CN111646650A - A sewage and sludge treatment system and its hydraulic cavitation sludge reduction machine - Google Patents
A sewage and sludge treatment system and its hydraulic cavitation sludge reduction machine Download PDFInfo
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Abstract
本发明公开了一种污水、污泥处理系统及其水力空化减泥机,所述系统包括生化反应池、二次沉淀池、污泥池、污泥均质池和污泥脱水机,污泥池设置有回流污泥输送管路,回流污泥输送管路安装有回流污泥提升泵,回流污泥输送管路的输出端与生化反应池的污水进口管道连接;生化反应池与二次沉淀池管道连接,二次沉淀池设置有处理水排出管道和污水出口管道,污水出口管道与污泥池连通;污泥池设置有剩余污泥泵,剩余污泥泵的输出端与污泥均质池连通;污水、污泥处理系统设置有水力空化减泥机,含有污泥的待处理混合液泵入水力空化减泥机经过处理后,使有机物通过生化作用更易分解,实现了污泥减量化,使用该系统后,污泥产出量可以减少50~70%。
The invention discloses a sewage and sludge treatment system and a hydraulic cavitation sludge reduction machine. The system includes a biochemical reaction tank, a secondary sedimentation tank, a sludge tank, a sludge homogenization tank and a sludge dewatering machine. The sludge tank is provided with a return sludge conveying pipeline, a return sludge lifting pump is installed in the return sludge conveying pipeline, and the output end of the return sludge conveying pipeline is connected with the sewage inlet pipeline of the biochemical reaction tank; The sedimentation tank is connected with the pipeline, the secondary sedimentation tank is provided with a treated water discharge pipeline and a sewage outlet pipeline, and the sewage outlet pipeline is connected with the sludge tank; The quality pool is connected; the sewage and sludge treatment system is equipped with a hydraulic cavitation sludge reducer, and the mixed liquid containing the sludge to be treated is pumped into the hydraulic cavitation sludge reducer for treatment, so that the organic matter is more easily decomposed by biochemical action, and the pollution is realized. Sludge reduction, after using this system, the sludge output can be reduced by 50-70%.
Description
技术领域technical field
本发明涉及污水、污泥处理技术领域,尤其是涉及一种污水、污泥处理系统及其水力空化减泥机。The invention relates to the technical field of sewage and sludge treatment, in particular to a sewage and sludge treatment system and a hydraulic cavitation sludge reducer.
背景技术Background technique
目前城镇污水、工业有机废水在采用生化方法处理的过程中都会产生大量的剩余污泥。就一般情况而言,每处理10000m3污水,处理过程会产生含水率80%的泥饼约5-10吨。这种污泥种含有病原体、重金属和持久性有机物等有害物质。污泥大多数自然堆放,尚未得到妥善处置。At present, a large amount of excess sludge will be produced in the process of biochemical treatment of urban sewage and industrial organic wastewater. Generally speaking, about 5-10 tons of mud cake with a moisture content of 80% will be produced during the treatment process for every 10,000 m 3 of sewage. This kind of sludge contains harmful substances such as pathogens, heavy metals and persistent organic compounds. Sludge is mostly piled up naturally and has not been properly disposed of.
目前国内外主要的污泥处理技术有:焚烧、填埋、厌氧消化、好氧发酵、热干化石灰稳定、污泥热解、水热处理等方法。均属于污泥产生后对其再进行的末端处理技术。而这些处理方式都会带来巨大的设备投资和高昂的运行费用,同时,还会产生二次污染以及生态安全风险。我国平均每天产生80%的泥饼约50万吨以上。由于这种污泥运输、储存、处理处置成本昂贵,目前又无经济有效的处理处置方法,从而导致了这种污泥通过堆肥、焚烧、热解处理的数量不足5%,绝大部分仍然自然堆存或无序抛撒,对环境造成巨大危害。因此需要一种减少污泥产量的装备,尤其是在污水处理过程中就可减少污泥产量,实现源头减排,进行清洁生产迫在眉睫,十分必要。At present, the main sludge treatment technologies at home and abroad are: incineration, landfill, anaerobic digestion, aerobic fermentation, thermal drying lime stabilization, sludge pyrolysis, hydrothermal treatment and other methods. All belong to the terminal treatment technology after sludge is produced. These treatment methods will bring huge equipment investment and high operating costs, and at the same time, will also produce secondary pollution and ecological safety risks. On average, 80% of the mud cake is produced every day in my country, which is more than 500,000 tons. Due to the high cost of transportation, storage, treatment and disposal of this sludge, and there is currently no cost-effective treatment and disposal method, the amount of this sludge treated by composting, incineration and pyrolysis is less than 5%, and most of the sludge is still natural. Stacking or throwing in disorder will cause great harm to the environment. Therefore, a device for reducing sludge production is needed, especially in the process of sewage treatment, which can reduce sludge production and realize source emission reduction. It is imminent and necessary to carry out clean production.
当前诸多串联组合式空化设备及装置专利的工作原理是:待处理混合液高速流过多级收缩喷管或孔板等时,产生水力空化效应以对混合液中的污染物进行降解处理。理论上多级收缩喷组及孔板的串联组合会产生协同效应,强化空化产生的强度,增强对污染物的降解力度。但实际应用中多级串联组合式空化装置或设备存在以下不足之处:The working principle of many current series combined cavitation equipment and device patents is: when the mixed liquid to be treated flows at a high speed through a multi-stage shrinking nozzle or orifice plate, etc., a hydraulic cavitation effect is generated to degrade the pollutants in the mixed liquid. . Theoretically, the series combination of multi-stage shrinking spray group and orifice plate will produce a synergistic effect, strengthen the intensity of cavitation, and enhance the degradation of pollutants. However, in practical applications, the multi-stage series combined cavitation device or equipment has the following shortcomings:
1、喷嘴或孔板等的串联,对输送泵性能参数及功率要求极高,每一级要想实现理想空化强度的流速及压力条件很难同时具备,调节难度极大;1. The series connection of nozzles or orifice plates requires extremely high performance parameters and power of the transfer pump. It is difficult to achieve the flow rate and pressure conditions of the ideal cavitation intensity at each stage at the same time, and the adjustment is extremely difficult;
2、现实中要处理的污染物混合液往往成分复杂,含有很多大块状固体物及长的絮体等,很容易堵塞设备,导致设备维护频次高,维护费用投入大;2. In reality, the pollutant mixture to be treated is often complex in composition, containing many large solids and long flocs, etc., which can easily block the equipment, resulting in high equipment maintenance frequency and large maintenance costs;
3、水力空化强度越大,易损件的寿命就越短需要定期更换,而串联组合式空化设备往往维护难度较大。3. The greater the strength of hydraulic cavitation, the shorter the life of wearing parts and need to be replaced regularly, while the series combined cavitation equipment is often difficult to maintain.
因此有必要予以改进。Therefore it is necessary to improve.
发明内容SUMMARY OF THE INVENTION
针对现有技术存在的不足,本发明的目的是提供一种污水、污泥处理系统及该系统的水力空化减泥机,简化了结构设计,提高空化效率。In view of the deficiencies in the prior art, the purpose of the present invention is to provide a sewage and sludge treatment system and a hydraulic cavitation sludge reducer for the system, which simplifies the structural design and improves the cavitation efficiency.
为了实现上述目的,本发明所采用的技术方案是In order to achieve the above purpose, the technical solution adopted in the present invention is
一种污水、污泥处理系统,包括依次通过管道连接的生化反应池、二次沉淀池、污泥池、污泥均质池和污泥脱水机,A sewage and sludge treatment system, comprising a biochemical reaction tank, a secondary sedimentation tank, a sludge tank, a sludge homogenization tank and a sludge dewatering machine connected in sequence through pipelines,
污泥池设置有回流污泥输送管路,回流污泥输送管路安装有回流污泥提升泵,回流污泥输送管路的输出端与生化反应池的污水进口管道连接;The sludge tank is provided with a return sludge conveying pipeline, a return sludge lifting pump is installed in the return sludge conveying pipeline, and the output end of the return sludge conveying pipeline is connected with the sewage inlet pipeline of the biochemical reaction tank;
生化反应池与二次沉淀池管道连接,二次沉淀池设置有处理水排出管道和污水出口管道,污水出口管道与污泥池连通;The biochemical reaction tank is connected with the secondary sedimentation tank pipeline, the secondary sedimentation tank is provided with a treated water discharge pipeline and a sewage outlet pipeline, and the sewage outlet pipeline is connected with the sludge tank;
污泥池设置有剩余污泥泵,剩余污泥泵的输出端与污泥均质池连通,污泥均质池的输出端与污泥脱水机连接;The sludge tank is provided with an excess sludge pump, the output end of the excess sludge pump is connected with the sludge homogenization tank, and the output end of the sludge homogenization tank is connected with the sludge dewatering machine;
所述污水、污泥处理系统设置有水力空化减泥机。The sewage and sludge treatment system is provided with a hydraulic cavitation sludge reducing machine.
进一步的技术方案中,所述污泥池管道连接有排污泵,排污泵的输入端设置有吸入管路,吸入管路的输入端与污泥池连通,排污泵的输出端设置有提升加压管路,提升加压管路的输出端与水力空化减泥机的输入端连通,水力空化减泥机的出水口设置有输出管路,输出管路的输出端与污泥池连通。In a further technical solution, the sludge tank pipeline is connected with a sewage pump, the input end of the sewage pump is provided with a suction pipeline, the input end of the suction pipeline is communicated with the sludge tank, and the output end of the sewage pump is provided with a lifting pressure. Pipeline, the output end of the lifting and pressurizing pipeline is connected with the input end of the hydraulic cavitation sludge reduction machine, the water outlet of the hydraulic cavitation sludge reduction machine is provided with an output pipeline, and the output end of the output pipeline is connected with the sludge tank.
进一步的技术方案中,所述生化反应池管道连接有排污泵,排污泵的输入端设置有吸入管路,吸入管路的输入端与生化反应池连通,排污泵的输出端设置有提升加压管路,提升加压管路的输出端与水力空化减泥机的输入端连通,水力空化减泥机的出水口设置有输出管路,输出管路的输出端与生化反应池连通。In a further technical solution, the pipeline of the biochemical reaction tank is connected with a sewage pump, the input end of the sewage pump is provided with a suction pipeline, the input end of the suction pipeline is communicated with the biochemical reaction tank, and the output end of the sewage pump is provided with a lifting and pressurizing pipeline. Pipeline, the output end of the lifting and pressurizing pipeline is connected with the input end of the hydraulic cavitation sludge reduction machine, the water outlet of the hydraulic cavitation sludge reduction machine is provided with an output pipeline, and the output end of the output pipeline is connected with the biochemical reaction pool.
进一步的技术方案中,所述污泥均质池管道连接有排污泵,排污泵的输入端设置有吸入管路,吸入管路的输入端与污泥均质池连通,排污泵的输出端设置有提升加压管路,提升加压管路的输出端与水力空化减泥机的输入端连通,水力空化减泥机的出水口设置有输出管路,输出管路的输出端与污泥均质池连通,污泥均质池设置有溢流管道,溢流管道的输出端与所述生化反应池连通。In a further technical solution, a sewage pump is connected to the pipeline of the sludge homogenization tank, the input end of the sewage pump is provided with a suction pipeline, the input end of the suction pipeline is communicated with the sludge homogenization tank, and the output end of the sewage pump is provided with a suction pipeline. There is a lifting pressure pipeline, the output end of the lifting pressure pipeline is connected with the input end of the hydraulic cavitation sludge reduction machine, the water outlet of the hydraulic cavitation sludge reduction machine is provided with an output pipeline, and the output end of the output pipeline is connected with the sewage. The sludge homogenization tank is connected, and the sludge homogenization tank is provided with an overflow pipeline, and the output end of the overflow pipeline is connected with the biochemical reaction tank.
一种污水、污泥处理系统的水力空化减泥机,包括壳体和空化喷射器,壳体的底部具有出水口;壳体上端部设置有至少两个空化喷射器,壳体安装有支架,支架的上端部设置有与空化喷射器相对应的粉碎挡板,每一空化喷射器的输出端分别朝向一粉碎挡板,支架的底部安装有旋转轴,旋转轴的底部伸入所述出水口内安装有空化诱导叶轮;A hydraulic cavitation and sludge reduction machine for sewage and sludge treatment systems, comprising a shell and a cavitation ejector, the bottom of the shell is provided with a water outlet; the upper end of the shell is provided with at least two cavitation ejectors, the shell is installed There is a bracket, the upper end of the bracket is provided with a pulverizing baffle corresponding to the cavitation ejector, the output end of each cavitation ejector faces a pulverizing baffle, the bottom of the bracket is equipped with a rotating shaft, and the bottom of the rotating shaft extends into A cavitation inducing impeller is installed in the water outlet;
空化喷射器包括收缩喷管和喷嘴,收缩喷管的输入端与进液泵的输出端连接,收缩喷管的输出端与喷嘴连通,喷嘴的输出端朝向所述粉碎挡板。The cavitation ejector includes a shrinking nozzle and a nozzle, the input end of the shrinking nozzle is connected with the output end of the liquid feed pump, the output end of the shrinking nozzle is connected with the nozzle, and the output end of the nozzle faces the pulverizing baffle.
当空化喷射器推动粉碎挡板进行旋转时,旋转轴带动空化诱导叶轮进行旋转。When the cavitation ejector pushes the crushing baffle to rotate, the rotating shaft drives the cavitation induction impeller to rotate.
进一步的技术方案中,所述支架包括安装架和固定架,固定件的底部安装于壳体的内壁,安装架安装于固定架。In a further technical solution, the bracket includes a mounting frame and a fixing frame, the bottom of the fixing piece is mounted on the inner wall of the housing, and the mounting frame is mounted on the fixing frame.
进一步的技术方案中,所述粉碎挡板向内凹入形成一锥形槽,锥角为30~60°。In a further technical solution, the pulverizing baffle plate is recessed inward to form a conical groove, and the conical angle is 30-60°.
进一步的技术方案中,所述旋转轴贯穿所述固定架的顶部与所述安装架连接,当空化喷射器推动粉碎挡板进行旋转时,旋转轴带动空化诱导叶轮进行旋转。In a further technical solution, the rotating shaft penetrates through the top of the fixing frame and is connected to the mounting frame. When the cavitation ejector pushes the pulverizing baffle to rotate, the rotating shaft drives the cavitation inducing impeller to rotate.
进一步的技术方案中,所述收缩喷管内置有螺旋导叶体,所述喷嘴为空心管状结构。In a further technical solution, a spiral guide vane body is built in the shrinking nozzle, and the nozzle is a hollow tubular structure.
进一步的技术方案中,所述喷嘴内置有螺旋导叶体,所述收缩喷管为空心锥体形结构。In a further technical solution, a spiral guide vane body is built in the nozzle, and the shrinking nozzle is a hollow cone-shaped structure.
采用上述结构后,本发明和现有技术相比所具有的优点是:本发明在使用过程中,混合液在空化喷射器中形成高速射流撞击在对应的粉碎挡板上,使混合液中的大颗粒污泥絮体及部分污泥细胞破碎,然后进入壳体下方,经过空化诱导叶轮产生射窝空化后通过出水口排出,本发明空化效率高,不易堵塞,维护成本低,占地面积小,结构简单,降低了生产成本。污水、污泥处理系统设置有水力空化减泥机,含有污泥的待处理混合液泵入水力空化减泥机经过处理后,使有机物通过生化作用更易分解,实现了污泥减量化,使用该系统后,污泥产出量可以减少50~70%。After the above structure is adopted, the advantages of the present invention compared with the prior art are: during the use of the present invention, the mixed liquid forms a high-speed jet in the cavitation ejector and impinges on the corresponding pulverizing baffles, so that the mixed liquid is formed in the cavitation ejector. The large granular sludge flocs and part of the sludge cells are broken, and then enter the lower part of the shell, and are discharged through the water outlet through the cavitation induced impeller to generate cavitation. Small footprint, simple structure, and reduced production costs. The sewage and sludge treatment system is equipped with a hydraulic cavitation sludge reducer, and the mixed liquid containing sludge to be treated is pumped into the hydraulic cavitation sludge reducer for treatment, so that the organic matter is more easily decomposed through biochemical action, and the sludge reduction is realized. , after using the system, the sludge output can be reduced by 50-70%.
附图说明Description of drawings
下面结合附图和实施例对本发明进一步说明。The present invention will be further described below in conjunction with the accompanying drawings and embodiments.
图1为本发明一种污水、污泥处理系统实施例1的流程图;Fig. 1 is a flow chart of
图2为本发明一种污水、污泥处理系统实施例2的流程图;2 is a flow chart of
图3为本发明一种污水、污泥处理系统实施例3的流程图;3 is a flow chart of
图4为水力空化减泥机的结构示意图;Fig. 4 is the structural schematic diagram of hydraulic cavitation sludge reduction machine;
图5为水力空化减泥机的俯视图;Fig. 5 is the top view of hydraulic cavitation sludge reducing machine;
图6为空化喷射器的结构图;Figure 6 is a structural diagram of a cavitation injector;
图7为锥形空化诱导盘的结构图;Figure 7 is a structural diagram of a conical cavitation inducing disc;
图8为水力空化减泥机的剖面图;Figure 8 is a cross-sectional view of a hydraulic cavitation sludge reducer;
图9为水力空化减泥机的工作示意图;Fig. 9 is the working schematic diagram of hydraulic cavitation sludge reduction machine;
图10是空化喷射器的另一结构示意图;Fig. 10 is another structural schematic diagram of the cavitation ejector;
图11是水力空化减泥机的另一结构示意图。Fig. 11 is another structural schematic diagram of the hydraulic cavitation sludge reducer.
具体实施方式Detailed ways
以下所述仅为本发明的较佳实施例,并不因此而限定本发明的保护范围。The following descriptions are only preferred embodiments of the present invention, and therefore do not limit the protection scope of the present invention.
实施例1Example 1
见图1所示,一种污水、污泥处理系统,包括依次通过管道连接的生化反应池7、二次沉淀池8、污泥池5、污泥均质池10和污泥脱水机11,As shown in Figure 1, a sewage and sludge treatment system includes a
污泥池5设置有回流污泥输送管路14,回流污泥输送管路14安装有回流污泥提升泵6,回流污泥输送管路14的输出端与生化反应池7的污水进口管道连接;污泥池5内的改性污泥通过回流污泥提升泵6将其通过回流污泥输送管路14送入生化反应池7内进行生化处理。The
生化反应池7与二次沉淀池8管道连接,二次沉淀池8设置有处理水排出管道和污水出口管道,污水出口管道与污泥池5连通;生化反应池7将生化处理后的污泥送入二次沉淀池8,二次沉淀池8将沉淀后的污泥送入污泥池5中,将处理后的水排出。The
污泥池5设置有剩余污泥泵9,剩余污泥泵9的输出端与污泥均质池10连通,污泥均质池10的输出端与污泥脱水机11连接;剩余污泥泵9将污泥池5内的污泥送入污泥均质池10内,污泥均质池10将污泥送入污泥脱水机11进行脱水处理,待处理完后将污泥排出。The
污水、污泥处理系统设置有水力空化减泥机3。The sewage and sludge treatment system is provided with a hydraulic cavitation
所述污泥池5管道连接有排污泵1,排污泵1的输入端设置有吸入管路13,吸入管路13的输入端与污泥池5连通,排污泵1的输出端设置有提升加压管路2,提升加压管路2的输出端与水力空化减泥机3的输入端连通,水力空化减泥机3的出水口设置有输出管路4,输出管路4的输出端与污泥池5连通。The
排污泵1的吸入管路13将污泥池5中50~80%的污泥量送入水力空化减泥机3进行空化处理,空化处理后80~100%的改性剩余污泥通过剩余污泥泵9泵入污泥均质池10后,由污泥脱水机11进行脱水处理。The
实施例2Example 2
见图2所示,本实施例与实施例1的区别在于:所述生化反应池7管道连接有排污泵1,排污泵1的输入端设置有吸入管路13,吸入管路13的输入端与生化反应池7连通,排污泵1的输出端设置有提升加压管路2,提升加压管路2的输出端与水力空化减泥机3的输入端连通,水力空化减泥机3的出水口设置有输出管路4,输出管路4的输出端与生化反应池7连通。As shown in FIG. 2 , the difference between this embodiment and
污泥泵1的吸入管路13将生化反应池7中80~100%的污水量送入水力空化减泥机3中进行空化处理,空化处理完后污水经过二次沉淀池8沉淀后,清水排放,二次沉淀池8底部的沉淀物压缩回流进入污泥池5中,污泥池5将30~100%的污泥量回流至生化反应池7进行处理,0~30%的剩余污泥送入污泥脱水机11进行处理。The
实施例3Example 3
见图3所示,本实施例与实施例1的区别在于:所述污泥均质池10管道连接有排污泵1,排污泵1的输入端设置有吸入管路13,吸入管路13的输入端与污泥均质池10连通,排污泵1的输出端设置有提升加压管路2,提升加压管路2的输出端与水力空化减泥机3的输入端连通,水力空化减泥机3的出水口设置有输出管路4,输出管路4的输出端与污泥均质池10连通。As shown in FIG. 3 , the difference between this embodiment and
污泥泵1将污泥均质池10中100%的污泥量送入水力空化减泥机3中进行空化处理,处理完成后,将其送回污泥均质池10中,一部分被处理的污泥经过溢流管道15流至生化池7进行再次生化处理,其余被处理污泥又污泥脱水机11处理。The
经过该系统处理后的,污泥产出量减少50~70%。After being treated by this system, the output of sludge is reduced by 50-70%.
实施例4Example 4
见图4~图9所示,一种污水、污泥处理系统的水力空化减泥机,包括壳体1和空化喷射器2,壳体1的底部具有出水口11;壳体1上端部设置有至少两个空化喷射器2,壳体1安装有支架31,支架31的上端部设置有与空化喷射器2相对应的粉碎挡板3,每一空化喷射器2的输出端分别朝向一粉碎挡板3,支架31的底部安装有旋转轴22,旋转轴22的底部伸入所述出水口11内安装有空化诱导叶轮4;As shown in FIGS. 4 to 9 , a hydraulic cavitation sludge reduction machine for sewage and sludge treatment systems includes a
空化喷射器2包括收缩喷管22和喷嘴21,收缩喷管22的输入端与进液泵的输出端连接,收缩喷管22的输出端与喷嘴21连通,喷嘴21的输出端朝向所述粉碎挡板3。The
当空化喷射器2推动粉碎挡板3进行旋转时,旋转轴22带动空化诱导叶轮4进行旋转。When the
空化诱导叶轮4随着旋转粉碎挡板3的高速转动而旋转,与所述壳体1的收窄结构协同产生绕流、射涡,增强次级空化,使混合液中的大颗粒污泥絮体及部分污泥细胞进一步破碎。The cavitation-inducing
本发明在使用过程中,混合液在空化喷射器2中形成高速射流撞击在对应的粉碎挡板3上,使混合液中的大颗粒污泥絮体及部分污泥细胞破碎,然后进入壳体1下方,经过空化诱导叶轮4产生射窝空化后通过出水口11排出,本发明空化效率高,不易堵塞,维护成本低,占地面积小。During the use process of the present invention, the mixed liquid forms a high-speed jet in the
支架31包括安装架311和固定架312,固定件的底部安装于壳体1的内壁,安装架311安装于固定架312。The
粉碎挡板3向内凹入形成一锥形槽,锥角为30~60°。通过带有锥形槽的粉碎挡板3能够加强对混合液的破碎空化。The crushing
旋转轴22贯穿所述固定架312的顶部与所述安装架连接,当空化喷射器2推动粉碎挡板3进行旋转时,旋转轴22带动空化诱导叶轮4进行旋转。空化诱导叶轮4有两个或三个叶轮片,且空化诱导叶轮的最大直径不超过所述水流出口11内径的80%;所述空化诱导叶轮4随着旋转粉碎挡板3的高速转动而旋转,与所述腔壁1的收窄结构协同产生绕流、射涡,增强次级空化,使混合液中的大颗粒污泥絮体及部分污泥细胞进一步破碎。The rotating
收缩喷管22内置有螺旋导叶体221,所述喷嘴21为空心管状结构。螺旋导叶体221的高度不超过收缩喷管22内径D的1/2,所述螺旋导叶体221的螺旋升角在48°~70°之间;所述螺旋导叶体221由三片螺旋导叶构成时,所述螺旋导叶体221的长度不超过1/2导程;所述螺旋导叶体221由两片螺旋导叶构成时,所述螺旋导叶体221的长度不超过3/4导程。通过螺旋导叶体211对收缩喷管22内的液体进一步压缩,加快液体喷出的速度,增强空化。The constricting
本发明采用并联与串联组合实现多级空化,因各级空化作用有所不同,且对各级空化的协同进行了优化。首先并联多个喷嘴21实现射流空化,同时喷嘴21的高速射流撞击对应的粉碎挡板3以使大颗粒污泥絮体破碎化,为后续空化破解污染物做好充分准备;其二、粉碎挡板3的旋转轴22下端连接空化诱导叶轮4,提高后续一级射流空化的强度;其三,喷嘴21汇聚上一级并联喷嘴21的流体能量再次产生射流空化。以上多级空化的协同连续作用,大大提高了污染物混合液的处理效率,降低了对单台输送泵的性能要求,参数调节变得简单,防堵塞效果好,维护变得更加容易,综合使用费用降低。The invention adopts the combination of parallel and series to realize multi-stage cavitation, because the cavitation effect of each stage is different, and the coordination of cavitation of each stage is optimized. First, a plurality of
实施例5Example 5
见图10~11所示,本实施例与实施例1的区别在于:喷嘴21内置有螺旋导叶体211,所述收缩喷管22为空心锥体形结构。螺旋导叶体221的高度不超过收缩喷管22内径D的1/2,所述螺旋导叶体221的螺旋升角在48°~70°之间;所述螺旋导叶体221由三片螺旋导叶构成时,所述螺旋导叶体221的长度不超过1/2导程;所述螺旋导叶体221由两片螺旋导叶构成时,所述螺旋导叶体221的长度不超过3/4导程。通过螺旋导叶体211对收缩喷管22内的液体进一步压缩,加快液体喷出的速度,增强空化。As shown in FIGS. 10 to 11 , the difference between this embodiment and
本发明水力空化减泥机为综合水力空化实用设备,工作原理如图7所示:由无堵塞排污泵提供一定流量和压力的污泥混合液高速进入空化喷射器2中,在空化喷射器2产生空化作用,并高速射出撞击粉碎挡板3的综合作用下实现对污泥混合液的第一次预处理,以达到大颗粒污泥絮体破碎化,并为次级的空化效应提供足够的压力及流量配比。接下来污泥混合液在减泥机3下端的漏斗型结构中产生次级射涡空化,对空化喷射器2空化预处理过的污泥混合液进行更充分地处理,以此提高减泥机3对泥水的一次性通过处理效率。通过在减泥机3下端水流出口11加装锥形空化诱导盘4,可以产生更为强烈的射涡空化。The hydraulic cavitation sludge reducer of the present invention is a comprehensive hydraulic cavitation practical equipment, and the working principle is shown in Figure 7: the sludge mixture with a certain flow and pressure provided by the non-clogging sewage pump enters the
污泥混合液经水力空化减泥机3以上多级空化处理后,污泥絮体变得破碎化,其中的难降解有机物直接分解成C02、H20,难降解有机物大分子链断裂为小分子链,然后被氧化成脂肪酸,从而提高污水有机物的可生化性。同时空化产生时伴随强烈的冲击波的微射流,并以每秒数万次连续作用发生着,带来高效机械切碎效应,并产生具有高化学活性的自由基-OH,随后与溶液中有机污染物发生氧化反应,将混合液中有机污染物氧化分解成为低分子量物质,冲击波和高速微射流在混合液中产生的强大水力剪切力,对污泥结构进行有效破坏,使大分子主链上的碳键断裂,转变为短链低分子有机物,使细胞内溶质流出,并进一步被分解掉,为后续生化反应创造有利条件,使有机物通过生化作用更易分解而减少,实现了污泥减量化。污水厂使用该方法后,污泥产出量可减少50~70%以上。After the sludge mixed liquid is treated by 3 or more stages of cavitation in the hydraulic cavitation sludge reducer, the sludge flocs become fragmented, and the refractory organic matter in it is directly decomposed into C0 2 and H 2 0, and the refractory organic matter macromolecular chain It is broken into small molecular chains and then oxidized into fatty acids, thereby improving the biodegradability of sewage organic matter. At the same time, the cavitation is accompanied by a strong shock wave micro-jet, and it occurs continuously at tens of thousands of times per second, bringing about a high-efficiency mechanical chopping effect, and generating a free radical -OH with high chemical activity, which is then combined with organic compounds in the solution. The pollutants undergo oxidation reaction, and the organic pollutants in the mixed liquid are oxidized and decomposed into low molecular weight substances. The strong hydraulic shear force generated by shock waves and high-speed micro-jets in the mixed liquid can effectively destroy the sludge structure and make the macromolecular main chain. The carbon bonds on it are broken and converted into short-chain low-molecular-weight organic matter, so that the intracellular solute flows out and is further decomposed, creating favorable conditions for subsequent biochemical reactions, making the organic matter easier to decompose and reducing through biochemical action, and achieving sludge reduction change. After the sewage plant uses this method, the sludge output can be reduced by more than 50-70%.
以上内容仅为本发明的较佳实施例,对于本领域的普通技术人员,依据本发明的思想,在具体实施方式及应用范围上均会有改变之处,本说明书内容不应理解为对本发明的限制。The above contents are only preferred embodiments of the present invention. For those of ordinary skill in the art, according to the idea of the present invention, there will be changes in the specific embodiments and application scope. limits.
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114149167A (en) * | 2021-12-20 | 2022-03-08 | 黑龙江省科学院高技术研究院 | Device and method for treating carbon source released by excess sludge through cavitation technology |
Citations (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103408208A (en) * | 2013-08-28 | 2013-11-27 | 范鹏辉 | A Supercritical Dissolved Air Cavitation Device for Enhanced Sludge Reduction |
| CN103408212A (en) * | 2013-08-28 | 2013-11-27 | 范鹏辉 | A method of using supercritical dissolved air cavitation equipment and its enhanced sludge reduction |
| KR20160006624A (en) * | 2014-07-09 | 2016-01-19 | 주식회사 엔바이로앤에너지 | Sludge solubilization facility using cavitation effect |
| CN205710376U (en) * | 2016-04-20 | 2016-11-23 | 广州市正思环保科技有限公司 | Mud decrement stabilization system |
| CN106630373A (en) * | 2015-11-04 | 2017-05-10 | 东莞源控环保科技有限公司 | Sewage treatment system and method for effectively realizing organic sludge reduction |
| CN106630523A (en) * | 2015-11-04 | 2017-05-10 | 东莞源控环保科技有限公司 | A hydraulic cavitation mud reducer and its sewage treatment method |
| CN106630370A (en) * | 2015-11-04 | 2017-05-10 | 东莞源控环保科技有限公司 | Hydraulic cavitation phosphorus removal device and sewage treatment system and method using the device |
| CN106902930A (en) * | 2017-02-16 | 2017-06-30 | 中南大学 | A kind of sludge organism body cell means for breaking walls and its method for sludge organism body cell broken wall |
| CN207608474U (en) * | 2017-10-27 | 2018-07-13 | 深圳市南科环保科技有限公司 | Reactor for treating excess sludge by cavitation jet |
| CN109467295A (en) * | 2019-01-02 | 2019-03-15 | 黄河科技学院 | A kind of sludge environmental protection treatment system |
| CN110370465A (en) * | 2019-08-08 | 2019-10-25 | 包丽珠 | A kind of concrete production drainpipe |
-
2020
- 2020-06-22 CN CN202010571407.5A patent/CN111646650B/en active Active
Patent Citations (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103408208A (en) * | 2013-08-28 | 2013-11-27 | 范鹏辉 | A Supercritical Dissolved Air Cavitation Device for Enhanced Sludge Reduction |
| CN103408212A (en) * | 2013-08-28 | 2013-11-27 | 范鹏辉 | A method of using supercritical dissolved air cavitation equipment and its enhanced sludge reduction |
| KR20160006624A (en) * | 2014-07-09 | 2016-01-19 | 주식회사 엔바이로앤에너지 | Sludge solubilization facility using cavitation effect |
| CN106630373A (en) * | 2015-11-04 | 2017-05-10 | 东莞源控环保科技有限公司 | Sewage treatment system and method for effectively realizing organic sludge reduction |
| CN106630523A (en) * | 2015-11-04 | 2017-05-10 | 东莞源控环保科技有限公司 | A hydraulic cavitation mud reducer and its sewage treatment method |
| CN106630370A (en) * | 2015-11-04 | 2017-05-10 | 东莞源控环保科技有限公司 | Hydraulic cavitation phosphorus removal device and sewage treatment system and method using the device |
| CN205710376U (en) * | 2016-04-20 | 2016-11-23 | 广州市正思环保科技有限公司 | Mud decrement stabilization system |
| CN106902930A (en) * | 2017-02-16 | 2017-06-30 | 中南大学 | A kind of sludge organism body cell means for breaking walls and its method for sludge organism body cell broken wall |
| CN207608474U (en) * | 2017-10-27 | 2018-07-13 | 深圳市南科环保科技有限公司 | Reactor for treating excess sludge by cavitation jet |
| CN109467295A (en) * | 2019-01-02 | 2019-03-15 | 黄河科技学院 | A kind of sludge environmental protection treatment system |
| CN110370465A (en) * | 2019-08-08 | 2019-10-25 | 包丽珠 | A kind of concrete production drainpipe |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114149167A (en) * | 2021-12-20 | 2022-03-08 | 黑龙江省科学院高技术研究院 | Device and method for treating carbon source released by excess sludge through cavitation technology |
| CN114149167B (en) * | 2021-12-20 | 2024-02-06 | 黑龙江省科学院高技术研究院 | Device and method for treating residual sludge by cavitation technology to release internal carbon source |
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|---|---|
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