organic matter. The aeration process can also act as a disturbance, so that the organic matter, microorganisms, and dissolved oxygen are well mixed to improve the removal efficiency. Existing traditional aeration equipment generally aerates through a single direct air blowing method, and controls the size of the aeration volume and the size of the bubbles by controlling the size of the aperture and the power of the blower. Long-term aeration may easily cause some aeration holes to be blocked, and pollutants Deposition inside the tube makes the aeration amount uneven and the bubbles generated are large, which leads to low mass transfer efficiency, low dissolved oxygen content, high energy consumption, low efficiency, and poor removal effect during the aeration process. Long-term use Post-aeration equipment is prone to aging and clogging, and the cost of equipment use is relatively high.
相较于鼓风曝气产生的普通气泡,通过气溶释气法产生的微气泡则具有比表面积大、停留时间长、传质效率高、曝气均匀、富含强氧化性的自由基等优点。但是,通过单一的气溶释气方式产生的微气泡量小,不能高效地产生足量的微气泡。Compared with the ordinary bubbles produced by blast aeration, the microbubbles produced by the aerosol release method have large specific surface area, long residence time, high mass transfer efficiency, uniform aeration, and rich in strong oxidizing free radicals, etc. advantage. However, the amount of microbubbles generated by a single air-dissolving and degassing method is small, and a sufficient amount of microbubbles cannot be efficiently generated.
另一方面,现有曝气设备智能化程度较低,曝气过程需要人工进行监测并操作控制曝气设备来调整曝气量,该过程耗费大量人力。On the other hand, the existing aeration equipment has a low degree of intelligence, and the aeration process requires manual monitoring and operation and control of the aeration equipment to adjust the aeration volume, which consumes a lot of manpower.
发明内容Contents of the invention
发明目的:本发明所要解决的技术问题是针对现有技术的不足,提供一种产生强化微气泡的曝气头。Purpose of the invention: The technical problem to be solved by the present invention is to provide an aeration head for generating enhanced microbubbles for the deficiencies of the prior art.
为了解决上述技术问题,本发明提供了一种产生强化微气泡的曝气头,该曝气头包括用于进入外部气体的曝气分管、用于进入气溶水的气水分管、曝气膜片、内层微气泡产生腔、外层曝气腔以及调节机构。内层微气泡产生腔,用于接收来自所述气水分管的气溶水并将所述气溶水通过气溶释气法产生微气泡,所述微气泡通过所述曝气膜片排出。外层曝气腔,用于接收来自曝气分管的气体并将所述气体通过所述曝气膜片排出。所述调节机构,用于调节从所述外层曝气腔流通至所述内层微气泡产生腔的气体的量。In order to solve the above technical problems, the present invention provides an aeration head for generating enhanced microbubbles, the aeration head includes an aeration branch pipe for entering external air, a gas moisture pipe for entering aerosol water, and an aeration membrane A sheet, an inner microbubble generating chamber, an outer aeration chamber and an adjustment mechanism. The inner microbubble generation chamber is used to receive the aerosolized water from the air-moisture pipe and generate microbubbles from the aerosolized water through the aerosol release method, and the microbubbles are discharged through the aeration membrane. The outer aeration chamber is used to receive the gas from the aeration branch pipe and discharge the gas through the aeration membrane. The adjustment mechanism is used to adjust the amount of gas flowing from the outer aeration chamber to the inner microbubble generation chamber.
在一些实施例中,该曝气头包括内部支撑件以及混合曝气管道。所述内部支撑件固定安装于所述曝气头内部。所述混合曝气管道贯穿内部支撑件。内部支撑件与混合曝气管道将曝气头内部分隔形成内层微气泡产生腔和外层曝气腔。混合曝气管道的侧壁上开设有用于连通内层微气泡产生腔和外层曝气腔的流通口。所述调节机构包括一个活动套设于混合曝气管道外侧用于封堵所述流通口的活动外管,所述活动外管能够沿混合曝气管道往复移动,用于调节活动外管的下部遮挡流通口的面积。In some embodiments, the aeration head includes an internal support and a mixing aeration tube. The internal support member is fixedly installed inside the aeration head. The mixing and aeration pipe runs through the inner support. The internal support and the mixed aeration pipe separate the interior of the aeration head to form an inner microbubble generation chamber and an outer aeration chamber. The side wall of the mixed aeration pipe is provided with a flow port for communicating with the microbubble generation chamber of the inner layer and the aeration chamber of the outer layer. The adjustment mechanism includes a movable outer tube that is movably sleeved on the outside of the mixed aeration pipeline to block the flow opening, and the movable outer tube can move back and forth along the mixed aeration pipeline to adjust the lower part of the movable outer tube Cover the area of the flow opening.
在一些实施例中,所述调节机构还包括挡板和回复弹簧,所述挡板安装于所述活动外管的下部,所述曝气分管输出的气体朝向挡板的下部。所述回复弹簧位于所述混合曝气管道与所述内部支撑件之间,所述活动外管通过所述回复弹簧连接所述内部支撑件。当增加所述曝气分管输出的气体量时,所述曝气分管输出的气体施加在所述挡板上的压力增大,活动外管在气体压力作用下沿所述混合曝气管道朝向所述曝气膜片运动并压缩回复弹簧。当减小所述曝气分管输出的气体量时,所述曝气分管输出的气体施加在所述挡板上的压力减小,所述活动外管在所述回复弹簧的回弹力下向远离所述曝气膜片的方向运动。当所述曝气分管输出的气体施加在所述挡板上的压力与所述回复弹簧施加在活动外管上的回弹力相平衡时,所述活动外管处于一个稳定的位置。In some embodiments, the adjustment mechanism further includes a baffle and a return spring, the baffle is installed on the lower part of the movable outer tube, and the gas output by the aeration branch pipe is directed to the lower part of the baffle. The return spring is located between the mixing aeration pipe and the inner support, and the movable outer tube is connected to the inner support through the return spring. When the amount of gas output by the aeration branch pipe is increased, the pressure exerted on the baffle by the gas output by the aeration branch pipe increases, and the movable outer pipe moves along the mixed aeration pipe toward the The aeration diaphragm moves and compresses the return spring. When the amount of gas output by the aeration branch pipe is reduced, the pressure exerted on the baffle by the gas output by the aeration branch pipe decreases, and the movable outer pipe moves away from the direction movement of the aeration membrane. When the pressure exerted on the baffle by the gas output by the aeration branch pipe is in balance with the rebound force exerted by the return spring on the movable outer pipe, the movable outer pipe is in a stable position.
由此,本申请通过连续调节曝气分管输出的气体的量,能够连续调节活动外管的下部遮挡流通口的面积。Thus, the present application can continuously adjust the area of the flow opening blocked by the lower part of the movable outer pipe by continuously adjusting the amount of gas output by the aeration branch pipe.
在一些实施例中,该曝气头还包括反冲洗管道,所述反冲洗管道的一端穿过所述外层曝气腔和所述内部支撑件并延伸至所述活动外管的外侧壁,所述活动外管的侧壁上开设有外管反冲洗孔,所述混合曝气管道的侧壁上开设有内管反冲洗孔。当所述曝气分管输出的气体量至最大值时,所述活动外管向上移动至所述回复弹簧完全压缩的位置,所述内管反冲洗孔、所述外管反冲洗孔以及所述反冲洗管道依次连通。In some embodiments, the aeration head further includes a backwashing pipe, one end of the backwashing pipe passes through the outer aeration chamber and the inner support and extends to the outer wall of the movable outer pipe, Outer pipe backwashing holes are opened on the side wall of the movable outer pipe, and inner pipe backwashing holes are opened on the side wall of the mixed aeration pipe. When the amount of gas output by the aeration branch pipe reaches the maximum value, the movable outer pipe moves upward to the position where the return spring is fully compressed, and the backwash hole of the inner pipe, the backwash hole of the outer pipe and the backwash hole of the outer pipe The backwashing pipelines are connected in sequence.
在一些实施例中,所述曝气膜片为双层曝气膜片,所述双层曝气膜片的两层膜片上的微孔位置相互交错。In some embodiments, the aeration membrane is a double-layer aeration membrane, and the positions of micropores on the two membranes of the double-layer aeration membrane are interlaced.
在一些实施例中,所述混合曝气管道通过减压孔连通所述气水分管,来自所述气水分管的气溶水通过所述减压孔向混合曝气管道释放微气泡;所述减压孔位于所述流通口的下方。In some embodiments, the mixed aeration pipeline communicates with the gas-moisture pipe through a decompression hole, and the aerosolized water from the gas-moisture pipe releases microbubbles to the mixed aeration pipeline through the decompression hole; The decompression hole is located below the flow port.
本发明还提供一种产生强化微气泡的曝气设备,该曝气设备包括上述的一种产生强化微气泡的曝气头、双吸泵、溶气罐、气泵、布水管、布气管、溶氧仪以及控制器,所述一个以上的曝气头位于曝气池内的水体底部。所述双吸泵设置有第一进水口、第二进水口以及出水口,所述双吸泵用于将外部气体从双吸泵的第一进水口泵送至双吸泵的出水口以及将曝气池内的水体上部池水从双吸泵的第二进水口泵送至双吸泵的出水口,以这种方式形成气水出水。所述溶气罐的输入端与所述双吸泵的出水口连通,用于接收所述气水出水,所述溶气罐的输出端通过布水管与各曝气头的气水分管连通,用于来自溶气罐的输出端的气溶水输送至各曝气头。所述气泵用于将外部气体从气泵的进气口泵送至气泵的出气口,所述气泵的出气口通过布气管与各曝气头的曝气分管连通。所述溶氧仪位于曝气池的水体内,用于监测曝气池的水体内的溶解氧含量。所述双吸泵、所述气泵以及所述溶氧仪分别都与所述控制器电连接,所述控制器基于来自所述溶氧仪的测量值来控制所述双吸泵的启停、所述气泵的启停以及气泵的进气量。The present invention also provides an aeration device for generating enhanced micro-bubbles, the aeration device includes the above-mentioned aeration head for generating enhanced micro-bubbles, a double-suction pump, an air dissolving tank, an air pump, a water distribution pipe, an air distribution pipe, a dissolving An oxygen meter and a controller, the more than one aeration heads are located at the bottom of the water body in the aeration tank. The double-suction pump is provided with a first water inlet, a second water inlet and a water outlet, and the double-suction pump is used to pump external air from the first water inlet of the double-suction pump to the water outlet of the double-suction pump and to The water in the upper part of the water body in the aeration tank is pumped from the second water inlet of the double-suction pump to the water outlet of the double-suction pump to form air-water outlet in this way. The input end of the dissolved air tank communicates with the water outlet of the double suction pump for receiving the air and water outlet, and the output end of the dissolved air tank communicates with the air and water pipes of each aeration head through the water distribution pipe. The aerosolized water from the outlet of the aerosol tank is delivered to each aeration head. The air pump is used to pump external air from the air inlet of the air pump to the air outlet of the air pump, and the air outlet of the air pump communicates with the aeration branch pipes of each aeration head through the air distribution pipe. The dissolved oxygen meter is located in the water body of the aeration tank and is used for monitoring the dissolved oxygen content in the water body of the aeration tank. The double-suction pump, the air pump and the dissolved oxygen meter are all electrically connected to the controller, and the controller controls the start and stop of the double-suction pump based on the measured value from the dissolved oxygen meter. The start and stop of the air pump and the intake air volume of the air pump.
在一些实施例中,该曝气设备还包括过滤器和第一管路,所述过滤器位于曝气池内的水体上部,所述双吸泵的第二进水口通过所述第一管路与所述过滤器连通。In some embodiments, the aeration equipment also includes a filter and a first pipeline, the filter is located on the upper part of the water body in the aeration tank, and the second water inlet of the double-suction pump passes through the first pipeline and the first pipeline. The filter communicates.
在一些实施例中,该曝气设备还包括第一进气管、第二进气管以及止回阀,所述双吸泵的第一进水口通过所述第一进气管与外部气体连通。所述气泵的进气口通过第二进气管与外部气体连通。所述第一止回阀位于所述第一管路上。In some embodiments, the aeration device further includes a first air inlet pipe, a second air inlet pipe and a check valve, and the first water inlet of the double-suction pump communicates with the outside air through the first air inlet pipe. The air inlet of the air pump communicates with the outside air through the second air inlet pipe. The first check valve is located on the first pipeline.
本发明提供了一种产生强化微气泡的曝气方法,该方法通过使用上述的一种产生强化微气泡的曝气设备来实施,包括以下步骤:The present invention provides an aeration method for generating enhanced microbubbles, which is implemented by using the above-mentioned aeration device for generating enhanced microbubbles, comprising the following steps:
开启双吸泵,外部气体和曝气池内的水体上部池水经所述双吸泵形成气水出水。所述气水出水经所述溶气罐形成气溶水。所述曝气头的气水分管接收所述气溶水,所述气溶水通过曝气头的减压孔形成微气泡。所述微气泡依次经由所述内层微气泡产生腔以及所述曝气膜片进入曝气池内的水体中,用于增加水体中的溶解氧含量。Turn on the double-suction pump, the external air and the upper pool water of the water body in the aeration tank pass through the double-suction pump to form gas-water outlet. The gas-water effluent passes through the gas-dissolving tank to form gas-soluble water. The air-moisture pipe of the aeration head receives the aerosolized water, and the aerosolized water passes through the decompression holes of the aeration head to form microbubbles. The microbubbles enter the water body in the aeration tank sequentially through the inner microbubble generating chamber and the aeration membrane to increase the dissolved oxygen content in the water body.
开启气泵,外部气体被泵送至所述曝气头的曝气分管,所述曝气头的曝气分管输出的气体朝向挡板下部。通过调节气泵的进气量来调节活动外管的下部遮挡流通口的面积,以便调节从外层曝气腔流通至所述内层微气泡产生腔的气体量,包括:当增大气泵的进气量时,曝气分管输出的气体借助挡板带动活动外管沿混合曝气管道向上移动,减小活动外管的下部遮挡流通口的面积,用于增加从外层曝气腔流通至所述内层微气泡产生腔的气体量。当减小气泵的进气量时,曝气分管输出的气体借助挡板带动活动外管沿混合曝气管道向下移动,增大活动外管的下部遮挡流通口的面积,用于减少从外层曝气腔流通至所述内层微气泡产生腔的气体量。所述从外层曝气腔流通至所述内层微气泡产生腔的气体搅动所述内层微气泡产生腔产生更多的微气泡,通过调节气泵的进气量来调节内层微气泡产生腔内的微气泡的量。The air pump is turned on, and the external air is pumped to the aeration sub-pipe of the aeration head, and the gas output by the aeration sub-pipe of the aeration head is toward the lower part of the baffle. By adjusting the air intake of the air pump, the area of the lower part of the movable outer tube is occluded, so as to adjust the amount of gas flowing from the outer aeration chamber to the inner microbubble generation chamber, including: when increasing the intake of the air pump When the air volume is high, the gas output by the aeration branch pipe drives the movable outer pipe to move upward along the mixed aeration pipe with the help of the baffle, reducing the area where the lower part of the movable outer pipe blocks the flow opening, and is used to increase the flow from the outer aeration chamber to the The gas volume of the microbubble generation chamber in the inner layer. When the air intake volume of the air pump is reduced, the gas output from the aeration branch pipe drives the movable outer pipe to move downward along the mixed aeration pipe with the help of the baffle, increasing the area of the lower part of the movable outer pipe to block the flow opening, which is used to reduce the flow rate from the outside. The amount of gas that flows from the layer aeration chamber to the inner layer microbubble generation chamber. The gas flowing from the outer layer aeration chamber to the inner layer microbubble generation chamber stirs the inner layer microbubble generation chamber to generate more microbubbles, and the generation of inner layer microbubbles is adjusted by adjusting the air intake of the air pump The amount of microbubbles in the cavity.
进一步,本发明提供的一种产生强化微气泡的曝气方法还包括以下步骤:Further, an aeration method for generating enhanced microbubbles provided by the present invention also includes the following steps:
开启双吸泵和气泵并调节气泵的进气量至最大值,所述活动外管向上移动至回复弹簧完全压缩的位置,所述内管反冲洗孔、外管反冲洗孔以及所述反冲洗管道依次连通。控制双吸泵在开启状态和停止状态之间切换,由曝气头的减压孔喷出的微气泡和从外层曝气腔流通至所述内层微气泡产生腔的气体混合后冲击所述内层微气泡产生腔的内壁。裹挟有所述内层微气泡产生腔内壁污染物的气水混合物由所述反冲洗管道排出。Turn on the double-suction pump and the air pump and adjust the intake air volume of the air pump to the maximum value, the movable outer pipe moves upward to the position where the return spring is fully compressed, the backwash hole of the inner pipe, the backwash hole of the outer pipe and the backwash The pipes are connected sequentially. Control the double-suction pump to switch between the open state and the stop state, and the microbubbles ejected from the decompression hole of the aeration head and the gas flowing from the outer aeration chamber to the inner microbubble generation chamber are mixed and then impacted. The inner wall of the inner microbubble generation chamber. The air-water mixture entrained with the pollutants on the inner wall of the inner microbubble generation chamber is discharged from the backwashing pipeline.
有益效果:Beneficial effect:
(1)本发明的曝气头通过设置外层曝气腔连通曝气分管与曝气膜片,从而允许外层曝气腔进行直接曝气;通过设置气水分管连通内层微气泡产生腔与曝气膜片,从而允许内层微气泡产生腔进行气溶释气法曝气;通过设置调节机构来调节从外层曝气腔流通至所述内层微气泡产生腔的气体的量,当外层曝气腔与内层微气泡产生腔连通,从曝气分管流通至内层微气泡产生腔的气体扰动内层微气泡产生腔,从而使内层微气泡产生腔内产生更多的微气泡,增加内层微气泡产生腔内气水混合物的气水比。相较于单一的溶气释气法,本申请的曝气头产生更多的微气泡;相较于单一的直接曝气法,本申请的曝气头产生足量的微气泡,解决了目前溶气释气过程曝气量小,直接曝气法产生气泡较大从而导致气泡传质差、溶解氧效果差的问题。(1) The aeration head of the present invention connects the aeration branch pipe and the aeration diaphragm by setting the outer layer aeration chamber, thereby allowing the outer layer aeration chamber to carry out direct aeration; by setting the gas moisture pipe to connect the inner layer microbubble generation chamber and the aeration diaphragm, so as to allow the inner layer microbubble generation chamber to perform aeration by aerosol release method; by setting the adjustment mechanism to adjust the amount of gas flowing from the outer layer aeration chamber to the inner layer microbubble generation chamber, When the outer layer aeration chamber is connected with the inner layer microbubble generation chamber, the gas flowing from the aeration branch pipe to the inner layer microbubble generation chamber disturbs the inner layer microbubble generation chamber, so that more microbubble generation chambers are generated in the inner layer Micro-bubbles increase the gas-water ratio of the gas-water mixture in the cavity generated by the micro-bubbles in the inner layer. Compared with a single method of dissolving air and degassing, the aeration head of this application produces more microbubbles; compared with a single direct aeration method, the aeration head of this application produces a sufficient amount of microbubbles, which solves the current problem The amount of aeration in the dissolved air release process is small, and the direct aeration method produces large bubbles, which leads to poor mass transfer of the bubbles and poor dissolved oxygen effect.
(2)本申请的一些实施例通过内部支撑件与混合曝气管道将曝气头内部分隔形成内层微气泡产生腔和外层曝气腔,并在混合曝气管道的侧壁上开设用于连通内层微气泡产生腔和外层曝气腔的流通口,通过设置一个活动套设于混合曝气管道外侧用于封堵所述流通口的活动外管,该活动外管能够沿混合曝气管道往复移动,以便调节活动外管的下部遮挡流通口的面积,进而调节从外层曝气腔流通至所述内层微气泡产生腔的气体的量,从而允许调节内层微气泡产生腔内产生的微气泡的量。(2) In some embodiments of the present application, the interior of the aeration head is separated by an internal support member and a mixed aeration pipe to form an inner layer microbubble generation chamber and an outer layer aeration chamber, and the side wall of the mixed aeration pipe is opened for use. In order to communicate with the flow port of the inner layer microbubble generation chamber and the outer layer aeration chamber, a movable outer tube is provided to block the flow port by setting a movable sleeve on the outside of the mixing aeration pipe, and the movable outer tube can move along the mixing The aeration pipe moves back and forth in order to adjust the area of the flow opening blocked by the lower part of the movable outer pipe, thereby adjusting the amount of gas flowing from the outer aeration chamber to the inner microbubble generation chamber, thereby allowing the adjustment of the inner microbubble generation The amount of microbubbles generated in the cavity.
(3)本申请的一些实施例通过在活动外管下部设置挡板,并使曝气分管输出的气体朝向该挡板下部,以便借助曝气分管输出的气体对挡板的压力,带动活动外管沿混合曝气管道移动;通过设置在混合曝气管道与内部支撑件之间设置回复弹簧,该回复弹簧连接活动外管和内部支撑件;当增加所述曝气分管输出的气体量时,所述曝气分管输出的气体施加在所述挡板上的压力增大,活动外管在气体压力作用下沿所述混合曝气管道朝向所述曝气膜片运动并压缩回复弹簧;当减小所述曝气分管输出的气体量时,所述曝气分管输出的气体施加在所述挡板上的压力减小,所述活动外管在所述回复弹簧的回弹力下向远离所述曝气膜片的方向运动;当曝气分管输出的气体施加在挡板上的力与回复弹簧施加在活动外管上的力平衡时,活动外管的位置稳定。本实施例的调节机构借助曝气分管输出的气体来控制活动外管沿混合曝气管道的位移量,即控制活动外管的下部遮挡流通口的面积大小,从而调节曝气分管输出的气体流通至内层微气泡产生腔的量,进而调节内层微气泡产生腔中微气泡的产生量。(3) In some embodiments of the present application, a baffle is provided at the lower part of the movable outer pipe, and the gas output by the aeration branch is directed toward the lower part of the baffle, so that the pressure of the gas output by the aeration branch on the baffle can drive the movable outer The pipe moves along the mixed aeration pipe; by setting a return spring between the mixed aeration pipe and the internal support, the return spring connects the movable outer pipe and the internal support; when increasing the amount of gas output by the aeration branch pipe, The pressure of the gas output by the aeration branch pipe on the baffle increases, and the movable outer tube moves toward the aeration diaphragm along the mixed aeration pipe under the action of the gas pressure and compresses the return spring; When the amount of gas output by the aeration branch pipe is small, the pressure exerted on the baffle by the gas output by the aeration branch pipe decreases, and the movable outer pipe moves away from the The direction of the aeration diaphragm moves; when the force exerted on the baffle by the gas output by the aeration branch pipe is balanced with the force exerted on the movable outer pipe by the return spring, the position of the movable outer pipe is stable. The adjustment mechanism of this embodiment controls the displacement of the movable outer pipe along the mixed aeration pipeline by means of the gas output by the aeration branch pipe, that is, controls the area of the flow opening blocked by the lower part of the movable outer pipe, thereby adjusting the gas flow output by the aeration branch pipe to the amount of the microbubble generation chamber in the inner layer, and then adjust the generation amount of microbubbles in the microbubble generation chamber in the inner layer.
(4)本申请的一些实施例的曝气膜片采用双层曝气膜片,双层曝气膜片的两层膜片上的微孔位置相互交错;当曝气头处于非工作状态时,双层曝气膜片的两层膜片依靠自身弹性贴合,以使外部污水、污泥等杂质无法进入曝气头内部;当曝气头处于工作状态时,双层曝气膜片的两层膜片分隔,以便曝气头内部的物质能从微孔排出。(4) The aeration membrane of some embodiments of the present application adopts a double-layer aeration membrane, and the micropore positions on the two-layer membrane of the double-layer aeration membrane are interlaced; when the aeration head is in a non-working state , the two-layer diaphragm of the double-layer aeration diaphragm relies on its own elasticity to fit, so that impurities such as external sewage and sludge cannot enter the interior of the aeration head; when the aeration head is in working condition, the double-layer aeration diaphragm The two layers of membranes are separated so that the substances inside the aerator head can be discharged from the micropores.
(5)本申请的一些实施例通过设置贯穿外层曝气腔和内部支撑件的反冲洗管道、开设在活动外管的侧壁上的外管反冲洗孔以及开设在混合曝气管道的侧壁上的内管反冲洗孔,当增加曝气分管输出的气体量至最大值时,回复弹簧处于完全压缩的位置,内管反冲洗孔、外管反冲洗孔以及反冲洗管道依次连通;从曝气分管流通至内层微气泡产生腔中的大量气体与内层微气泡产生腔内的气水混合物混合后冲击内层微气泡产生腔的内壁并裹挟来自内层微气泡产生腔的内壁的污泥、微生物等附着物;当曝气分管输出的气体量至最大输出值时,内层微气泡产生腔内部压力大于外部水压,同时由于曝气膜片对气水混合物的排出存在阻力,在内部压力的作用下,裹挟有污泥、微生物等附着物的气水混合物依次经由内管反冲洗孔、外管反冲洗孔以及反冲洗管道排出;通过间歇地向气水分管供入气溶水的方式对内层微气泡产生腔内部形成扰动,从而使得污泥、微生物等附着物更容易随着气水混合物排出至水体中。通过以上过程,本申请的曝气头实现了反向冲洗清洁功能。(5) In some embodiments of the present application, the backwashing pipe that runs through the outer layer aeration chamber and the internal support, the backwashing hole of the outer pipe provided on the side wall of the movable outer pipe, and the sidewall of the mixed aeration pipe are provided. The backwash hole of the inner tube on the wall, when the gas volume output by the aeration branch pipe is increased to the maximum value, the return spring is in a fully compressed position, and the backwash hole of the inner tube, the backwash hole of the outer tube and the backwash pipe are connected in sequence; A large amount of gas flowing through the aeration branch pipe into the inner microbubble generation chamber mixes with the gas-water mixture in the inner layer microbubble generation chamber, then impacts the inner wall of the inner layer microbubble generation chamber and entrains the air from the inner wall of the inner layer microbubble generation chamber Attachments such as sludge and microorganisms; when the gas volume output by the aeration branch pipe reaches the maximum output value, the internal pressure of the microbubble generation chamber in the inner layer is greater than the external water pressure, and because the aeration diaphragm has resistance to the discharge of the gas-water mixture, Under the action of internal pressure, the air-water mixture entrained with sludge, microorganisms and other attachments is discharged through the backwash hole of the inner pipe, the backwash hole of the outer pipe and the backwash pipe in sequence; The way of water creates disturbances inside the microbubble generation cavity in the inner layer, making it easier for sludge, microorganisms and other attachments to be discharged into the water body along with the air-water mixture. Through the above process, the aeration head of the present application realizes the function of back flushing and cleaning.
(6)本申请能够通过控制气水分管是否向内层微气泡产生腔输入溶气水、曝气分管是否向外层曝气腔输送外部气体以及调节向外层曝气腔输送的外部气体的量来调节本申请的曝气头的曝气模式;当气水分管向内层微气泡产生腔输入溶气水、曝气分管不向外层曝气腔输送外部气体时,该曝气头处于气溶释气模式;当气水分管不向内层微气泡产生腔输入溶气水、曝气分管向外层曝气腔输送外部气体时,该曝气头处于直接曝气模式;当气水分管向内层微气泡产生腔输入溶气水、曝气分管向外层曝气腔输送外部气体但未输送最大气体量时,该曝气头处于混合曝气模式;当曝气分管向外层曝气腔输送外部气体且输出最大气体量、气水分管向内层微气泡产生腔间断地输入溶气水时,该曝气头处于反向冲洗模式。(6) This application can control whether the air-moisture pipe feeds dissolved air water into the inner microbubble generation chamber, whether the aeration branch pipe delivers external air to the outer aeration chamber, and adjusts the amount of external gas delivered to the outer aeration chamber. Adjust the aeration mode of the aeration head of this application; when the gas moisture pipe inputs dissolved air water to the inner microbubble generation chamber, and the aeration branch pipe does not deliver external air to the outer aeration chamber, the aeration head is in the Aerosol release mode; when the gas water pipe does not input dissolved air water to the inner microbubble generation chamber, and the aeration branch pipe delivers external air to the outer aeration chamber, the aeration head is in the direct aeration mode; when the air water When the sub-pipe supplies dissolved air water to the inner micro-bubble generation chamber, and the aeration sub-pipe delivers external air to the outer aeration chamber but does not deliver the maximum amount of gas, the aeration head is in the mixed aeration mode; When the aeration chamber transports external air and outputs the maximum amount of gas, and the gas-moisture pipe intermittently inputs dissolved air water to the inner microbubble generation chamber, the aeration head is in the reverse flushing mode.
(7)本申请提供的曝气设备能够通过控制器基于来自溶氧仪的测量值来控制双吸泵的启停、气泵的启停以及气泵的进气量,进而调节该曝气设备的曝气模式:当控制器控制双吸泵启动、气泵停用时,该曝气设备处于气溶释气模式;当控制器控制双吸泵停用、气泵启用且未输出最大气体量时,该曝气设备处于直接曝气模式;当控制器控制双吸泵启用、气泵启用且未输出最大气体量时,该曝气设备处于混合曝气模式;当控制器控制气泵启用且输出最大气体量、双吸泵在启用与停用之间切换时,该曝气设备处于反向冲洗模式;一方面,本申请的曝气设备可以提升微气泡的曝气量,弥补溶气释气法可能存在的微气泡曝气量不足的缺点;另一方面可以根据曝气池内溶解氧含量的变化,改变曝气模式,优化曝气过程,节省能耗。(7) The aeration equipment provided by this application can control the start and stop of the double-suction pump, the start and stop of the air pump, and the air intake of the air pump through the controller based on the measured value from the dissolved oxygen meter, and then adjust the aeration of the aeration equipment. Gas mode: When the controller controls the double-suction pump to start and the air pump to stop, the aeration equipment is in the aerosol release mode; The aeration equipment is in the direct aeration mode; when the controller controls the activation of the double suction pump, the air pump is enabled and the maximum gas volume is not output, the aeration equipment is in the mixed aeration mode; When the suction pump is switched between activation and deactivation, the aeration equipment is in the reverse flushing mode; The disadvantage of insufficient air bubble aeration; on the other hand, according to the change of dissolved oxygen content in the aeration tank, the aeration mode can be changed, the aeration process can be optimized, and energy consumption can be saved.
(8)本申请的曝气设备通过设置控制器基于来自溶氧仪的测量值来控制双吸泵的启停、气泵的启停以及气泵的进气量,减少人力操作,同时通过溶氧仪能够实时监测水中溶氧情况。(8) The aeration equipment of the present application controls the start and stop of the double-suction pump, the start and stop of the air pump, and the air intake of the air pump based on the measured value from the dissolved oxygen meter by setting the controller, thereby reducing manpower operations, and simultaneously passing the dissolved oxygen meter It can monitor the dissolved oxygen in water in real time.
(9)本申请的曝气设备通过双吸泵将外部气体从双吸泵的第一进水口泵送至双吸泵的出水口以及将曝气池内的水体上部池水从双吸泵的第二进水口泵送至双吸泵的出水口,以这种方式形成气水出水,该气水出水通过溶气释气过程重新回到曝气池底部,从而实现污水回流,形成外部循环过程,延长水处理过程的停留时间。(9) The aeration equipment of the present application pumps the external air from the first water inlet of the double-suction pump to the water outlet of the double-suction pump through the double-suction pump and pumps the water in the upper part of the water body in the aeration tank from the second water inlet of the double-suction pump. The water inlet is pumped to the outlet of the double-suction pump, in this way, the air-water outlet is formed, and the air-water outlet returns to the bottom of the aeration tank through the process of dissolved air and degassing, so as to realize the return of sewage and form an external circulation process, extending the The residence time of the water treatment process.
附图说明Description of drawings
下面结合附图和具体实施方式对本发明做更进一步的具体说明,本发明的上述和/或其他方面的优点将会变得更加清楚。The advantages of the above and/or other aspects of the present invention will become clearer as the present invention will be further described in detail in conjunction with the accompanying drawings and specific embodiments.
图1为本发明的一个实施例提供的一种产生强化微气泡的曝气头的立体示意图一;Fig. 1 is a three-dimensional schematic diagram 1 of an aeration head for generating enhanced microbubbles provided by an embodiment of the present invention;
图2为图1所示的曝气头的俯视图;Fig. 2 is a top view of the aeration head shown in Fig. 1;
图3为图1所示的曝气头的立体示意图二;Fig. 3 is a perspective view II of the aeration head shown in Fig. 1;
图4为图1所示的曝气头的剖视图;Fig. 4 is a sectional view of the aeration head shown in Fig. 1;
图5为图1所示的曝气头内部的结构示意图;Fig. 5 is a schematic diagram of the internal structure of the aeration head shown in Fig. 1;
图6为采用图1所示的曝气头的曝气设备的结构示意图。Fig. 6 is a schematic structural diagram of an aeration device using the aeration head shown in Fig. 1 .
具体实施方式Detailed ways
本发明的附图标记如下所示:The reference signs of the present invention are as follows:
曝气池000,曝气头100、曝气分管110、气水分管120、曝气膜片130、曝气头壳体140、内部支撑件150、反冲洗管道151、混合曝气管道160、减压孔161、流通口162、内管反冲洗孔163、内部腔室170、内层微气泡产生腔171、外层曝气腔172、外管反冲洗孔183、调节机构190、挡板191、回复弹簧192、活动外管193、双吸泵200、第一进水口210、第二进水口220、出水口230、第一进气管240、溶气罐300、输入端310、输出端320、气泵400、进气口410、出气口420、第二进气管430、布水管500、布气管600、溶氧仪700、控制器800、过滤器900、第一管路910、第一止回阀920。
下面结合附图对本申请的技术方案进行详细的阐述。The technical solution of the present application will be described in detail below in conjunction with the accompanying drawings.
单一的直接鼓气方式通过控制孔径大小和鼓风机功率来控制曝气量大小及气泡大小。由于受到孔径大小的影响,单一的直接鼓气方式产生的气泡较大,并且经过长时间曝气后,部分孔洞容易被堵,气体无法覆盖整个曝气头顶部,导致曝气量不均匀,进而导致传质效率低、溶解氧含量低,曝气过程能耗高、效率低,去除效果较差等问题。相较于鼓风曝气产生的普通气泡,通过气溶释气法产生的微气泡则具有比表面积大、停留时间长、传质效率高、曝气均匀、富含强氧化性的自由基等优点。但是,因为溶气释气法需加压将气体溶于水中,整个过程不连续,导致通过单一的气溶释气方式产生的微气泡量小,不能高效地产生足量的微气泡。The single direct aeration method controls the aeration volume and bubble size by controlling the aperture size and blower power. Due to the influence of pore size, the bubbles generated by a single direct aeration method are relatively large, and after a long time of aeration, some pores are easily blocked, and the gas cannot cover the entire top of the aeration head, resulting in uneven aeration volume, and then It leads to problems such as low mass transfer efficiency, low dissolved oxygen content, high energy consumption, low efficiency, and poor removal effect during the aeration process. Compared with the ordinary bubbles produced by blast aeration, the microbubbles produced by the aerosol release method have large specific surface area, long residence time, high mass transfer efficiency, uniform aeration, and rich in strong oxidizing free radicals, etc. advantage. However, because the gas dissolution and release method needs to be pressurized to dissolve the gas in water, the whole process is discontinuous, resulting in a small amount of microbubbles generated by a single method of gas dissolution and degassing, which cannot efficiently generate a sufficient amount of microbubbles.
如图1至图4所示,本申请提供了一种产生强化微气泡的曝气头,该曝气头100可以安装于曝气池000内的水体底部。该曝气头100整体呈花洒状,外壁弧度为90°至145°。该曝气头100包括用于进入外部气体的曝气分管110、用于进入气溶水的气水分管120、曝气膜片130、内层微气泡产生腔171、外层曝气腔172以及调节机构190。内层微气泡产生腔171,用于接收来自气水分管120的气溶水并将所述气溶水通过气溶释气法产生微气泡,微气泡通过曝气膜片130排出。外层曝气腔172,用于接收来自曝气分管110的气体并将所述气体通过曝气膜片130排出。调节机构190,用于调节从外层曝气腔172流通至内层微气泡产生腔171的气体的量。在本申请中,所述外部气体可以是外部空气。As shown in FIGS. 1 to 4 , the present application provides an aeration head for generating enhanced microbubbles. The
本发明的曝气头通过设置外层曝气腔172连通曝气分管110与曝气膜片130,从而允许外层曝气腔172进行直接曝气。通过设置气水分管120连通内层微气泡产生腔171与曝气膜片130,从而允许内层微气泡产生腔171进行气溶释气法曝气。通过设置调节机构190来调节从外层曝气腔172流通至内层微气泡产生腔171的气体的量,当外层曝气腔172与内层微气泡产生腔171连通,从曝气分管110流通至内层微气泡产生腔171的气体扰动内层微气泡产生腔171,从而使内层微气泡产生腔171内产生更多的微气泡,增加内层微气泡产生腔171内气水混合物的气水比。相较于单一的溶气释气法,本申请的曝气头100产生更多的微气泡。相较于单一的直接曝气法,本申请的曝气头100产生足量的微气泡,解决了目前溶气释气过程曝气量小,直接曝气法产生气泡较大从而导致气泡传质差、溶解氧效果差的问题。The aeration head of the present invention communicates with the
在一些实施例中,如图4所示,混合曝气管道160通过减压孔161连通气水分管120,来自气水分管120的气溶水通过减压孔161向混合曝气管道160释放微气泡。减压孔161位于流通口162的下方。在一些示例中,减压孔161的孔径的取值范围为500~1500μm。溶气水经过该减压孔161产生的微气泡的尺寸大小范围为0.5~2mm。In some embodiments, as shown in FIG. 4 , the
在一些实施例中,该曝气头100包括内部支撑件150以及混合曝气管道160。内部支撑件150固定安装于曝气头100内部。混合曝气管道160贯穿内部支撑件150。内部支撑件150与混合曝气管道160将曝气头100内部分隔形成内层微气泡产生腔171和外层曝气腔172。混合曝气管道160的侧壁上开设有用于连通内层微气泡产生腔171和外层曝气腔172的流通口162。调节机构190包括一个活动套设于混合曝气管道160外侧用于封堵流通口162的活动外管193,活动外管193能够沿混合曝气管道160往复移动,用于调节活动外管193的下部遮挡流通口162的面积。In some embodiments, the
当活动外管193封堵流通口162,通过向气水分管120输入溶气水,溶气水经过减压孔161释放微气泡,微气泡经过内层微气泡产生腔171和曝气膜片130后排出,即在内层微气泡产生腔171中通过溶气释气法完成了曝气。When the movable
当曝气分管110输出气体,活动外管193沿混合曝气管道160上移并使流通口162露出时,外层曝气腔172与内层微气泡产生腔171连通,从曝气分管110流通至内层微气泡产生腔171的气体扰动内层微气泡产生腔171,从而使内层微气泡产生腔171内产生更多的微气泡,增加内层微气泡产生腔171内气水混合物的气水比。相较于单一的通过溶气释气法完成曝气,上述过程将直接曝气法与溶气释气法相结合,产生了更多的微气泡。同时,本申请通过调节曝气分管110输出的气体量或者调节活动外管193沿混合曝气管道160的位移量,即控制活动外管193的下部遮挡流通口162的面积大小,能够调节曝气分管110输出的气体流通至内层微气泡产生腔171的量,进而实现控制内层微气泡产生腔171中微气泡的产生量。When the
在一些示例中,流通口162为椭圆孔,椭圆孔的长轴尺寸长度为0.5cm,短轴尺寸长度为0.2cm。在一些示例中,流通口162的数量的取值范围为3~5,这些流通口162沿混合曝气管道160的周向均匀分布。In some examples, the
具体的,如图4所示,曝气膜片130位于该曝气头100的顶部。曝气膜片130与该曝气头100的曝气头壳体140连接形成该曝气头100的内部腔室170。内部支撑件150固定安装于内部腔室170内部,内部支撑件150的外周边缘部与曝气膜片130连接。内部支撑件150和混合曝气管道160将该曝气头100的内部腔室170分隔形成内层微气泡产生腔171和外层曝气腔172。内层微气泡产生腔171的内表面包括内部支撑件150的顶部外表面、曝气膜片130的内表面以及混合曝气管道160的内壁表面。外层曝气腔172的内壁包括内部支撑件150的侧壁外表面、曝气膜片130的内表面、曝气头壳体140的内壁表面以及混合曝气管道160的部分外壁表面。Specifically, as shown in FIG. 4 , the
在一些实施例中,如图4和图5所示,调节机构190还包括挡板191和回复弹簧192,挡板191安装于活动外管193的下部,曝气分管110输出的气体朝向挡板191的下部。回复弹簧192位于混合曝气管道160与内部支撑件150之间,活动外管193通过回复弹簧192连接内部支撑件150。当增加曝气分管110输出的气体量时,曝气分管110输出的气体施加在挡板191上的压力增大,活动外管193在气体压力作用下沿混合曝气管道160朝向曝气膜片130运动并压缩回复弹簧192。当减小曝气分管110输出的气体量时,曝气分管110输出的气体施加在挡板191上的压力减小,活动外管193在回复弹簧192的作用力下向远离曝气膜片130的方向运动。当曝气分管110输出的气体施加在挡板191上的力与回复弹簧192施加在活动外管193上的力平衡时,活动外管193的位置稳定,从而使该曝气头100输出的微气泡的量保持稳定,进而允许本实施例提供的曝气头100通过连续调节曝气分管110输出的气体的量来连续调节该曝气头100输出的微气泡的量。In some embodiments, as shown in Figure 4 and Figure 5, the
在本实施例中,调节机构190借助曝气分管110输出的气体来控制活动外管193沿混合曝气管道160的位移量,即控制活动外管193的下部遮挡流通口162的面积大小,从而调节曝气分管110输出的气体流通至内层微气泡产生腔171的量,进而调节内层微气泡产生腔171中微气泡的产生量。In this embodiment, the
在一些示例中,挡板191和活动外管193可以采用PP塑料。回复弹簧192选用抗腐蚀的不锈钢材料。在一些示例中,混合曝气管道160的外壁下部设置有用于支撑活动外管193的限位部。当曝气分管110不输出气体时,回复弹簧192处于自然状态,限位部与活动外管193的底部接触连接。In some examples, the
在一些实施例中,如图3至图5所示,曝气膜片130可以采用双层曝气膜片,曝气膜片130的两层膜片上的微孔位置相互交错,当曝气头处于非工作状态时,曝气膜片130的两层膜片依靠自身弹性贴合,以使外部污水、污泥等杂质无法进入内层微气泡产生腔171和外层曝气腔172,当曝气头处于工作状态时,曝气膜片130的两层膜片分隔,以便内层微气泡产生腔171的含有微气泡的气水混合物和外层曝气腔172的气体能从微孔排出。在一些示例中,两层膜片上的微孔孔径的取值范围为0.5~2mm。In some embodiments, as shown in Figures 3 to 5, the
在一些实施例中,该曝气头还包括反冲洗管道151,反冲洗管道151的一端穿过外层曝气腔172和内部支撑件150并延伸至活动外管193的外侧壁,活动外管193的侧壁上开设有外管反冲洗孔183,混合曝气管道160的侧壁上开设有内管反冲洗孔163。当开启双吸泵200和气泵400并增加曝气分管110输出的气体量至最大输出值时,曝气分管110输出的气体施加在挡板191上的力增加至最大,使得活动外管193向上移动至回复弹簧192完全压缩的位置,内管反冲洗孔163、外管反冲洗孔183以及反冲洗管道151依次连通。In some embodiments, the aeration head also includes a
此时,大量气体从曝气分管110流通至内层微气泡产生腔171中并与内层微气泡产生腔171的气水混合物混合后冲击内层微气泡产生腔171的内壁并裹挟来自内层微气泡产生腔171的内壁的污泥、微生物等附着物。由于曝气分管110输出的气体量至最大输出值时,内层微气泡产生腔171内部压力大于外部水压,同时由于曝气膜片130对气水混合物的排出存在阻力,在内部压力的作用下,裹挟有污泥、微生物等附着物的气水混合物依次经由内管反冲洗孔163、外管反冲洗孔183以及反冲洗管道151排出。然后,规律地向气水分管120供入和停供气溶水,以便对内层微气泡产生腔171内部形成扰动,从而使得污泥、微生物等附着物更容易随着气水混合物排出至水体中。通过以上过程,本实施例的曝气头100实现了对自身的反向冲洗清洁。At this time, a large amount of gas flows from the
当长时间使用后的曝气头100出现曝气效果差时,可通过以上过程对该曝气头100进行自清洁,从而延长该曝气头100的使用寿命。曝气效果差是指发生水中溶解氧含量提升较慢或者气泡产生量减少等情况。When the
在一些示例中,内管反冲洗孔163、外管反冲洗孔183以及反冲洗管道151具有相同的内孔直径,内孔直径的取值范围为0.3~0.4mm。In some examples, the
在一些示例中,流通口162沿混合曝气管道160方向的尺寸大于等于活动外管193的行程,以便当增加曝气分管110输出的气体量至最大输出值时,流通口162未被活动外管193下部遮挡的面积达到最大,从而使曝气分管110输出的气体更多地流通至内层微气泡产生腔171内,以充分利用曝气分管110输出的气体以及进一步提升曝气头100的反向冲洗清洁能力。In some examples, the size of the
如图6所示,本发明还提供了一种产生强化微气泡的曝气设备。该曝气设备包括上述的一种产生强化微气泡的曝气头100、双吸泵200、溶气罐300、气泵400、布水管500、布气管600、溶氧仪700以及控制器800。一个以上的曝气头100位于曝气池000内的水体底部且曝气头100的曝气膜片130朝向曝气池000的水面。双吸泵200设置有第一进水口210、第二进水口220以及出水口230,双吸泵200用于将外部气体从双吸泵200的第一进水口210泵送至双吸泵200的出水口230以及将曝气池000内的水体上部池水从双吸泵200的第二进水口220泵送至双吸泵200的出水口230,以这种方式形成气水出水。As shown in Figure 6, the present invention also provides an aeration device for generating enhanced microbubbles. The aeration equipment includes the
溶气罐300的输入端310与双吸泵200的出水口230连通,用于接收气水出水。溶气罐300的输出端320通过布水管500与各曝气头100的气水分管120连通,当溶气罐300达到预设的压力值时,溶气罐300的输出端320输出气溶水并将其输送至各曝气头100。The
气泵400用于将外部气体从气泵400的进气口410泵送至气泵400的出气口420,气泵400的出气口420通过布气管600与各曝气头100的曝气分管110连通。溶氧仪700位于曝气池000的水体内,用于监测曝气池000的水体内的溶解氧含量。双吸泵200、气泵400以及溶氧仪700分别都与控制器800电连接,控制器800基于来自溶氧仪700的测量值来控制双吸泵200的启停、气泵400的启停以及气泵400的进气量。The
本发明通过设置控制器800基于来自溶氧仪700的测量值来控制双吸泵200的启停、气泵400的启停以及气泵400的进气量,来调节该曝气设备的曝气模式。当控制器800控制双吸泵200启动、气泵400停用时,该曝气设备处于气溶释气模式。当控制器800控制双吸泵200停用、气泵400启用且未输出最大气体量时,该曝气设备处于直接曝气模式。当控制器800控制双吸泵200启用、气泵400启用且未输出最大气体量时,该曝气设备处于混合曝气模式。当控制器800控制气泵400启用且输出最大气体量、双吸泵200在启用与停用之间切换时,该曝气设备处于反向冲洗模式。The present invention adjusts the aeration mode of the aeration device by setting the
在一些实施例中,控制器800还可以基于来自溶氧仪700的测量值来控制双吸泵200的功率大小,以便调节双吸泵200的第一进水口210的进气量和第二进水口220的进水量,进而调节曝气头100的曝气量。In some embodiments, the
在一些示例中,双吸泵200的气水比的取值范围为1:8~1:11。在一些示例中,溶气罐300选择抗压材料,例如碳钢或者不锈钢材料。溶气罐300上可以设置有压力感应器。在一些示例中,溶气罐300的预设的压力范围0.4~0.6MPa。当该感应器压力感应到的压力达到预设的压力范围时,溶气罐300的输出端320输出气溶水。In some examples, the gas-water ratio of the double-
在一些示例中,布气管600采用PVC或PE材料。布水管500采用PPR或PE材料。In some examples, the
在一些实施例中,该曝气设备还包括过滤器900和第一管路910,过滤器900位于曝气池000内的水体上部,双吸泵200的第二进水口220通过第一管路910与过滤器900连通。第一管路910可以采用耐腐蚀材料,例如PVC、ABS或者PP。In some embodiments, the aeration equipment further includes a
本实施例通过设置过滤器来过滤出曝气池000内的水体上部存在的水污泥等杂质。In this embodiment, impurities such as water sludge existing in the upper part of the water body in the
在一些实施例中,该曝气设备还包括第一进气管240和第二进气管430,双吸泵200的第一进水口210通过第一进气管240与外部气体连通。气泵400的进气口410通过第二进气管430与外部气体连通。In some embodiments, the aeration device further includes a
在一些实施例中,该曝气设备还包括第一止回阀920,第一止回阀920位于第一管路910上。In some embodiments, the aeration device further includes a
在一些实施例中,该曝气设备还包括第二止回阀和第三止回阀,第二止回阀位于第一进气管240上,第三止回阀位于第二进气管430上,用于防止因气泵400、双吸泵200关停,造成水、气回流,进而导致气泵400的驱动电机以及双吸泵200的驱动电机反转。In some embodiments, the aeration device further includes a second check valve and a third check valve, the second check valve is located on the first
本发明还提供了一种产生强化微气泡的曝气方法,该曝气方法的实施使用本申请提供的一种产生强化微气泡的曝气设备,包括以下步骤:The present invention also provides an aeration method for generating enhanced microbubbles. The implementation of the aeration method uses an aeration device for generating enhanced microbubbles provided by the application, including the following steps:
开启双吸泵200,外部气体和曝气池000内的水体上部池水经双吸泵200形成气水出水。气水出水经溶气罐300形成气溶水。曝气头100的气水分管120接收气溶水,气溶水通过曝气头100的减压孔161形成微气泡。微气泡依次经由内层微气泡产生腔171以及曝气膜片130进入曝气池000内的水体中,用于增加水体中的溶解氧含量。Turn on the double-
开启气泵400,外部气体被泵送至曝气头100的曝气分管110,曝气头100的曝气分管110输出的气体朝向挡板191下部。通过调节气泵400的进气量来调节活动外管193的下部遮挡流通口162的面积,以便调节从外层曝气腔172流通至内层微气泡产生腔171的气体量,包括:当增大气泵400的进气量时,曝气分管110输出的气体借助挡板191带动活动外管193沿混合曝气管道160向上移动,从而减小活动外管193的下部遮挡流通口162的面积,用于增加从外层曝气腔172流通至内层微气泡产生腔171的气体量。当减小气泵400的进气量时,曝气分管110输出的气体借助挡板191带动活动外管193沿混合曝气管道160向下移动,从而增大活动外管193的下部遮挡流通口162的面积,用于减少从外层曝气腔172流通至内层微气泡产生腔171的气体量。从外层曝气腔172流通至内层微气泡产生腔171的气体搅动内层微气泡产生腔171产生更多的微气泡,通过调节气泵400的进气量来调节内层微气泡产生腔171内的微气泡的量。When the
本申请提供的一种产生强化微气泡的曝气方法还包括以下步骤:An aeration method for generating enhanced microbubbles provided by the application also includes the following steps:
开启双吸泵200和气泵400并调节气泵400的进气量至最大值,活动外管193向上移动至回复弹簧192完全压缩的位置,内管反冲洗孔163、外管反冲洗孔183以及反冲洗管道151依次连通。控制双吸泵200在开启状态和停止状态之间切换,从曝气头100的减压孔161排出的含有微气泡的气水混合物与从外层曝气腔172流通至内层微气泡产生腔171的气体混合后冲击内层微气泡产生腔171的内壁。裹挟有内层微气泡产生腔171内壁附着物的气水混合物依次经由内管反冲洗孔163、外管反冲洗孔183以及反冲洗管道151排出。Turn on the
使用采用气溶释气法进行曝气的普通曝气设备、采用鼓风曝气法进行曝气的单一微孔曝气设备、采用本发明提供的曝气设备分别对曝气池内的废水进行处理,各设备的COD(Chemical Oxygen Demand,化学需氧量)去除率、氧气利用率、使用寿命、能耗、智能化程度等性能参数如下表所示。从下表1可知,本发明提供的曝气设备集合了气溶释气法和直接曝气法两种曝气方式的优点,相较于其他两种设备,具有氧气利用率高、COD去除率高、使用寿命长、智能化程度高以及能耗较低的优点,能够满足好氧曝气过程。The waste water in the aeration tank is treated respectively by using the common aeration equipment which adopts the gas-dissolving and release-gas method for aeration, the single microporous aeration equipment which adopts the blast aeration method for aeration, and the aeration equipment provided by the present invention. , COD (Chemical Oxygen Demand, chemical oxygen demand) removal rate, oxygen utilization rate, service life, energy consumption, intelligent degree and other performance parameters of each equipment are shown in the table below. It can be seen from the following table 1 that the aeration equipment provided by the present invention combines the advantages of the two aeration methods of the aerosol release method and the direct aeration method. Compared with the other two equipments, it has high oxygen utilization rate and COD removal rate. The advantages of high efficiency, long service life, high degree of intelligence and low energy consumption can meet the aerobic aeration process.
表1各类设备情况对比Table 1 Comparison of various types of equipment
本发明提供了一种产生强化微气泡的曝气头、曝气设备以及曝气方法的思路及方法,具体实现该技术方案的方法和途径很多,以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。本实施例中未明确的各组成部分均可用现有技术加以实现。The present invention provides an idea and method of an aeration head, aeration equipment and an aeration method for generating enhanced microbubbles. There are many methods and approaches for realizing the technical solution, and the above are only preferred embodiments of the present invention. It should be pointed out that those skilled in the art can make some improvements and modifications without departing from the principle of the present invention, and these improvements and modifications should also be regarded as the protection scope of the present invention. All components that are not specified in this embodiment can be realized by existing technologies.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202211639294.3A CN115818854B (en) | 2022-12-20 | 2022-12-20 | Aeration head, aeration equipment and aeration method for generating enhanced microbubbles |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202211639294.3A CN115818854B (en) | 2022-12-20 | 2022-12-20 | Aeration head, aeration equipment and aeration method for generating enhanced microbubbles |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN115818854A true CN115818854A (en) | 2023-03-21 |
| CN115818854B CN115818854B (en) | 2025-05-30 |
Family
ID=85516928
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202211639294.3A Active CN115818854B (en) | 2022-12-20 | 2022-12-20 | Aeration head, aeration equipment and aeration method for generating enhanced microbubbles |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN115818854B (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116750864A (en) * | 2023-04-26 | 2023-09-15 | 苏州中晟环境修复有限公司 | Biological incubator based on river channel water quality cleaning and application method thereof |
| CN118756633A (en) * | 2024-09-02 | 2024-10-11 | 长春华普大通防冰工程技术有限公司 | Concrete dam body anti-icing device |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN206457326U (en) * | 2016-08-29 | 2017-09-01 | 张春辉 | A water-gas mixed oxygenation device |
| CN211546107U (en) * | 2019-11-18 | 2020-09-22 | 杜哲森 | A sewage treatment aeration structures for environmental protection |
| CN213085605U (en) * | 2020-07-22 | 2021-04-30 | 深圳源域生态科创中心有限公司 | Intelligent nano aeration system |
| CN112939212A (en) * | 2021-02-09 | 2021-06-11 | 华东理工大学 | Device and method for enhancing aeration by utilizing micro-bubbles generated by hydraulic shearing |
| KR20220065115A (en) * | 2020-11-12 | 2022-05-20 | 주식회사 대성환경이엔지 | Mixing apparatus for aeration tank |
-
2022
- 2022-12-20 CN CN202211639294.3A patent/CN115818854B/en active Active
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN206457326U (en) * | 2016-08-29 | 2017-09-01 | 张春辉 | A water-gas mixed oxygenation device |
| CN211546107U (en) * | 2019-11-18 | 2020-09-22 | 杜哲森 | A sewage treatment aeration structures for environmental protection |
| CN213085605U (en) * | 2020-07-22 | 2021-04-30 | 深圳源域生态科创中心有限公司 | Intelligent nano aeration system |
| KR20220065115A (en) * | 2020-11-12 | 2022-05-20 | 주식회사 대성환경이엔지 | Mixing apparatus for aeration tank |
| CN112939212A (en) * | 2021-02-09 | 2021-06-11 | 华东理工大学 | Device and method for enhancing aeration by utilizing micro-bubbles generated by hydraulic shearing |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116750864A (en) * | 2023-04-26 | 2023-09-15 | 苏州中晟环境修复有限公司 | Biological incubator based on river channel water quality cleaning and application method thereof |
| CN118756633A (en) * | 2024-09-02 | 2024-10-11 | 长春华普大通防冰工程技术有限公司 | Concrete dam body anti-icing device |
Also Published As
| Publication number | Publication date |
|---|---|
| CN115818854B (en) | 2025-05-30 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US9095826B2 (en) | Apparatus and process for wastewater treatment and biological nutrient removal in activated sludge systems | |
| US8066873B2 (en) | Floating bioreactor system | |
| US11339068B2 (en) | Eductor-based membrane bioreactor | |
| CN115818854A (en) | Aeration head, aeration equipment and aeration method for generating reinforced micro bubbles | |
| CN101024539A (en) | Integrated bubble-free aeration biological composite film film-separation biological reactor | |
| CN202968244U (en) | Jet aerator | |
| KR20110058989A (en) | Hybrid diffuser system | |
| KR20070017429A (en) | Underwater Aeration System with Increased Aeration Capacity and Improved Stability | |
| CA2718851C (en) | Apparatus and process for treatment of wastewater and biological nutrient removal in activated sludge systems | |
| CN201598205U (en) | water processor | |
| CN209039272U (en) | Sewage-treatment plant | |
| CN111333205A (en) | Aeration method and device for biological sewage treatment | |
| CN203048733U (en) | Advanced sewage treatment device | |
| JP2012024647A (en) | Immersion type membrane separator and micro bubble diffusing pipe | |
| JP2010075924A (en) | Underwater aerator | |
| CN100545096C (en) | The large-flux low-pressure membrane module that is used for sewage disposal MBR technology | |
| CN201264942Y (en) | Contact oxidation apparatus for sewage treatment | |
| CN107686166A (en) | Integrated A/O device based on embedding bacterium technology | |
| KR20060111429A (en) | Underwater Aeration System with Improved Oxygen Transfer Rate and Stability | |
| CN203922839U (en) | A kind of Novel small-sized sewage treatment unit | |
| CN103159319A (en) | Biofilter | |
| CN207313248U (en) | Integrated A/O device based on embedding bacterium technology | |
| CN2608489Y (en) | Membrane biological reactor | |
| KR100578892B1 (en) | Flotation separation treatment apparatus and method | |
| CN116474579B (en) | Microbubble generating unit and generator using gas jet method in liquid |
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 | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |
