CN103754986B - A kind of Oil stain mixture separation system - Google Patents

A kind of Oil stain mixture separation system Download PDF

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CN103754986B
CN103754986B CN201410033548.6A CN201410033548A CN103754986B CN 103754986 B CN103754986 B CN 103754986B CN 201410033548 A CN201410033548 A CN 201410033548A CN 103754986 B CN103754986 B CN 103754986B
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oil
water
spiral slot
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separation system
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CN103754986A (en
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高迎新
耿麒翔
焦思明
陈宏�
杨敏
张国林
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Research Center for Eco Environmental Sciences of CAS
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Abstract

A kind of Oil stain mixture separation system is provided, its main body is the separator main body (114) of roughly cylindrical tube shape, and major parts comprises spiral slot cylindrical shell (104), spiral slot (108), mixed solution entry portal (110), water shoot (113), particulate matter settlement plate (111) and separator main body (114); Separator main body (114) inner side is provided with spiral slot cylindrical shell (104), is close to spiral slot cylindrical shell (104) inwall and spiral slot (108) is installed; Separator main body (114) bottom is provided with entry to mixed solution (109), and the mixed solution of entry to mixed solution (109) enters flow velocity at more than 2m/s.Use Oil stain mixture separation system of the present invention can control the ratio of oily water separation, and have wide range of applications.

Description

一种油污混合物分离系统A kind of oil pollution mixture separation system

技术领域 technical field

本发明属于物质物理分离领域,具体涉及一种油污混合物分离系统,其适用于处理量大的石油化工行业中的油污混合物分离系统。 The invention belongs to the field of physical separation of substances, and in particular relates to an oil and dirt mixture separation system, which is suitable for the oil and dirt mixture separation system in the petrochemical industry with large processing capacity.

背景技术 Background technique

随着经济社会的发展,废水污染与日俱增,环境污染越来越受到人民的重视,而含油废水是众多废水中常见的,易于带来环境污染的工业和生活废水,危害严重,其处理在国内外均引起高度重视。目前在石油开采、石油炼制、石油化工、车辆清洗、机械制造、食品加工等过程中均会产生含油废水。油类污染物一旦进入水体立刻在水面扩散形成油膜,阻止水体从大气中复氧。油类迁移范围广、降解速度慢,最终影响人类健康。根据含油废水的来源和油类在水中的存在形式不同,可分为:浮油、分散油、乳化油和溶解油四大类。这些油类成分复杂,含有大量矿物油或植物油、乳化剂及其它有机物,乳化程度高、性质稳定、去除难度大。因此,如何高效进行油水分离以达到排放标准仍是一个难题。 With the development of economy and society, wastewater pollution is increasing day by day, and environmental pollution is getting more and more attention from the people. Oily wastewater is common in many wastewaters, and it is easy to cause environmental pollution. Industrial and domestic wastewater is seriously harmful, and its treatment is domestic and foreign have drawn great attention. At present, oily wastewater will be produced in the process of oil exploration, oil refining, petrochemical industry, vehicle cleaning, machinery manufacturing, food processing, etc. Once oily pollutants enter the water body, they immediately spread on the water surface to form an oil film, preventing the water body from reoxygenating from the atmosphere. Oil has a wide range of migration and slow degradation, which ultimately affects human health. According to the source of oily wastewater and the different forms of oil in water, it can be divided into four categories: floating oil, dispersed oil, emulsified oil and dissolved oil. These oils have complex components, containing a large amount of mineral oil or vegetable oil, emulsifiers and other organic substances, with high emulsification degree, stable properties and difficult removal. Therefore, how to efficiently separate oil and water to meet emission standards is still a difficult problem.

目前常用的处理含油废水的方法有重力分离法、离心分离法、气浮法、超滤法、过滤法、吸附法等。各处理法都有自己的优缺点。重力分离法和离心分离法只能分离水中的浮油和少量粒径较大的分散油,对于分散、乳化、溶解的油基本没有去除效果,因此通常作为含油废水的预处理装置。气浮法是根据浮力的作用原理,将乳化油和分散油的油珠粘附在大量的微气泡上,气泡由于自身的浮力将油珠带出水面,以实现固液分离过程。在实际应用中,由于废水水质不同,综合考虑处理效果和基建、运行费用等因素,所选的气浮工艺也有所不同。比较常见的是真空溶气气浮法和加压溶气气浮法,前者受各种因素限制目前使用很少,后者是最常采用的气浮法。气浮法一般和混凝技术相结合,可以去除水中大部分分散油,对乳化和溶解的油也有一定的去除率,因此是采用最多的含油废水处理方法。但现有传统气浮法处理含油废水存在几大缺点:浮油难处理,浮选时间停留较长;污泥易沉积在气浮池底,释放器频繁堵塞;在处理量大的时候,气浮设备占地面积大,投资费用高;设备整体性不完整,安装繁琐;对以乳化油和溶解油为主的含油废水,传统气浮的去除效果不佳。 At present, the commonly used methods for treating oily wastewater include gravity separation, centrifugal separation, air flotation, ultrafiltration, filtration, adsorption and so on. Each treatment has its own advantages and disadvantages. Gravity separation and centrifugal separation can only separate floating oil in water and a small amount of dispersed oil with large particle size, and basically have no removal effect on dispersed, emulsified, and dissolved oil, so they are usually used as pretreatment devices for oily wastewater. The air flotation method is based on the principle of buoyancy, the oil droplets of emulsified oil and dispersed oil are adhered to a large number of micro-bubbles, and the bubbles take the oil droplets out of the water surface due to their own buoyancy to achieve solid-liquid separation. In practical application, due to the different quality of wastewater, the selected air flotation process is also different considering the treatment effect, infrastructure and operation costs and other factors. The more common ones are the vacuum dissolved air flotation method and the pressurized dissolved air flotation method. The former is rarely used due to various factors, and the latter is the most commonly used air flotation method. Air flotation is generally combined with coagulation technology, which can remove most of the dispersed oil in water, and has a certain removal rate for emulsified and dissolved oil, so it is the most widely used oily wastewater treatment method. However, the existing traditional air flotation method has several disadvantages in the treatment of oily wastewater: oil slicks are difficult to handle, and the flotation time stays for a long time; sludge is easily deposited at the bottom of the air flotation tank, and the releaser is frequently blocked; The equipment occupies a large area and the investment cost is high; the integrity of the equipment is not complete and the installation is cumbersome; for the oily wastewater mainly emulsified oil and dissolved oil, the removal effect of traditional air flotation is not good.

超滤法近些年来主要用于浓缩乳化的矿物油。尽管超滤技术在一定条件下可以有效分离油水,但浓缩过程中产生的膜污染会导致膜通量严重衰减,跨膜压差大幅上升,膜寿命缩短,膜分离效率下降,能耗增大。大部分超滤膜在运行半年之后就进入频繁清洗期,不但消耗大量清洗剂,而且产生含油清洗液的二次污染问题。很少有超滤膜的使用寿命可以超过两年。由于膜 的投资通常较大,超滤除油系统的初期投资和运行成本都很高。此外超滤对浮油的耐受极低,一旦系统中由于预处理不善、浓缩析出等原因产生浮油,会对超滤膜带来不可逆转的破坏。 In recent years, ultrafiltration has been mainly used to concentrate emulsified mineral oil. Although ultrafiltration technology can effectively separate oil and water under certain conditions, the membrane fouling generated during the concentration process will lead to serious attenuation of membrane flux, a significant increase in transmembrane pressure difference, shortened membrane life, reduced membrane separation efficiency, and increased energy consumption. Most ultrafiltration membranes enter the frequent cleaning period after half a year of operation, which not only consumes a large amount of cleaning agent, but also causes secondary pollution of oily cleaning fluid. Few ultrafiltration membranes can last more than two years. Since the membrane investment is usually large, the initial investment and operating costs of the ultrafiltration oil removal system are high. In addition, ultrafiltration has very low tolerance to oil slicks. Once oil slicks occur in the system due to poor pretreatment, concentration and precipitation, etc., it will cause irreversible damage to the ultrafiltration membrane.

过滤和吸附法主要是用特殊滤料(核桃壳,吸油塑料)等来吸附水中微量的油。这种方法仅适用于废水中含油量很低的情况,否则会造成滤料很快饱和。频繁的清洗和再生会造成滤料的机械损伤,并且由于难以彻底反洗滤料会逐渐失效,需要经常进行补充,运行费用较高。且当油滴乳化时该方法的去除效果不佳。中国专利CN201342267Y公开的高效油水分离装置是这样实现的:包括分离容器和隔板,分离容器上部一侧设置水泵,分离容器顶部设置盖板,盖板上设有进水口,容器底部设置出水管,分离容器底部设置的隔水板、隔油板和定位板将分离容器依次分割为油、分离池和水池,油池顶部设置出油管;隔油板下端与分离池底部留有连通口;分离池底部设有气浮管,气浮管连接气浮泵。此分离装置只适用于水量比较小的含油废水,而且处理流程较长,废水流量及操作不能很好的控制。 Filtration and adsorption methods mainly use special filter materials (walnut shells, oil-absorbing plastics) to absorb trace amounts of oil in water. This method is only applicable when the oil content in the wastewater is very low, otherwise the filter material will be saturated very quickly. Frequent cleaning and regeneration will cause mechanical damage to the filter material, and because it is difficult to completely backwash the filter material will gradually lose its effectiveness, it needs to be replenished frequently, and the operating cost is high. And when the oil droplets are emulsified, the removal effect of this method is not good. The high-efficiency oil-water separation device disclosed in Chinese patent CN201342267Y is realized in the following way: it includes a separation container and a partition, a water pump is arranged on the upper side of the separation container, a cover plate is arranged on the top of the separation container, a water inlet is arranged on the cover plate, and a water outlet pipe is arranged at the bottom of the container. The water baffle plate, oil baffle plate and positioning plate set at the bottom of the separation container divide the separation container into oil, separation pool and water pool in turn, and the oil outlet pipe is set on the top of the oil pool; there is a communication port between the lower end of the oil baffle plate and the bottom of the separation pool; the separation pool An air flotation pipe is provided at the bottom, and the air flotation pipe is connected with an air flotation pump. This separation device is only suitable for oily wastewater with relatively small water volume, and the treatment process is long, and the wastewater flow and operation cannot be well controlled.

中国专利CN102225812A的油田回注水膜法处理,其基本流程包括:含油污水进入沉降罐沉降,除去部分大的悬浮固体和浮油,沉降后的水进入陶瓷膜超滤设备,在陶瓷膜设备内部循环过滤,透过膜的渗透液直接回注,未透过的继续沉降循环过滤。虽然该工艺简单,过滤精度高,但是运行一段时间后,油等污垢会堵塞膜管,导致膜通量大幅度衰减,不易顺利达到油水分离的结果。 Chinese patent CN102225812A oil field reinjection water membrane treatment, its basic process includes: oily sewage enters the settling tank to settle, remove part of the large suspended solids and slick oil, the settled water enters the ceramic membrane ultrafiltration equipment, and circulates inside the ceramic membrane equipment Filtration, the permeate that passes through the membrane is directly reinjected, and the permeate that is not permeated continues to settle and circulate and filter. Although the process is simple and the filtration accuracy is high, after a period of operation, oil and other dirt will block the membrane tube, resulting in a significant attenuation of the membrane flux, and it is difficult to achieve the result of oil-water separation smoothly.

基于旋流分离技术在含油废水处理中的广泛应用,近来很多水处理生产厂家都提出将传统气浮和旋流技术相结合的观点,取得了一些研究成果。 Based on the wide application of cyclone separation technology in the treatment of oily wastewater, many water treatment manufacturers have recently proposed the idea of combining traditional air flotation and cyclone technology, and achieved some research results.

美国专利US7157007中阐述了一种油、气、水三相分离装置,该装置为一个立式气浮分离罐,主要分为上、中、下三层,分别利用了旋流分离、粗粒化和气浮分离技术。位于罐上部的中间位置安装有一个内筒,含油废水从切向入口进入到内筒中产生旋流,在内筒中进行油水分离,油相直接进入撇油斗。从内筒底部流出的水流经过位于罐中部的聚结层时,分散的油滴在此聚集长大。部分大颗粒油滴会在浮力作用下,克服自身重力和主体相的下向流动而开始向上浮升,从而又去除了一部分油。在罐下部安装有喷射器,利用罐内顶部的气体和回流净化水在喷射器内剪切混合后,产生微小气泡,对从聚结层流下来的含油废水进行气浮处理。但聚结层的定期清理问题非常麻烦,同时整套设备的内部结构非常复杂,加工制造的成本较高。 U.S. Patent No. 7,157,007 describes a three-phase separation device for oil, gas, and water. The device is a vertical air flotation separation tank, which is mainly divided into upper, middle, and lower layers. and air flotation separation technology. An inner cylinder is installed in the middle of the upper part of the tank. The oily waste water enters the inner cylinder from the tangential inlet to generate swirling flow, and the oil and water are separated in the inner cylinder, and the oil phase directly enters the oil skimmer. When the water flowing from the bottom of the inner cylinder passes through the coalescing layer in the middle of the tank, the dispersed oil droplets gather and grow. Under the action of buoyancy, some large-particle oil droplets will overcome their own gravity and the downward flow of the main phase and start to float upward, thereby removing part of the oil. An ejector is installed at the lower part of the tank, and the gas at the top of the tank and the reflux purified water are sheared and mixed in the ejector to generate tiny bubbles to perform air flotation treatment on the oily wastewater flowing down from the coalescing layer. However, the regular cleaning of the coalescing layer is very troublesome, and the internal structure of the whole set of equipment is very complicated, and the cost of processing and manufacturing is relatively high.

美国专利US7144503中阐述了一种脱气浮选组合罐,罐内有一个圆柱状内筒和一个螺旋状入口导片,含油废水从罐上部的切向入口进入罐中形成旋流,同时气泡从水中析出。气泡和油滴在旋流的作用下被压至内筒壁,二者结合粘附后上升到罐顶,通过罐顶的油气出口排出。据专利权人的报道,此装置对含油废水的处理效果较好,并且成本及维护费用很低,比较适用于海上作业的石油生产平台或者浮式生产储卸油轮(FPSO)等空间要求比较严格的领域使用。但从 该专利所附的结构图上来看,上升到罐内顶部的油和气泡浮渣的外排存在着一些问题。尤其海上作业的石油生产平台或FPSO会因波、浪、流的作用而处于晃动状态,此时罐内部的液面难以保持稳定,从而致使该装置外排油和气泡浮渣中的含水量过高,从而严重影响了分离效果。 U.S. Patent No. 7,144,503 describes a combined degassing flotation tank. There is a cylindrical inner cylinder and a spiral inlet guide in the tank. The oily wastewater enters the tank from the tangential inlet on the upper part of the tank to form a swirling flow, and at the same time, the air bubbles flow from the Precipitate in water. Bubbles and oil droplets are pressed to the inner cylinder wall under the action of the swirling flow, and the two are combined and adhered to rise to the top of the tank, and are discharged through the oil and gas outlet on the top of the tank. According to the report of the patentee, this device has a good treatment effect on oily wastewater, and the cost and maintenance costs are very low. It is more suitable for offshore oil production platforms or floating production, storage and offloading (FPSO) and other space requirements. field use. But from the structural diagram attached to this patent, there are some problems in the oil and air bubble scum rising to the top of the tank. Especially the offshore oil production platform or FPSO will be in a sloshing state due to the action of waves, waves, and currents. At this time, the liquid level inside the tank is difficult to maintain stable, resulting in excessive water content in the oil discharged from the device and the air bubble scum. High, which seriously affects the separation effect.

由上述可见,目前现有的处理技术很难对含油污水取得良好的处理效果,特别是当含油污水的组分越来越复杂时,处理难度越来越大。 It can be seen from the above that the current existing treatment technologies are difficult to achieve good treatment effects on oily sewage, especially when the components of oily sewage become more and more complex, the treatment becomes more and more difficult.

发明内容 Contents of the invention

为了解决上述问题,本发明人针对针对上述现有技术的不足,经过多次设计和研究,提出了一种油污混合物分离系统。 In order to solve the above-mentioned problems, the inventor proposed a separation system for oil-contamination mixture after several designs and researches aimed at the deficiencies of the above-mentioned prior art.

依据本发明的技术方案,所提供的一种油污混合物分离系统主体为大致圆柱筒状的分离器主体114,主要部件包括螺旋槽筒体104、螺旋槽108、混合液射入口110、排水管113、颗粒物沉降板111和分离器主体114;在分离器主体114内侧设置有螺旋槽筒体104,紧贴于螺旋槽筒体104内壁安装有螺旋槽108;在分离器主体114下部设置有混合液入口109,混合液入口109的混合液进入流速在2m/s以上。 According to the technical solution of the present invention, the main body of the oil-contamination mixture separation system provided is a roughly cylindrical separator body 114, and the main components include a spiral groove cylinder 104, a spiral groove 108, a mixed liquid injection port 110, and a drain pipe 113 1. Particle settling plate 111 and separator main body 114; a spiral groove cylinder 104 is arranged inside the separator main body 114, and a spiral groove 108 is installed close to the inner wall of the spiral groove cylinder 104; a mixed liquid is arranged at the bottom of the separator main body 114 Inlet 109, the flow rate of the mixed liquid entering the mixed liquid inlet 109 is above 2m/s.

优选地,螺旋槽筒体104用于旋流分离,从混合液入口109射流进入的油水混合液沿螺旋槽108在槽内流动,比重较重的物质贴紧槽壁向上流,比重较轻的物质逐渐旋流到螺旋槽筒体104中间位置且慢慢上浮。 Preferably, the spiral groove cylinder 104 is used for cyclone separation, and the oil-water mixture jetted from the mixed liquid inlet 109 flows in the groove along the spiral groove 108, and the material with a heavier specific gravity clings to the groove wall and flows upward, while the material with a lighter specific gravity The material gradually swirls to the middle position of the spiral groove cylinder 104 and slowly floats up.

更优选地,螺旋槽108为实体结构固定在螺旋槽筒体104上,螺旋槽108的安装螺距H为75mm、槽深60mm; More preferably, the spiral groove 108 is a solid structure fixed on the spiral groove cylinder 104, the installation pitch H of the spiral groove 108 is 75 mm, and the groove depth is 60 mm;

优选地,槽深、螺距与混合液入口直径的比例关系1∶1∶1.25,即槽深:螺距:进口直径(混合液入口109直径)=1∶1∶1.25。 Preferably, the ratio of groove depth, screw pitch and mixed liquid inlet diameter is 1:1:1.25, that is, groove depth: screw pitch: inlet diameter (the diameter of mixed liquid inlet 109) = 1:1:1.25.

优选地,油污混合物分离系统还包括排水口101、排水调节阀门102、分离器油液聚集区103、排油调节阀门105,排水口101,其用于处理后的水从该排水口101排出;排水调节阀门102,其用于调节出水高度及出水流速,配合进水调节使用;分离器油液聚集区103,旋转分离出的油液上浮到此处区域聚集待外排;排油调节阀门105,其用于通过调节出油流量来控制出油的含水率,当油量较低时,关闭排油调节阀门105,当油量较高时,再打开排油调节阀门105。 Preferably, the oil-contamination mixture separation system also includes a drain 101, a drain regulating valve 102, a separator oil accumulation area 103, an oil discharge regulating valve 105, and a drain 101, which is used to discharge treated water from the drain 101; Drainage adjustment valve 102, which is used to adjust the water outlet height and water outlet flow rate, and is used in conjunction with water inlet adjustment; separator oil accumulation area 103, where the oil liquid separated by rotation floats up to this area to be collected and discharged; oil discharge adjustment valve 105 , which is used to control the water content of the oil by adjusting the oil flow rate. When the oil volume is low, the oil discharge regulating valve 105 is closed, and when the oil volume is high, the oil discharge regulating valve 105 is opened.

进一步地,油污混合物分离系统还包括排油口106,含水较低的油液从此处排出;大部分分离出的水从流水区107(缝隙)流到分离器主体下面。从流水区107(缝隙)流到分离器主体下面的水通过排水管113从排水口101排出。 Further, the oil-contamination mixture separation system also includes an oil discharge port 106, from which the oil with low water content is discharged; most of the separated water flows from the water flow area 107 (slit) to below the main body of the separator. The water flowing from the water flow area 107 (slit) to the underside of the separator main body is discharged from the drain port 101 through the drain pipe 113 .

更进一步地,混合液射入口110的管口与螺旋槽108呈切向接触。  Furthermore, the nozzle of the mixed liquid injection port 110 is in tangential contact with the spiral groove 108 . the

使用本发明的油污混合物分离系统能够控制油水分离的比例,即很好地控制分离油品中的含水量,具有现有技术中所无可比拟的油水分离效果。并且还可以适用于含有油污、沙石等物质的分离,即应用范围广泛。 The oil-stain mixture separation system of the present invention can control the ratio of oil-water separation, that is, well control the water content in the separated oil, and has an unparalleled oil-water separation effect in the prior art. And it can also be applied to the separation of substances containing oil, sand, etc., that is, it has a wide range of applications.

附图说明 Description of drawings

附图1是依据本发明的油污混合物分离系统的示意图。 Accompanying drawing 1 is the schematic diagram according to the separation system of oil-contaminated mixture of the present invention.

具体实施方式 Detailed ways

下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明的一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。另外地,不应当将本发明的保护范围仅仅限制至下述具体结构或部件或具体参数。 The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of them. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention. Additionally, the protection scope of the present invention should not be limited only to the following specific structures or components or specific parameters.

本发明的油污混合物分离系统,适用于来自于混合有水、落地油及地面泥砂的混合物分离,所述混合物简称为油水混合液。 The oil-stain mixture separation system of the present invention is suitable for the separation of mixtures mixed with water, ground oil, and ground mud and sand. The mixture is referred to as oil-water mixture for short.

如图1所示的油污混合物分离系统,其主体为大致圆柱筒状的分离器主体114,主要部件包括螺旋槽筒体104、螺旋槽108、混合液射入口110、排水管113、颗粒物沉降板111和分离器主体114。在分离器主体114内侧设置有螺旋槽筒体104,依附于螺旋槽筒体104内壁安装有螺旋槽108;在分离器主体114下部设置有混合液入口109,此处的混合液进入流速在2m/s以上,以保证水流在螺旋槽108内的旋流分离效果(混合液的温度保持在常温以上,进一步优选在20摄氏度以上)。 The oil-contamination mixture separation system shown in Figure 1, its main body is a roughly cylindrical separator body 114, and its main components include a spiral groove cylinder 104, a spiral groove 108, a mixed liquid injection port 110, a drain pipe 113, and a particle settling plate 111 and separator body 114. A spiral groove cylinder 104 is provided inside the separator main body 114, and a spiral groove 108 is attached to the inner wall of the spiral groove cylinder 104; a mixed liquid inlet 109 is arranged at the lower part of the separator main body 114, and the mixed liquid entering flow rate here is 2m /s or more to ensure the cyclone separation effect of the water flow in the spiral groove 108 (the temperature of the mixed liquid is kept above normal temperature, more preferably above 20 degrees Celsius).

此外,螺旋槽筒体104用于旋流分离,从混合液入口109射流进入的油水混合液沿螺旋槽108在槽内流动,比重较重的物质贴紧槽壁向上流,比重较轻的物质逐渐旋流到螺旋槽筒体104中间位置且慢慢上浮。螺旋槽108为实体结构固定在螺旋槽筒体104上,螺旋槽108的安装螺距H为75mm、槽深60mm;在优选实施例中,槽深、螺距与混合液入口直径的比例关系1∶1∶1.25,即槽深:螺距:进口直径(混合液入口109直径)=1∶1∶1.25,此时旋流效果最好。 In addition, the spiral groove cylinder 104 is used for cyclone separation. The oil-water mixture jetted from the mixed liquid inlet 109 flows in the groove along the spiral groove 108. The material with a heavier specific gravity clings to the groove wall and flows upward, while the material with a lighter specific gravity Gradually swirl to the middle position of the spiral groove cylinder 104 and slowly float up. The spiral groove 108 is fixed on the spiral groove barrel 104 as a solid structure, and the installation pitch H of the spiral groove 108 is 75 mm, and the groove depth is 60 mm; in a preferred embodiment, the ratio between the groove depth, the pitch and the diameter of the mixed liquid inlet is 1:1 : 1.25, i.e. groove depth: screw pitch: inlet diameter (109 diameters of the mixed solution inlet)=1: 1: 1.25, the swirling effect is the best now.

如图1所示的油污混合物分离系统还包括以下部件:排水口101,其用于处理后的水从该排水口101排出;排水调节阀门102,其用于调节出水高度及出水流速,配合进水调节使用;分离器油液聚集区103,旋转分离出的油液上浮到此处区域聚集待外排;排油调节阀门105,其用于通过调节出油流量来控制出油的含水率,当油量较低时,关闭排油调节阀门105,当油 量较高时,再打开排油调节阀门105;排油口106,含水较低的油液从此处排出;大部分分离出的水从流水区107(缝隙)流到分离器主体下面。从流水区107(缝隙)流到分离器主体下面的水通过排水管113从排水口101排出。 The oil-contamination mixture separation system as shown in Figure 1 also includes the following components: a drain 101, which is used to discharge the treated water from the drain 101; a drain regulating valve 102, which is used to adjust the height of the water outlet and the flow rate of the water outlet, and cooperate with the inlet Water adjustment is used; the oil accumulation area 103 of the separator, the oil liquid separated by rotation floats up to this area to be accumulated to be discharged; the oil discharge regulating valve 105 is used to control the water content of the oil by adjusting the oil flow, When the oil quantity is low, close the oil discharge regulating valve 105, and when the oil quantity is high, open the oil discharge regulating valve 105; the oil discharge port 106, the oil with low water content is discharged from here; most of the separated water It flows from the water flow area 107 (slit) to below the separator main body. The water flowing from the water flow area 107 (slit) to the underside of the separator main body is discharged from the drain port 101 through the drain pipe 113 .

优选地,混合液射入口110的管口与螺旋槽108呈切向接触,为后续进入的液体打下基础,使得全部都是射流切可以正常在螺旋槽内旋转。颗粒物沉降板111射流进入的混合液内如果有颗粒物例如砂子或石子等大块物质会沉降到板上,定期的打开颗粒物排出口112的排放阀门进行排放。(颗粒物排出口112用于沉降到颗粒物沉降板上的颗粒物从此口排出。定时排放或者每次使用结束后排放)。 Preferably, the nozzle of the mixed liquid injection port 110 is in tangential contact with the helical groove 108, laying a foundation for the subsequent entering liquid, so that all the jets can normally rotate in the helical groove. If there are particles such as sand or stones in the mixed solution entered by the particle settling plate 111, the particles will settle on the plate, and the discharge valve of the particle discharge port 112 is opened regularly to discharge. (The particulate matter discharge port 112 is used to discharge the particulate matter settled on the particulate matter settling plate from this port. It is discharged regularly or after each use).

在本发明中分离器主体114采用壁厚度为5mm的罐体,主体材质为优质的304(不锈钢型号)。 In the present invention, the separator main body 114 adopts a tank body with a wall thickness of 5mm, and the main body material is high-quality 304 (stainless steel type).

使用本发明的油污混合物分离系统,油水混合液通过高压泵经过混合液入口109进入到分离器主体内,从混合液射流口110喷射到螺旋槽108内,通过沿螺旋槽108的旋转,其中将轻质的物质旋流到螺旋槽筒体104的中间位置并不断上浮到分离器油液聚集区103处,然后通过排油口106排出。比重较大的水则始终靠近螺旋槽筒体的边缘位置,在旋流到螺旋槽筒体顶部后,从流水区107流到底部通过排水管113经过排水口101排出设备。其中排水调节阀门102可以调整出水的速率及油液的排出高度,其中排油调节阀门105可以调节出油的含水率。 Using the oil-stain mixture separation system of the present invention, the oil-water mixture enters the main body of the separator through the mixed liquid inlet 109 through the high-pressure pump, sprays from the mixed liquid jet port 110 into the spiral groove 108, and rotates along the spiral groove 108, wherein the Light matter swirls to the middle position of the spiral groove barrel 104 and continuously floats up to the oil accumulation area 103 of the separator, and then is discharged through the oil discharge port 106 . Water with a larger specific gravity is always close to the edge of the spiral groove cylinder. After swirling to the top of the spiral groove cylinder, it flows from the water flow area 107 to the bottom through the drain pipe 113 and is discharged from the device through the drain port 101. Wherein the drain regulating valve 102 can adjust the rate of water discharge and the discharge height of the oil, and the oil discharge regulating valve 105 can adjust the water content of the oil.

以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到的变化或替换,都应涵盖在本发明的保护范围之内。本领域普通的技术人员可以理解,在不背离所附权利要求定义的本发明的精神和范围的情况下,可以在形式和细节中做出各种各样的修改。 The above is only a preferred embodiment of the present invention, but the scope of protection of the present invention is not limited thereto. Any person skilled in the art within the technical scope disclosed in the present invention can easily think of changes or Replacement should be covered within the protection scope of the present invention. It will be understood by those of ordinary skill in the art that various changes in form and details may be made without departing from the spirit and scope of the present invention as defined by the appended claims.

Claims (5)

1. an Oil stain mixture separation system, its main body is the separator main body (114) of roughly cylindrical tube shape, and major parts comprises spiral slot cylindrical shell (104), spiral slot (108), mixed solution entry portal (110), water shoot (113), particulate matter settlement plate (111) and separator main body (114); Separator main body (114) inner side is provided with spiral slot cylindrical shell (104), is close to spiral slot cylindrical shell (104) inwall and spiral slot (108) is installed; Separator main body (114) bottom is provided with entry to mixed solution (109), and the mixed solution of entry to mixed solution (109) enters flow velocity at more than 2m/s;
Oil stain mixture separation system also comprises water port (101), draining regulated valve (102), separator fluid accumulation area (103), oil extraction regulated valve (105), water port (101), its for the treatment of after water discharge from this water port (101); Draining regulated valve (102), it is for adjusting water outlet height and Water discharge flow speed, coordinates water inlet to regulate and uses; Separator fluid accumulation area (103), the fluid that rotating separation goes out floats to region clustering herein and treats outer row; Oil extraction regulated valve (105), it is for by regulating fuel-displaced flow to control fuel-displaced water ratio, when oil mass is lower, closes oil extraction regulated valve (105), when oil mass is higher, then opens oil extraction regulated valve (105).
2. Oil stain mixture separation system according to claim 1, it is characterized in that: spiral slot cylindrical shell (104) is for cyclonic separation, the oil-water mixture entered from entry to mixed solution (109) jet flows in groove along spiral slot (108), the heavier material of proportion is adjacent to cell wall to upper reaches, and the lighter material of proportion gradually eddy flow is waited a moment to spiral slot cylindrical shell (104) mid-way slow floating.
3. Oil stain mixture separation system according to claim 2, it is characterized in that: spiral slot (108) is fixed on spiral slot cylindrical shell (104) for entity structure, and the installation pitch H of spiral slot (108) is 75mm, groove depth 60mm.
4. Oil stain mixture separation system according to claim 1, is characterized in that: Oil stain mixture separation system also comprises oil discharge outlet (106), and moisture lower fluid is discharged from here; The isolated water of major part flows to below separator main body from flowing water district (107) (gap); The water flow to below separator main body from flowing water district (107) (gap) is discharged from water port (101) by water shoot (113).
5. according to arbitrary described Oil stain mixture separation system of claim 2-4, it is characterized in that: the mouth of pipe and the spiral slot (108) of mixed solution entry portal (110) are tangentially contact.
CN201410033548.6A 2014-01-24 2014-01-24 A kind of Oil stain mixture separation system Expired - Fee Related CN103754986B (en)

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