CN109332018B - Hydraulic cyclone - Google Patents
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- CN109332018B CN109332018B CN201811157478.XA CN201811157478A CN109332018B CN 109332018 B CN109332018 B CN 109332018B CN 201811157478 A CN201811157478 A CN 201811157478A CN 109332018 B CN109332018 B CN 109332018B
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- 239000007788 liquid Substances 0.000 claims abstract description 58
- 239000002351 wastewater Substances 0.000 claims abstract description 35
- 238000000605 extraction Methods 0.000 abstract description 16
- 238000000926 separation method Methods 0.000 abstract description 14
- 230000006641 stabilisation Effects 0.000 description 5
- 238000011105 stabilization Methods 0.000 description 5
- 238000000034 method Methods 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 230000009471 action Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 238000005191 phase separation Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B04—CENTRIFUGAL APPARATUS OR MACHINES FOR CARRYING-OUT PHYSICAL OR CHEMICAL PROCESSES
- B04C—APPARATUS USING FREE VORTEX FLOW, e.g. CYCLONES
- B04C5/00—Apparatus in which the axial direction of the vortex is reversed
- B04C5/02—Construction of inlets by which the vortex flow is generated, e.g. tangential admission, the fluid flow being forced to follow a downward path by spirally wound bulkheads, or with slightly downwardly-directed tangential admission
- B04C5/04—Tangential inlets
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B04—CENTRIFUGAL APPARATUS OR MACHINES FOR CARRYING-OUT PHYSICAL OR CHEMICAL PROCESSES
- B04C—APPARATUS USING FREE VORTEX FLOW, e.g. CYCLONES
- B04C5/00—Apparatus in which the axial direction of the vortex is reversed
- B04C5/08—Vortex chamber constructions
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Abstract
Description
技术领域technical field
本发明涉及萃取与分离技术领域,尤其涉及一种水力旋流器。The invention relates to the technical field of extraction and separation, in particular to a hydrocyclone.
背景技术Background technique
水力旋流器是一种分离设备,主要利用两相的密度不同所受的离心力不同而使两相分离。The hydrocyclone is a kind of separation equipment, which mainly uses the different centrifugal force of the two phases to separate the two phases.
对于煤化工废水行业,除油脱酚均在预处理阶段进行,现有技术主要是利用隔油池除油,萃取塔脱酚,但两者占地面积大,成本高。For the coal chemical wastewater industry, oil removal and dephenolization are carried out in the pretreatment stage. The existing technology mainly uses oil separators for oil removal and extraction towers for dephenolization, but both of them cover a large area and have high costs.
因此,亟待需要提供一种新型水力旋流器来解决上述问题。Therefore, there is an urgent need to provide a new type of hydrocyclone to solve the above problems.
发明内容SUMMARY OF THE INVENTION
本发明的目的在于提供一种水力旋流器,以解决现有旋流器不能同时兼具萃取与分离的问题。The purpose of the present invention is to provide a hydrocyclone to solve the problem that the existing cyclone cannot have both extraction and separation at the same time.
为达此目的,本发明采用以下技术方案:For this purpose, the present invention adopts the following technical solutions:
一种水力旋流器,包括:A hydrocyclone comprising:
进液管,其用于供给油相萃取剂和废水,进液管内设有多个挡板;The liquid inlet pipe is used for supplying the oil phase extractant and waste water, and the liquid inlet pipe is provided with a plurality of baffles;
旋流器本体,其包括位于旋流器本体上部的圆柱管和位于旋流器本体下部的尾管,圆柱管分别与进液管和尾管连通,圆柱管内还设有溢流管。The cyclone body includes a cylindrical pipe located at the upper part of the cyclone body and a tail pipe located at the lower part of the cyclone body. The cylindrical pipe is respectively connected with the liquid inlet pipe and the tail pipe.
作为优选,挡板交错地环设于进液管内壁。Preferably, the baffles are arranged alternately and annularly on the inner wall of the liquid inlet pipe.
作为优选,挡板的高度为进液管直径的0.2-0.8倍。Preferably, the height of the baffle is 0.2-0.8 times the diameter of the liquid inlet pipe.
作为优选,挡板的形状为矩形、弧形或三角形。Preferably, the shape of the baffle is a rectangle, an arc or a triangle.
作为优选,挡板与进液管的进液方向的夹角为50°-120°。Preferably, the included angle between the baffle and the liquid inlet direction of the liquid inlet pipe is 50°-120°.
作为优选,相邻两个挡板的距离为10mm-25mm。Preferably, the distance between two adjacent baffles is 10mm-25mm.
作为优选,进液管的长度为100mm-200mm。Preferably, the length of the liquid inlet pipe is 100mm-200mm.
作为优选,进液管的直径为10mm-30mm。Preferably, the diameter of the liquid inlet pipe is 10mm-30mm.
作为优选,旋流器本体还包括双锥管,其位于圆柱管与尾管之间。Preferably, the cyclone body further includes a double-cone pipe, which is located between the cylindrical pipe and the tail pipe.
作为优选,圆柱管分别与溢流管和双锥管通过法兰连接,双锥管与尾管通过法兰连接。Preferably, the cylindrical pipe is connected with the overflow pipe and the double-cone pipe respectively through flanges, and the double-cone pipe is connected with the tail pipe through flanges.
本发明的有益效果:Beneficial effects of the present invention:
本发明通过在进液管内部设置多个挡板,增加了油相萃取剂和废水的湍动能,两相接触面积增大,且在原有分离的基础上增加了萃取能力,使得萃取剂与废水经进液管快速萃取后,通过旋流器本体可使两者分离,同时兼有萃取与分离能力,解决了现有旋流器不能同时兼具萃取与分离的问题。The invention increases the turbulent kinetic energy of the oil-phase extractant and the wastewater by arranging a plurality of baffles inside the liquid inlet pipe, increases the contact area of the two phases, and increases the extraction capacity on the basis of the original separation, so that the extractant and the wastewater can be separated. After the rapid extraction through the liquid inlet pipe, the two can be separated through the cyclone body, which has both extraction and separation capabilities, and solves the problem that the existing cyclone cannot have both extraction and separation at the same time.
附图说明Description of drawings
图1是本发明提供的水力旋流器的结构示意图。FIG. 1 is a schematic structural diagram of a hydrocyclone provided by the present invention.
图中:In the picture:
1、进液管;2、圆柱管;3、溢流管;4、双锥管;5、尾管;6、挡板。1. Inlet pipe; 2. Cylindrical pipe; 3. Overflow pipe; 4. Double cone pipe; 5. Tail pipe; 6. Baffle.
具体实施方式Detailed ways
下面结合附图并通过具体实施方式来进一步说明本发明的技术方案。The technical solutions of the present invention are further described below with reference to the accompanying drawings and through specific embodiments.
如图1所示,其为本发明提供的水力旋流器的结构示意图。该水力旋流器包括进液管1和旋流器本体,旋流器本体包括圆柱管2、溢流管3、双锥管4和尾管5,其中:As shown in FIG. 1 , it is a schematic structural diagram of the hydrocyclone provided by the present invention. The hydrocyclone includes a liquid inlet pipe 1 and a cyclone body, and the cyclone body includes a cylindrical pipe 2, an overflow pipe 3, a double cone pipe 4 and a tail pipe 5, wherein:
进液管1用于供给油相萃取剂和废水,进液管1内设有多个挡板6,通过在进液管1内部设置多个挡板6,增加了油相萃取剂和废水的湍动能,两相接触面积增大,且在原有分离的基础上增加了萃取能力,使得萃取剂与废水经进液管1能实现快速萃取。The liquid inlet pipe 1 is used for supplying the oil phase extractant and waste water, and a plurality of baffles 6 are arranged in the liquid inlet pipe 1. By setting a plurality of baffle plates 6 inside the liquid inlet pipe 1, the difference between the oil phase extraction agent and the waste water is increased. The turbulent kinetic energy increases the contact area of the two phases, and the extraction capacity is increased on the basis of the original separation, so that the extraction agent and the wastewater can be quickly extracted through the liquid inlet pipe 1.
圆柱管2位于旋流器本体的上部,尾管5位于旋流器本体下部,圆柱管2分别与进液管1和尾管5连通,圆柱管2内还设有溢流管3。优选地,进液管1的出液方向沿圆柱管2的切线设置,溢流管3位于圆柱管2的中心处,且与圆柱管2连通。如此设置,可使油相萃取剂和废水进入圆柱管2后产生离心力,并在离心力的作用下,油相萃取剂和水相分离,油相萃取剂向圆柱管2的中心处偏移,最后通过溢流管3排出,废水则通过尾管5排出。The cylindrical pipe 2 is located at the upper part of the cyclone body, and the tail pipe 5 is located at the lower part of the cyclone body. The cylindrical pipe 2 is connected with the liquid inlet pipe 1 and the tail pipe 5 respectively. Preferably, the liquid outlet direction of the liquid inlet pipe 1 is arranged along the tangent of the cylindrical pipe 2 , and the overflow pipe 3 is located at the center of the cylindrical pipe 2 and communicated with the cylindrical pipe 2 . In this way, the oil phase extractant and the waste water can enter the cylindrical tube 2 to generate centrifugal force, and under the action of the centrifugal force, the oil phase extractant and the water phase are separated, and the oil phase extractant is shifted to the center of the cylindrical tube 2, and finally The waste water is discharged through the overflow pipe 3, and the waste water is discharged through the tail pipe 5.
具体地,双锥管4位于圆柱管2与尾管5之间,优选地,圆柱管2分别与溢流管3和双锥管4通过法兰连接,双锥管4与尾管5通过法兰连接。在竖直方向上,双锥管4的直径逐渐减小,如此油相萃取剂和废水进入圆柱管2后到达双锥管4时,由于直径的减小,可使其切向速度增加,从而保证了两相分离的效果。而且双锥管4可使得内部流体旋转角动量能够及时获得补充,提高旋流强度,强化分离。Specifically, the double-cone pipe 4 is located between the cylindrical pipe 2 and the tail pipe 5. Preferably, the cylindrical pipe 2 is connected with the overflow pipe 3 and the double-cone pipe 4 by flanges, respectively, and the double-cone pipe 4 and the tail pipe 5 are connected by a method. blue connection. In the vertical direction, the diameter of the double-cone pipe 4 gradually decreases, so that when the oil phase extractant and the waste water enter the cylindrical pipe 2 and then reach the double-cone pipe 4, the tangential velocity can be increased due to the reduction of the diameter, thereby increasing the tangential velocity. The effect of two-phase separation is guaranteed. Moreover, the double-cone tube 4 can make the rotational angular momentum of the internal fluid be replenished in time, improve the swirl intensity, and strengthen the separation.
具体地,尾管5的末端还可设有一段或多段锥管,由于尾管5通常较长,中心轻质相(即油相)在末端旋转强度显著减弱、角动量不足、常常出现“摆尾”现象,影响分离效率。而在尾管5的末端增加一段或多段锥管可以弥补角动量、稳定中心轻质相液柱,从而提高分离效率。Specifically, the end of the tail pipe 5 can also be provided with one or more sections of tapered pipes. Since the tail pipe 5 is usually long, the rotation strength of the central light phase (ie the oil phase) at the end is significantly weakened, the angular momentum is insufficient, and “swinging” often occurs. tail" phenomenon, which affects the separation efficiency. However, adding one or more conical tubes at the end of the tail pipe 5 can make up for the angular momentum and stabilize the central light phase liquid column, thereby improving the separation efficiency.
具体地,挡板6交错地环设于进液管1内壁,可增加液体的湍动能和接触面积,使得萃取剂更加有效的萃取废水中的有机物。优选地,相邻两个挡板6的距离为10mm-25mm。进一步地,挡板6的形状为矩形、弧形或三角形,还可以为其它形状,在本实施方式中不做具体限定。为进一步提高油相萃取剂和废水的湍动能,将挡板6与进液管1的进液方向的夹角设为50°-120°。Specifically, the baffles 6 are alternately arranged on the inner wall of the liquid inlet pipe 1, which can increase the turbulent kinetic energy and contact area of the liquid, so that the extractant can more effectively extract the organic matter in the wastewater. Preferably, the distance between two adjacent baffles 6 is 10mm-25mm. Further, the shape of the baffle 6 is a rectangle, an arc or a triangle, and may also be other shapes, which are not specifically limited in this embodiment. In order to further improve the turbulent kinetic energy of the oil phase extractant and the waste water, the included angle between the baffle 6 and the liquid inlet direction of the liquid inlet pipe 1 is set to 50°-120°.
具体地,进液管的长度为100mm-200mm,直径为10mm-30mm,以使油相萃取剂和废水的萃取效果更加充分。Specifically, the length of the liquid inlet pipe is 100mm-200mm, and the diameter is 10mm-30mm, so as to make the extraction effect of the oil phase extractant and the waste water more sufficient.
以下为常规水力旋流器与本发明提供的水力旋流器实验过程和结果对比。The following is a comparison of the experimental process and results between the conventional hydrocyclone and the hydrocyclone provided by the present invention.
本实施例采用的水力旋流器为传统的双锥型水力旋流器,将传统双锥型水力旋流器与本发明提供的水力旋流器分别进行实验,实验中两种水力旋流器的圆柱管2直径为40mm,高度为40mm,溢流管3直径为4mm,双锥管4的上锥管长度为76mm,下锥管长度为382mm,进液管1长200mm,直径15mm,挡板6的高度分别为3mm、5mm、7mm、9mm和11mm,挡板位置交错安装。The hydrocyclone used in this embodiment is a traditional double-cone type hydrocyclone. The traditional double-cone type hydrocyclone and the hydrocyclone provided by the present invention are tested separately. In the experiment, two types of hydrocyclones are used. The diameter of the cylindrical pipe 2 is 40mm, the height is 40mm, the diameter of the overflow pipe 3 is 4mm, the length of the upper cone pipe of the double cone pipe 4 is 76mm, the length of the lower cone pipe is 382mm, the length of the liquid inlet pipe 1 is 200mm, the diameter is 15mm, the block The heights of the plates 6 are respectively 3mm, 5mm, 7mm, 9mm and 11mm, and the baffles are installed in a staggered position.
下面结合附图并通过具体实施方式来进一步说明本发明的技术方案。The technical solutions of the present invention are further described below with reference to the accompanying drawings and through specific embodiments.
实施例一Example 1
本实例采用传统水力旋流器进行实验操作,取少量原水测其COD(化学需氧量,Chemical Oxygen Demand),萃取剂与废水在泵的作用下从进液管1沿切线方向进入水力旋流器中,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E1。In this example, a traditional hydrocyclone is used for the experimental operation, and a small amount of raw water is taken to measure its COD (Chemical Oxygen Demand). In the device, after the system runs stably, take the wastewater flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E1.
实施例二Embodiment 2
本实施例与实施例一不同之处在于,在距离进液管1入口60mm处安装宽度为3mm,高度为15mm的矩形挡板6,挡板6与进液管1垂直方向安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E2。The difference between this embodiment and the first embodiment is that a rectangular baffle 6 with a width of 3 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the baffle 6 is installed perpendicular to the liquid inlet pipe 1, and the system is running. After stabilization, take the wastewater flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E2.
实施例三Embodiment 3
本实施例与实施例一不同之处在于,在距离进液管1入口60mm处安装宽度为5mm,高度为15mm的矩形挡板6,挡板6与进液管1垂直方向安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E3。The difference between this embodiment and the first embodiment is that a rectangular baffle 6 with a width of 5 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the baffle 6 is installed perpendicular to the liquid inlet pipe 1, and the system is running. After stabilization, take the wastewater flowing out from the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E3.
实施例四Embodiment 4
本实施例与实施例一不同之处在于,在距离进液管1入口60mm处安装宽度为7mm,高度为15mm的矩形挡板6,挡板6与进液管1垂直方向安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E4。The difference between this embodiment and the first embodiment is that a rectangular baffle 6 with a width of 7 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the baffle 6 is installed perpendicular to the liquid inlet pipe 1, and the system is running. After stabilization, take the wastewater flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E4.
实施例五Embodiment 5
本实施例与实施例一不同之处在于,在距离进液管1入口60mm处安装宽度为9mm,高度为15mm的矩形挡板6,挡板6与进液管1垂直方向安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E5。The difference between this embodiment and the first embodiment is that a rectangular baffle 6 with a width of 9 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the baffle 6 is installed perpendicular to the liquid inlet pipe 1, and the system is running. After stabilization, take the wastewater flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E5.
实施例六Embodiment 6
本实施例与实施例一不同之处在于,在距离进液管1入口60mm处安装宽度为11mm,高度为15mm的矩形挡板6,挡板6与进液管1垂直方向安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E6。The difference between this embodiment and the first embodiment is that a rectangular baffle 6 with a width of 11 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the baffle 6 is installed perpendicular to the liquid inlet pipe 1, and the system is running. After stabilization, take the wastewater flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E6.
实施例七Embodiment 7
本实施例与实施例四不同之处在于,在距离进液管1入口60mm处安装宽度为7mm,高度为15mm的矩形挡板6,挡板6与进液管1以夹角70°安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E7。The difference between this embodiment and the fourth embodiment is that a rectangular baffle 6 with a width of 7 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the baffle 6 and the liquid inlet pipe 1 are installed at an included angle of 70°, After the system runs stably, take the wastewater flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E7.
实施例八Embodiment 8
本实施例与实施例四不同之处在于,挡板6与进液管1以夹角80°安装,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E8。The difference between this embodiment and the fourth embodiment is that the baffle plate 6 and the liquid inlet pipe 1 are installed at an angle of 80°. After the system runs stably, the waste water flowing out of the tail pipe 5 is taken to measure its COD and the pressure from the inlet to the tail outlet is measured. Decrease p, record and calculate the COD removal rate E8.
实施例九Embodiment 9
本实施例与实施例四不同之处在于,在距离进液管1入口60mm处安装宽度为7mm,高度为15mm的矩形挡板6,在距离第一块挡板6后15mm处交错垂直安装第二块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E9。The difference between this embodiment and the fourth embodiment is that a rectangular baffle 6 with a width of 7 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and the second baffle plate 6 is staggered and vertically installed at a distance of 15 mm behind the first baffle plate 6. Two baffles 6, after the system runs stably, take the waste water flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E9.
实施例十Embodiment ten
本实施例与实施例四不同之处在于,在距离进液管1入口60mm处安装宽度为7mm,高度为15mm的矩形挡板6,在距离第一块挡板6后18mm处交错安装第二块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E10。The difference between this embodiment and the fourth embodiment is that a rectangular baffle 6 with a width of 7 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and a second baffle plate 6 is staggered and installed at a distance of 18 mm behind the first baffle 6. Block baffle 6, after the system runs stably, take the waste water flowing out of the tail pipe 5 to measure its COD and measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E10.
实施例十一Embodiment 11
本实施例与实施例四不同之处在于,在距离进液管1入口60mm处安装宽度为7mm,高度为15mm的矩形挡板6,在距离第一块挡板6后20mm处交错安装第二块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E11。The difference between this embodiment and the fourth embodiment is that a rectangular baffle 6 with a width of 7 mm and a height of 15 mm is installed at a distance of 60 mm from the inlet of the liquid inlet pipe 1, and a second baffle plate 6 is staggered and installed at a distance of 20 mm behind the first baffle 6. Block baffle 6, after the system runs stably, take the waste water flowing out of the tail pipe 5 to measure its COD, measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E11.
实施例十二Embodiment 12
本实施例与实施例十一不同之处在于,在距离第二块挡板6后20mm处交错垂直安装第三块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E12。The difference between this embodiment and the eleventh embodiment is that the third baffle 6 is staggered and vertically installed at a distance of 20 mm behind the second baffle 6, and the COD of the waste water flowing out of the tail pipe 5 is measured after the system runs stably. And measure the pressure drop p from the inlet to the tail outlet, record and calculate the COD removal rate E12.
实施例十三Embodiment thirteen
本实施例与实施例十二不同之处在于,在距离第三块挡板6后20mm处交错安装第四块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E13。The difference between this embodiment and the twelfth embodiment is that the fourth baffle 6 is installed staggeredly at a distance of 20 mm behind the third baffle 6, and after the system runs stably, the waste water flowing out of the tail pipe 5 is taken to measure its COD and Measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E13.
实施例十四Embodiment 14
本实施例与实施例十三不同之处在于,在距离第四块挡板6后20mm处交错安装第五块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E14。The difference between this embodiment and the thirteenth embodiment is that the fifth baffle 6 is installed staggeredly at a distance of 20 mm behind the fourth baffle 6, and after the system runs stably, the waste water flowing out of the tail pipe 5 is taken to measure its COD and Measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E14.
实施例十五Embodiment fifteen
本实施例与实施例十四不同之处在于,在距离第五块挡板6后20mm处交错安装第六块挡板6,等系统运行稳定后取尾管5中流出的废水测其COD并测入口到尾部出口压降p,记录计算COD去除率E15。The difference between this embodiment and the fourteenth embodiment is that the sixth baffle 6 is installed staggeredly at a distance of 20 mm behind the fifth baffle 6, and after the system runs stably, the waste water flowing out of the tail pipe 5 is taken to measure its COD and Measure the pressure drop p from the inlet to the tail outlet, and record and calculate the COD removal rate E15.
表一为不同结构设计的进液管进行萃取的萃取率和压降,表一中显示了在进液管1中交错安装挡板6的旋流器较传统水力旋流器COD去除率提高了29%,因此,本发明提供的水力旋流器能够显著降低废水COD。而且通过表一可知,多挡板6交错安装时,相较单挡板6去除率高,因此,通过增加一定挡板6数量,对于降低废水的COD更加有利。Table 1 shows the extraction rate and pressure drop of the liquid inlet pipes with different structural designs. Table 1 shows that the cyclone with the baffles 6 installed in the liquid inlet pipe 1 in a staggered manner improves the COD removal rate compared with the traditional hydrocyclone. 29%, therefore, the hydrocyclone provided by the present invention can significantly reduce the COD of wastewater. Moreover, it can be seen from Table 1 that when multiple baffles 6 are installed in a staggered manner, the removal rate is higher than that of a single baffle 6. Therefore, by increasing a certain number of baffles 6, it is more beneficial to reduce the COD of wastewater.
表1Table 1
显然,本发明的上述实施例仅仅是为了清楚说明本发明所作的举例,而并非是对本发明的实施方式的限定。对于所属领域的普通技术用户来说,在上述说明的基础上还可以做出其它不同形式的变化或变动。这里无需也无法对所有的实施方式予以穷举。凡在本发明的精神和原则之内所作的任何修改、等同替换和改进等,均应包含在本发明权利要求的保护范围之内。Obviously, the above-mentioned embodiments of the present invention are only examples for clearly illustrating the present invention, rather than limiting the embodiments of the present invention. For users of ordinary skill in the art, changes or modifications in other different forms can also be made on the basis of the above description. There is no need and cannot be exhaustive of all implementations here. Any modifications, equivalent replacements and improvements made within the spirit and principle of the present invention shall be included within the protection scope of the claims of the present invention.
Claims (9)
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2116457A (en) * | 1982-03-13 | 1983-09-28 | British Petroleum Co Plc | Inlet mechanism for cyclone separator |
AU7146587A (en) * | 1987-04-13 | 1988-10-20 | Hunter, Ian Noel | A Device for disentraining fluids from gases |
CN202570449U (en) * | 2012-06-11 | 2012-12-05 | 威海市海王旋流器有限公司 | Spiral feeding body hydrocyclone |
CN103008121A (en) * | 2012-12-22 | 2013-04-03 | 天津天雷科技有限公司 | Cyclone separator with novel structure |
CN204074292U (en) * | 2014-07-08 | 2015-01-07 | 中节能天辰(北京)环保科技有限公司 | A kind of dry paint-fog capturing device |
-
2018
- 2018-09-30 CN CN201811157478.XA patent/CN109332018B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2116457A (en) * | 1982-03-13 | 1983-09-28 | British Petroleum Co Plc | Inlet mechanism for cyclone separator |
AU7146587A (en) * | 1987-04-13 | 1988-10-20 | Hunter, Ian Noel | A Device for disentraining fluids from gases |
CN202570449U (en) * | 2012-06-11 | 2012-12-05 | 威海市海王旋流器有限公司 | Spiral feeding body hydrocyclone |
CN103008121A (en) * | 2012-12-22 | 2013-04-03 | 天津天雷科技有限公司 | Cyclone separator with novel structure |
CN204074292U (en) * | 2014-07-08 | 2015-01-07 | 中节能天辰(北京)环保科技有限公司 | A kind of dry paint-fog capturing device |
Non-Patent Citations (1)
Title |
---|
入口挡板对旋风分离器内流动分布影响的试验研究;李永健等;《当代化工》;20110331;第40卷(第3期);第311-313页 * |
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