CN205095472U - Subside and remove oil tank and extraction water processing system - Google Patents
Subside and remove oil tank and extraction water processing system Download PDFInfo
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Abstract
本实用新型公开了沉降除油罐及采出水处理系统,沉降除油罐包括罐体,罐体内设有中心管柱、配水室、集油槽和设于罐体底部排泥装置;中心管柱设于罐体内并至少下端密封,中心管柱的上部连通有第一出水管,下部连通有多个集水管路,集水管路上设有入水口;配水室连接有多个配水管路和第一进水管,配水管路设有出水口;集油槽围绕罐体的内壁形成环形。本实用新型的沉降除油罐采用立式竖流式储罐,设置均匀的集配水系统,在竖流状态下使水中的油、水和悬浮固体因密度不同而自然分离。本实用新型的采出水处理系统由一级处理的沉降除油罐和二级处理的化学调整旋流反应分离装置组成,采出水经过两级处理后,出水含油和悬浮物可达到15mg/L以内。
The utility model discloses a subsidence oil removal tank and a produced water treatment system. The subsidence oil removal tank includes a tank body, and the tank body is provided with a central pipe column, a water distribution chamber, an oil collection tank and a mud discharge device at the bottom of the tank body; In the tank and at least the lower end is sealed. The upper part of the central column is connected with the first water outlet pipe, and the lower part is connected with multiple water collection pipes. The water collection pipes are provided with water inlets; the water distribution chamber is connected with multiple water distribution pipes and the first water inlet. The water pipe and the water distribution pipeline are provided with a water outlet; the oil collecting tank forms a ring around the inner wall of the tank body. The settling oil removal tank of the utility model adopts a vertical vertical flow storage tank, and a uniform water collection and distribution system is set up, so that oil, water and suspended solids in the water are naturally separated due to different densities in the vertical flow state. The produced water treatment system of the utility model is composed of a subsidence oil removal tank for primary treatment and a chemically adjusted cyclone reaction separation device for secondary treatment. After two-stage treatment, the produced water contains oil and suspended matter within 15 mg/L. .
Description
技术领域technical field
本实用新型属于油田开发地面工程稠油采出水处理技术领域,特别是应用于国内外SAGD(SteamAssistedGravityDrainage蒸汽辅助重力泄油)稠油开发中产生的高温、低油水密度差和高乳化度的采出水处理中。The utility model belongs to the technical field of heavy oil produced water treatment for surface engineering of oil field development, and is particularly applied to produced water with high temperature, low oil-water density difference and high emulsification degree produced in the development of SAGD (Steam Assisted Gravity Drainage) heavy oil at home and abroad. Processing.
背景技术Background technique
目前国际通行的油田采出水处理技术主要为重力沉降除油、气浮、旋流除油器、过滤等除油工艺,出水再进行除盐和软化处理,然后用于锅炉给水。由于稠油开采的采出水温度较高,不适于利用生物法处理,主要使用的物理和物理化学处理方法有:At present, the internationally accepted oilfield produced water treatment technologies mainly include gravity sedimentation deoiling, air flotation, cyclone degreaser, filtration and other deoiling processes. The effluent is desalinated and softened before being used as boiler feed water. Due to the high temperature of produced water in heavy oil exploitation, it is not suitable for biological treatment. The main physical and physicochemical treatment methods are:
物理法:物理法主要利用物理原理分离水中的油、固体悬浮颗粒等杂质,物理法主要包括重力沉降分离法、旋流除油器去除法、平流式除油池分离以及过滤法。Physical method: The physical method mainly uses physical principles to separate impurities such as oil and solid suspended particles in water. The physical method mainly includes gravity sedimentation separation method, cyclone degreaser removal method, advection degreasing tank separation and filtration method.
物理化学法:对于采出水中存在分散油、乳化油及以分散态、溶解态、胶体物质存在的悬浮物时,不能单独采用物理法去除,需要进行化学和物理结合的方法去除。主要包括混凝沉淀、气浮法、化学药剂反应池等方法。Physical and chemical methods: When there are dispersed oil, emulsified oil, and suspended solids in the form of dispersed, dissolved, and colloidal substances in the produced water, they cannot be removed by physical methods alone, and a combination of chemical and physical methods is required. It mainly includes coagulation sedimentation, air flotation method, chemical agent reaction tank and other methods.
一般采出水处理系统的进水的含油为2000ppm,悬浮物为300ppm,系统总出水要求为含油和悬浮物均低于5ppm,采出水处理系统常见工艺流程为除油罐+气浮机+过滤器,针对于每段流程的处理设施略有不同。目前存在问题主要有两个方面,一是作为第一级的除油罐处理效率有待进一步提升,二是需要应用更加高效稳定的处理工艺来弥补单纯物理法的不足,现有技术特点及不足之处如下:Generally, the oil content of the influent of the produced water treatment system is 2000ppm, and the suspended solids are 300ppm. The total output water requirement of the system is that both the oil content and suspended solids are lower than 5ppm. The common process flow of the produced water treatment system is oil removal tank + air flotation machine + filter , the processing facilities for each process are slightly different. At present, there are mainly two problems. One is that the treatment efficiency of the first-stage oil removal tank needs to be further improved. The other is that a more efficient and stable treatment process needs to be applied to make up for the shortcomings of the pure physical method. The characteristics and shortcomings of the existing technology as follows:
目前除油罐作为除油工艺的第一级处理设施,接受了含油2000ppm,悬浮物为300ppm的采出水原水水质,设计出水指标一般为含油小于300ppm、悬浮物小于150ppm,除油罐的设计除油率一般达90%,悬浮物去除率达50%,但投资小于后端气浮和过滤器,属于除油系统达标运行首要关注因素。因除油罐出水不达标而造成后端气浮和过滤设备影响总系统出水水质,进而对后端的MVC(降膜蒸发除盐)等除盐设施带来破坏,并将导致高额的维修费用。因此保证处于整个除油工艺和除盐工艺最前端作为第一级处理设施的除油罐的处理效果是减轻后端处理压力、保证后端稳定运行的关键所在。目前国外常用的除油罐主要有以下两种形式:At present, the oil removal tank is used as the first-level treatment facility of the oil removal process. It accepts the raw water quality of the produced water with an oil content of 2000ppm and a suspended solid of 300ppm. The oil rate is generally up to 90%, and the removal rate of suspended solids is up to 50%, but the investment is less than the back-end air flotation and filter, which is the primary concern for the standard operation of the oil removal system. The water quality of the total system effluent is affected by the back-end air flotation and filtration equipment due to the substandard effluent of the oil removal tank, which will damage the desalination facilities such as the MVC (falling film evaporation desalination) at the back end, and will lead to high maintenance costs . Therefore, ensuring the treatment effect of the oil removal tank at the forefront of the entire oil removal process and desalination process as the first-level treatment facility is the key to reducing the pressure of the back-end treatment and ensuring the stable operation of the back-end. At present, there are two main types of degreasing tanks commonly used abroad:
平流式除油罐:该除油罐为水平流式,罐内部安装有竖直挡板,将罐体分割为几部分,相邻部分设过流通道,整体形成一个水平折流式除油罐。由于分隔开几部分,因此在有限的罐圆周截面积内形成较长的过流通道,水流流过时,油珠由于密度小于水而上浮至液面上部,从进水口至出水口,较大粒径的油珠依次完成上浮全过程,在除油罐顶部被收集排出,较小的油珠由于上浮速度小未能完成上浮去除过程而随水流进入下一级流程。Horizontal flow degreasing tank: the degreasing tank is a horizontal flow type, and a vertical baffle is installed inside the tank, which divides the tank body into several parts, and the adjacent parts are provided with flow passages, forming a horizontal baffle type degreasing tank as a whole . Due to the separation of several parts, a longer flow channel is formed in the limited circumferential cross-sectional area of the tank. When the water flows through, the oil droplets float up to the upper part of the liquid surface because the density is lower than that of water. From the water inlet to the water outlet, the larger The oil droplets with particle size complete the whole process of floating in turn, and are collected and discharged at the top of the oil removal tank. The smaller oil droplets fail to complete the floating removal process due to the small floating speed and enter the next stage of the process with the water flow.
普通竖流除油罐:该除油罐为立式除油罐,水流总体来说为竖直流,进水通过罐中心筒上的出水箱出水,水箱出水采用管路出水,水流经配水管分配后垂直向下流,最后进入罐底收水口收集后排出罐外。Ordinary vertical flow degreasing tank: the degreasing tank is a vertical degreasing tank, and the water flow is generally vertical. After distribution, it flows vertically downward, and finally enters the water collection port at the bottom of the tank to be collected and then discharged out of the tank.
这些用于采出水的除油罐只考虑了油水密度差带来的油珠上浮效应,但未从油珠粗粒化改善、提高上浮速度方面做根本改进,且对来水波动性适应性较差,需针对均匀集配水、改善罐内水流态、改进排泥方式等方面进行优化These oil removal tanks for produced water only take into account the floating effect of oil droplets brought about by the difference in density between oil and water, but have not made fundamental improvements in terms of coarse-grained oil droplets and increased floating speed, and are less adaptable to incoming water fluctuations. Poor, it needs to be optimized for uniform collection and distribution of water, improvement of water flow state in the tank, improvement of mud discharge method, etc.
另一方面,国外大多数油田采出水处理工艺较单一,主要为物理流程即气浮流程,对来水波动性、水质差异性适应性较差,由于前段除油罐和气浮出水的不稳定造成过滤器滤料污染而停用的情况时有发生,且对于系统腐蚀、结垢没有专门的解决措施,药剂成本较高,且目前使用的药剂混凝反应沉降工艺不成熟,不适应油田采出水处理工程建设高效处理、水质稳定达标的要求。On the other hand, the produced water treatment process of most foreign oilfields is relatively simple, mainly the physical process, namely the air flotation process, which has poor adaptability to the fluctuation of incoming water and the difference in water quality. The situation that the filter material is polluted and shut down occurs from time to time, and there is no special solution to system corrosion and scaling, the cost of chemicals is high, and the coagulation reaction and sedimentation process of chemicals currently used is immature and not suitable for oilfield production. The construction of effluent treatment projects requires efficient treatment and stable water quality up to the standard.
综上所述,现有技术中采出水处理主要存在以下几个问题:In summary, the produced water treatment in the prior art mainly has the following problems:
1)除油罐方面:1) In terms of oil removal tank:
a、集水配水不均匀:以上两种除油罐均采用进水口大股进水的方式,水流进入罐中时扰动较大,没有均匀配水会影响水的流态,在水中形成扰流,扰动水流多个方向的剪切力使得油珠除了上浮力带来的上浮速度外还有其他方向的速度,在有限的时间内影响了上浮高度,因此在设计除油率的要求下,提高了停留时间的要求。且没有均匀配水也减小了对来水冲击的适应能力,容易造成团聚状原油未能分配开来就进入除油罐,由于沉降能力不足而直接进入下端流程,对下端设备造成污染。除油后的水由于未能均匀收集,易形成短流,出水段出水口附近流态不好的地方易聚集污油和污泥,带来出水水质波动。a. Uneven water collection and water distribution: The above two oil removal tanks adopt the method of large water inlet at the water inlet. When the water flow enters the tank, the disturbance is relatively large. Without uniform water distribution, the flow state of the water will be affected, and turbulence will be formed in the water. The shear force in multiple directions of the disturbed water flow causes the oil droplets to have speeds in other directions besides the buoyancy brought about by the buoyancy force, which affects the floating height in a limited time. Therefore, under the requirements of the designed oil removal rate, the increase dwell time requirements. Moreover, the lack of uniform water distribution also reduces the ability to adapt to the impact of incoming water. It is easy to cause agglomerated crude oil to enter the oil removal tank without being distributed, and directly enter the lower-end process due to insufficient settling capacity, causing pollution to the lower-end equipment. The water after degreasing is not uniformly collected, so it is easy to form a short flow, and the place with poor flow state near the outlet of the water outlet is easy to accumulate dirty oil and sludge, resulting in fluctuations in the quality of the effluent.
b、无高效的排泥设施:目前这两种除油罐内无专门排泥设施,上游带来的泥沙、有机物胶体和水中沉积污泥均自然沉降至罐底,目前设置排污口接清罐车定期清罐操作的方式去除,当污泥较少时只排出部分罐底水,当沉泥较大时清全罐。这种操作方式一方面不能全部去除罐底污泥,在清罐口另一侧的污泥依然会堆积,另一方面清全罐时需要停产,或除油罐一般要建两座,增加投资。b. No efficient sludge discharge facilities: At present, there are no special sludge discharge facilities in these two types of oil removal tanks. The sediment, organic colloids and sludge deposited in water from the upstream will naturally settle to the bottom of the tank. The tank truck is removed by regular tank cleaning operation. When there is less sludge, only part of the bottom water of the tank is discharged, and when the sludge is large, the whole tank is cleaned. On the one hand, this operation method cannot remove all the sludge at the bottom of the tank, and the sludge on the other side of the tank cleaning port will still accumulate. On the other hand, when cleaning the tank, it needs to stop production, or generally two oil removal tanks need to be built, which increases investment. .
c、平流式除油罐流态不理想。由于水和油珠为同向流动,油珠除由于浮力带来的上浮速度外,还受水流剪切力左右而有一个水平前进速度,因此油珠实际为抛物线上浮轨迹。因水流流速远大于上浮流速,使得在有限的上浮高度内,水平推进轨迹较长,对流道长度要求较高,在上升高度不变的情况下,增大了除油罐截面积,有效停留时间相应延长。c. The flow state of the advection degreasing tank is not ideal. Because the water and the oil droplet flow in the same direction, the oil droplet has a horizontal forward speed due to the shear force of the water flow in addition to the buoyancy brought about by the buoyancy force, so the oil droplet actually follows a parabolic floating track. Because the water flow velocity is much greater than the floating velocity, within the limited floating height, the horizontal propulsion trajectory is longer, and the requirements for the length of the flow channel are higher. In the case of the same rising height, the cross-sectional area of the oil removal tank is increased, and the effective residence time is increased. extended accordingly.
2)工艺流程方面:现有除油罐和气浮流程不能确保出水水质稳定合格,对过滤器压力较大。部分油田原油脱水效果不良,使污水油含量大,冲击污水处理设施,前端一级处理的重力除油和二级处理的气浮和旋流除油器出水不稳定。随着多种二次、三次采油技术的大范围推广,回收水掺入采出水处理系统处理,使采出水粘度增加,乳化油更加稳定,油水密度差小,气浮和旋流分离器难以达到理想效果。在设备方面普遍存在小颗粒悬浮物及微小粒径油的去除效率低的缺陷,以上多种原因均将处理压力转嫁到过滤器,造成滤料堵塞影响处理效果,并因前端来油量不合格而使滤料污染无法运行的情况时有发生。2) In terms of process flow: the existing oil removal tank and air flotation process cannot ensure stable and qualified effluent water quality, and the pressure on the filter is relatively high. The dehydration effect of crude oil in some oilfields is not good, so that the sewage oil content is large, impacting sewage treatment facilities, the gravity degreasing of the front-end primary treatment and the air flotation and cyclone degreaser of the secondary treatment are unstable. With the large-scale promotion of various secondary and tertiary oil recovery technologies, the recovered water is mixed with the produced water treatment system for treatment, which increases the viscosity of the produced water, makes the emulsified oil more stable, and has a small oil-water density difference, which is difficult to achieve with air flotation and cyclone separators. Ideal effect. In terms of equipment, there are generally defects in the removal efficiency of small suspended solids and fine particle size oil. The above reasons will transfer the processing pressure to the filter, causing the blockage of the filter material to affect the processing effect, and the amount of oil coming from the front end is unqualified. However, the situation that the filter material is polluted and unable to operate occurs from time to time.
3)采出水处理系统无有效离子平衡措施,腐蚀结垢问题严重。由于除油罐+气浮流程仅对采出水进行物理法处理,对水中钙镁等成垢离子不能有效降低,除油系统结垢问题突出,除垢剂加药成本大。3) The produced water treatment system has no effective ion balance measures, and the problem of corrosion and scaling is serious. Since the deoiling tank + air flotation process only performs physical treatment on the produced water, the scaling ions such as calcium and magnesium in the water cannot be effectively reduced, the scaling problem of the deoiling system is prominent, and the cost of adding descaling agents is high.
4)化学处理工艺亟待优化。鉴于物理流程对出水稳定性和防垢能力的不足,部分油田开始采用化学药剂反应池的工艺来解决上述问题,但由于应用时间较短,仅为化学药剂反应絮凝池的工艺,没有形成有效、集成化的加药反应分离工艺和设备。絮凝反应池造价高、施工困难。用化学混凝沉降的方法处理含油污水时,需要投加大量的净水药剂,从而形成大量的絮体,絮体沉降后成为污泥,直接被沉降后排出,净水药剂的性能没有完全利用,并且形成的絮体松散,污泥沉降性能差,不利于后续污泥的脱水处理,因此工作效率低,工作质量差、成本高。4) The chemical treatment process needs to be optimized urgently. In view of the insufficiency of the physical process on the stability of the effluent and the anti-scaling ability, some oilfields have begun to use the process of chemical agent reaction tanks to solve the above problems. Integrated dosing reaction separation process and equipment. The flocculation reaction tank is expensive and difficult to construct. When chemical coagulation and sedimentation are used to treat oily sewage, it is necessary to add a large amount of water purification agents to form a large number of flocs. After the flocs settle, they become sludge and are directly discharged after sedimentation. The performance of water purification agents is not fully utilized. , and the formed flocs are loose, and the sludge settling performance is poor, which is not conducive to the subsequent sludge dehydration treatment, so the work efficiency is low, the work quality is poor, and the cost is high.
实用新型内容Utility model content
鉴于现有技术中存在的上述问题,本实用新型所要解决的技术问题是提供一种能够有效的去除采出水中的油和悬浮固体的沉降除油罐。In view of the above-mentioned problems in the prior art, the technical problem to be solved by the utility model is to provide a settling oil removal tank capable of effectively removing oil and suspended solids in produced water.
为了解决上述技术问题,本实用新型采用了如下技术方案:沉降除油罐,包括罐体,In order to solve the above technical problems, the utility model adopts the following technical scheme: the subsidence degreasing tank, including the tank body,
所述罐体内设置有中空的中心管柱、配水室、集油槽和排泥装置;The tank is provided with a hollow central pipe column, a water distribution chamber, an oil collection tank and a mud discharge device;
所述中心管柱竖直设于所述罐体内并至少下端密封,所述中心管柱的上部连通有延伸至所述罐体外的第一出水管,下部连通有位于所述罐体内的多个集水管路,所述集水管路上设置有入水口;The central pipe column is vertically arranged in the tank body and at least the lower end is sealed, the upper part of the central pipe column communicates with the first water outlet pipe extending to the outside of the tank body, and the lower part communicates with a plurality of outlet pipes located in the tank body. A water collection pipeline, the water collection pipeline is provided with a water inlet;
所述配水室连接有位于所述罐体内的多个配水管路和延伸至所述罐体外的第一进水管,所述配水管路上设置有出水口;The water distribution chamber is connected with a plurality of water distribution pipelines located in the tank and a first water inlet pipe extending to the outside of the tank, and a water outlet is arranged on the water distribution pipeline;
所述集油槽围绕所述罐体的内壁形成环形;The oil sump forms a ring around the inner wall of the tank;
所述排泥装置设置于所述罐体内的底部。The mud discharge device is arranged at the bottom of the tank.
作为优选,每个所述配水管路包括垂直于所述中心管柱的一根配水干管、垂直连接于所述配水干管上的一根配水主支管和连接在所述配水主支管上的多根配水分支管,每根所述配水分支管上分别具有所述出水口。Preferably, each of the water distribution pipelines includes a main water distribution pipe perpendicular to the central column, a main water distribution branch vertically connected to the main water distribution pipe, and a main branch pipe connected to the main water distribution pipe. A plurality of water distribution branch pipes, each of which has the water outlet respectively.
作为优选,所述出水口呈喇叭状并开口向上。Preferably, the water outlet is trumpet-shaped and opens upward.
作为优选,所述配水室套设在所述中心管柱上,多个所述配水管路的多根所述配水干管均布于所述配水室上。Preferably, the water distribution chamber is sleeved on the central pipe column, and the plurality of water distribution main pipes of the plurality of water distribution pipelines are evenly distributed on the water distribution chamber.
作为优选,每个所述集水管路包括垂直于所述中心管柱的一根集水干管、垂直连接于所述集水干管上的一根集水主支管和连接在所述集水主支管上的多根集水分支管,每根所述集水分支管上分别具有所述入水口。Preferably, each of the water collection pipelines includes a main water collection pipe perpendicular to the central pipe column, a main water collection branch pipe vertically connected to the main water collection pipe, and a main branch pipe connected to the main water collection pipe There are a plurality of water collection branch pipes on the water collection branch pipe, and each of the water collection branch pipes has the water inlet respectively.
作为优选,所述入水口呈喇叭状并开口向下。Preferably, the water inlet is trumpet-shaped and opens downward.
本实用新型同时公开一种采出水处理系统,包括除油罐和化学调整旋流反应分离装置,所述除油罐为上述的沉降除油罐,所述第一出水管连接至所述化学调整旋流反应分离装置。The utility model also discloses a produced water treatment system, which includes an oil removal tank and a chemical adjustment swirl reaction separation device, the oil removal tank is the above-mentioned settlement oil removal tank, and the first water outlet pipe is connected to the chemical adjustment Cyclone reaction separation device.
作为优选,所述化学调整旋流反应分离装置为旋流反应分离罐,所述旋流反应分离罐包括罐体和纵向置于所述罐体内的旋流反应中心筒,所述旋流反应中心筒的下端与所述罐体的内腔相连通,所述旋流反应中心筒从上到下依次分为第一级旋流反应段、第二级旋流反应段和第三级旋流反应段;As a preference, the chemical adjustment cyclone reaction separation device is a cyclone reaction separation tank, the cyclone reaction separation tank includes a tank body and a cyclone reaction center tube vertically placed in the tank body, the cyclone reaction center The lower end of the cylinder communicates with the inner cavity of the tank, and the swirl reaction central cylinder is divided into the first-stage swirl reaction section, the second-stage swirl reaction section and the third-stage swirl reaction section from top to bottom. part;
所述罐体上固定连接有伸入到所述第一级旋流反应段内的第二进水管、伸入到所述第二级旋流反应段内的第二净水剂管和伸入到所述第三级旋流反应段内的絮凝剂管,所述第二进水管上连通有第一净水剂管;The tank body is fixedly connected with a second water inlet pipe extending into the first-stage cyclone reaction section, a second water purification agent pipe extending into the second-stage cyclone reaction section, and a To the flocculant pipe in the third-stage cyclone reaction section, the second water inlet pipe is connected with the first water purification agent pipe;
所述罐体内的上部固定设置有集水管和位于所述集水管的上方的集油管,所述集水管上开设有进水口,所述集水管上连接有伸出所述罐体外的第二出水管;所述集油管上开设有进油口,所述集油管上连接有伸出所述罐体外的出油管;The upper part of the tank is fixed with a water collecting pipe and an oil collecting pipe above the water collecting pipe. The water collecting pipe is provided with a water inlet, and the water collecting pipe is connected with a second outlet extending out of the tank. Water pipe; the oil collecting pipe is provided with an oil inlet, and the oil collecting pipe is connected with an oil outlet pipe protruding from the outside of the tank;
所述罐体的底部连接有排泥管;A mud discharge pipe is connected to the bottom of the tank;
所述第一出水管与所述第二进水管连接。The first water outlet pipe is connected to the second water inlet pipe.
作为优选,所述集水管和集油管均为环形,所述集水管和集油管均套在所述旋流反应中心筒外,所述进水口为均布于所述集水管上的多个,所述进油口为均布于所述集油管上的多个。Preferably, the water collecting pipe and the oil collecting pipe are ring-shaped, and both the water collecting pipe and the oil collecting pipe are set outside the swirl reaction central cylinder, and the water inlets are multiple evenly distributed on the water collecting pipe, The oil inlets are multiple evenly distributed on the oil collecting pipe.
作为优选,所述第二进水管的轴线方向与所述旋流反应中心筒的内壁相切。Preferably, the axial direction of the second water inlet pipe is tangent to the inner wall of the cyclone reaction center cylinder.
作为优选,所述化学调整旋流反应分离装置包括旋流反应器和除渣分离罐;As a preference, the chemical adjustment cyclone reaction separation device includes a cyclone reactor and a slag removal separation tank;
所述旋流反应器包括罐体,所述罐体内设置有用于将所述罐体分隔为位于下部的第一级反应腔和位于上部的第二级反应腔的隔板;The cyclone reactor includes a tank body, and the tank body is provided with a partition for separating the tank body into a first-stage reaction chamber located at the lower part and a second-stage reaction chamber located at the upper part;
对应所述第一级反应腔的罐体上开设有进水口,所述进水口内设置有伸入所述第一级反应腔内的第三进水管;A water inlet is opened on the tank body corresponding to the first-stage reaction chamber, and a third water inlet pipe extending into the first-stage reaction chamber is arranged in the water inlet;
对应所述第二级反应腔的罐体上开设有净水药剂投加口和出水口,所述净水药剂投加口内设置有伸入所述第二级反应腔内的药剂投加管,所述出水口内设置有伸入所述第二级反应腔内的第三出水管,所述药剂投加管位于所述第二级反应腔的下部,所述第三出水管位于所述第二级反应腔的上部;The tank body corresponding to the second-stage reaction chamber is provided with a water purification agent dosing port and a water outlet, and the water purification agent dosing port is provided with a drug dosing pipe extending into the second-stage reaction chamber, The water outlet is provided with a third water outlet pipe extending into the second-stage reaction chamber, the drug dosing pipe is located at the lower part of the second-stage reaction chamber, and the third water outlet pipe is located at the second The upper part of the reaction chamber;
所述隔板上开设有通孔,所述通孔通过连接管与所述药剂投加管连通;A through hole is opened on the partition, and the through hole communicates with the medicament dosing pipe through a connecting pipe;
所述罐体的底部设置有排污放空管;The bottom of the tank is provided with a sewage discharge pipe;
所述第三进水管与所述第一出水管连接。The third water inlet pipe is connected to the first water outlet pipe.
作为优选,所述除渣分离罐为喷雾除渣分离罐,所述喷雾除渣分离罐包括罐体、中心旋流筒、喷雾除渣装置、收油装置、排泥装置和收水装置;Preferably, the slag removal separation tank is a spray slag removal separation tank, and the spray slag removal separation tank includes a tank body, a central cyclone, a spray slag removal device, an oil collection device, a mud discharge device and a water collection device;
所述中心旋流筒位于所述罐体内且上端敞口,下端与所述罐体固定并密封,所述中心旋流筒与所述罐体之间形成环腔,所述中心旋流筒的下部具有至少一个与所述罐体的内腔相连通的连通口,所述中心旋流筒的中部连接有第四进水管,所述第四进水管的一端位于所述中心旋流筒内,另一端与所述第三出水管连接;The central swirl cylinder is located in the tank with an open upper end, and the lower end is fixed and sealed with the tank body. An annular cavity is formed between the central swirl cylinder and the tank body. The center swirl cylinder The lower part has at least one communication port communicating with the inner cavity of the tank body, the middle part of the central swirl tube is connected with a fourth water inlet pipe, and one end of the fourth water inlet pipe is located in the central swirl tube, The other end is connected to the third outlet pipe;
所述喷雾除渣装置设置于所述中心旋流筒的上部外侧;The spray slag removal device is arranged outside the upper part of the central cyclone;
所述收油装置设置于所述中心旋流筒上端对应的罐体内壁上;The oil collector is arranged on the inner wall of the tank corresponding to the upper end of the central cyclone;
所述排泥装置设置于所述罐体底部对应所述连通口的位置;The mud discharge device is arranged at the bottom of the tank corresponding to the communicating port;
所述收水装置包括安装于所述罐体外侧上部的外挂水箱和收水管,所述收水管包括收水环管和L状引管,所述收水环管位于罐体内的中部并套于所述中心旋流筒外;所述L状引管的一端与所述收水环管连通,另一端穿出所述罐体并伸入所述外挂水箱内,所述外挂水箱内连接有第四出水管。The water collection device includes an external water tank and a water collection pipe installed on the outer upper part of the tank body. The water collection pipe includes a water collection ring pipe and an L-shaped guide pipe. The water collection ring pipe is located in the middle of the tank body and is placed on the Outside the central swirl tube; one end of the L-shaped guide pipe communicates with the water collection ring pipe, and the other end passes through the tank body and extends into the external water tank. The external water tank is connected with a second Four outlet pipes.
作为优选,所述外挂水箱内设置有水位调节器,所述水位调节器包括外筒、调节内筒、丝杆、安装架、手轮和手轮座,所述外筒固定于外挂水箱内的底部,所述L状引管位于所述外筒内,所述第四出水管位于所述外筒的外部;所述调节内筒套装于所述外筒内并能够上下移动,且所述调节内筒的外壁与所述外筒的内壁保持密封,所述调节内筒上固定有所述丝杆,所述安装架位于所述外筒的上方,所述手轮座的下端安装于所述安装架上,所述手轮座的上端安装所述手轮,所述手轮中部安装有能够使所述丝杆穿过的螺母。As a preference, a water level regulator is provided in the external water tank, and the water level regulator includes an outer cylinder, an inner cylinder for adjustment, a screw rod, a mounting frame, a handwheel and a handwheel seat, and the outer cylinder is fixed on the inner cylinder of the external water tank. bottom, the L-shaped guide pipe is located in the outer cylinder, the fourth outlet pipe is located outside the outer cylinder; the adjustment inner cylinder is set in the outer cylinder and can move up and down, and the adjustment The outer wall of the inner cylinder is kept sealed with the inner wall of the outer cylinder, the screw rod is fixed on the adjusting inner cylinder, the installation frame is located above the outer cylinder, and the lower end of the handwheel seat is installed on the On the installation frame, the upper end of the hand wheel seat is equipped with the hand wheel, and the middle part of the hand wheel is equipped with a nut capable of passing the screw mandrel.
作为优选,所述第四进水管的轴线方向与所述中心旋流筒的内壁相切,且所述第四进水管的出口位于所述中心旋流筒的内壁上;所述收油装置为围绕所述罐体的内壁形成的环形槽,所述环形槽上连接有伸出所述罐体外的收油管。Preferably, the axial direction of the fourth water inlet pipe is tangent to the inner wall of the central swirl tube, and the outlet of the fourth water inlet pipe is located on the inner wall of the central swirl tube; the oil collector is An annular groove formed around the inner wall of the tank body is connected with an oil collecting pipe extending out of the tank body.
作为优选,所述喷雾除渣装置包括收渣槽、集渣斗、收渣管和冲洗水管;Preferably, the spray slag removal device includes a slag collecting tank, a slag collecting hopper, a slag collecting pipe and a flushing water pipe;
所述中心旋流筒的上端穿过所述收渣槽的底面位于所述收渣槽内,所述收渣槽的底面为一端高一端低的斜面;The upper end of the central cyclone passes through the bottom surface of the slag collection tank and is located in the slag collection tank. The bottom surface of the slag collection tank is an inclined plane with one end high and the other end low;
所述集渣斗设置于所述收渣槽的底端的外部;The slag collecting hopper is arranged outside the bottom end of the slag collecting tank;
所述收渣管连接于所述集渣斗上并伸出所述罐体外;The slag collecting pipe is connected to the slag collecting hopper and extends out of the tank;
所述冲洗水管的上端固定于所述中心旋流筒的上方,所述冲洗水管上连接有喷雾喷头,所述冲洗水管的下端穿出所述罐体外。The upper end of the flushing water pipe is fixed above the central swirl tube, the spray nozzle is connected to the flushing water pipe, and the lower end of the flushing water pipe passes out of the tank.
作为优选,所述除渣分离罐为负压除渣分离罐,所述负压除渣分离罐包括罐体和设置于所述罐体内的筒体,所述筒体的上端敞口,下端与所述罐体固定并密封,所述筒体与所述罐体之间形成环腔,所述筒体的下部具有至少一个与所述罐体的内腔相连通的出口;所述筒体内的上部固定安装有收渣漏斗,所述收渣漏斗的底部连接有伸出罐体外的排渣管;所述筒体的中部连接有第五进水管;所述罐体的上部内壁上形成环形的收油槽,所述收油槽上连接有伸出所述罐体外的收油管;所述环腔的中部固定有环形的填料层;所述填料层上方的环腔内设置环形的收水管,所述收水管上连接有伸出所述罐体外的第五出水管;所述罐体底部固定有位于所述环腔内的第一环形吸泥管,所述填料层上方固定有第二环形吸泥管。As a preference, the slag removal separation tank is a negative pressure slag removal separation tank, the negative pressure slag removal separation tank includes a tank body and a cylinder body arranged in the tank body, the upper end of the cylinder body is open, and the lower end is connected to the The tank body is fixed and sealed, an annular cavity is formed between the cylinder body and the tank body, and the lower part of the cylinder body has at least one outlet communicating with the inner cavity of the tank body; The upper part is fixed with a slag collection funnel, the bottom of which is connected with a slag discharge pipe protruding from the outside of the tank; the middle part of the cylinder is connected with a fifth water inlet pipe; the upper inner wall of the tank body forms a ring-shaped An oil collection tank, the oil collection tank is connected with an oil collection pipe protruding from the outside of the tank; an annular packing layer is fixed in the middle of the ring cavity; an annular water collection pipe is arranged in the ring cavity above the packing layer, and the The fifth water outlet pipe extending out of the tank is connected to the water collection pipe; the bottom of the tank body is fixed with a first annular mud suction pipe located in the annular cavity, and a second annular mud suction pipe is fixed above the packing layer. Tube.
与现有技术相比,本实用新型的沉降除油罐、采出水处理系统和处理方法的有益效果在于:Compared with the prior art, the beneficial effects of the subsidence oil removal tank, the produced water treatment system and the treatment method of the present invention are:
1、本实用新型中的沉降除油罐采用立式竖流式储罐,设置均匀的集配水系统,在竖流状态下使采出水中的油、水和悬浮固体因密度不同而自然分离,并具有收油及排泥功能,因而极大的提高了采出水除油的工作效率和工作质量。相比传统的平流式除油罐除油效率提高约40%,节约工程投资约30%,有效解决了现有技术中除油罐处理效率低的问题。1. The settling oil removal tank in this utility model adopts a vertical vertical flow storage tank, and a uniform water collection and distribution system is set up. Under the vertical flow state, the oil, water and suspended solids in the produced water are naturally separated due to different densities. It also has the functions of oil collection and mud discharge, thus greatly improving the work efficiency and work quality of produced water deoiling. Compared with the traditional advection oil removal tank, the oil removal efficiency is increased by about 40%, and the engineering investment is saved by about 30%, which effectively solves the problem of low processing efficiency of the oil removal tank in the prior art.
2、本实用新型的采出水处理系统主要由作为一级处理的沉降除油罐和作为二级处理的化学调整旋流反应分离装置组成,可弥补单纯物理法的不足,随着含油污水处理后达标回用的环保要求日益严格,以及对采出水处理系统出水稳定达标和有效防止腐蚀结垢的需求凸显,本实用新型兼顾水质净化和水质稳定,利用能有效控制采出水腐蚀结垢的化学调整旋流反应分离装置,以适应油水密度差小、含一定量高分子有机物或复杂水性采出水的处理。通过投加净水药剂(化学药剂),实现对采出水水性的改良,并通过高效的反应设备实现油、悬浮物和净水药剂的混合反应,并有效分离,实现水的净化,并对水中的成垢和腐蚀性离子进行控制。2. The produced water treatment system of the present utility model is mainly composed of a settling oil removal tank as the primary treatment and a chemically adjusted cyclone reaction separation device as the secondary treatment, which can make up for the deficiency of the pure physical method. Environmental protection requirements for standard reuse are becoming increasingly stringent, and the demand for stable water output from the produced water treatment system and effective prevention of corrosion and scaling is prominent. The cyclone reaction separation device is suitable for the treatment of produced water with small oil-water density difference, a certain amount of high-molecular organic matter or complex water. By adding water purification agents (chemical agents), the water properties of produced water can be improved, and the mixed reaction of oil, suspended solids and water purification agents can be realized through efficient reaction equipment, and the effective separation can be achieved to achieve water purification and water purification. Scaling and corrosive ions are controlled.
3、本实用新型能够应用于国内外SAGD稠油开发中产生的高温低油水密度差和高乳化度采出水处理中,采出水经过这两级处理后,出水含油和悬浮物可达到15mg/L以内,后端辅以过滤即可满足回用要求。解决了高温低油水密度差高乳化度采出水油珠粒径小、油水稳定性强、常规处理流程难度大的问题,为稠油开发解决采出水达标处理回用锅炉的出路问题,避免的污水外排污染环境,同时节约清水产生巨大的经济效益。3. The utility model can be applied to the treatment of produced water with high temperature, low oil-water density difference and high emulsification degree produced in the development of SAGD heavy oil at home and abroad. After these two stages of treatment, the oil and suspended matter in the produced water can reach 15mg/L Within, the backend can be supplemented with filtering to meet the reuse requirements. It solves the problems of high temperature, low oil-water density difference, high emulsification degree, small particle size of produced water and oil beads, strong oil-water stability, and difficult conventional treatment process. It solves the problem of the outlet of produced water to meet the standard treatment and reuse boiler for the development of heavy oil, and avoids sewage The pollution of the environment is discharged outside, and at the same time, the saving of clean water produces huge economic benefits.
附图说明Description of drawings
图1为本实用新型的沉降除油罐的结构示意图。Fig. 1 is a structural schematic diagram of a subsidence oil removal tank of the present invention.
图2为图1中的A-A向视图。Fig. 2 is a view along the line A-A in Fig. 1 .
图3为本实用新型的采出水处理系统中的旋流反应分离罐的结构示意图。Fig. 3 is a schematic structural view of the cyclone reaction separation tank in the produced water treatment system of the present invention.
图4为本实用新型的采出水处理系统中的旋流反应器的结构示意图。Fig. 4 is a structural schematic diagram of the cyclone reactor in the produced water treatment system of the present invention.
图5为本实用新型的采出水处理系统中的喷雾除渣分离罐的结构示意图。Fig. 5 is a structural schematic diagram of the spray slag removal separation tank in the produced water treatment system of the present invention.
图6为本实用新型的采出水处理系统中的负压除渣分离罐的结构示意图。Fig. 6 is a structural schematic diagram of the negative pressure slag removal separation tank in the produced water treatment system of the present invention.
具体实施方式detailed description
下面结合附图和具体实施例对本实用新型作进一步详细描述,但不作为对本实用新型的限定。The utility model will be further described in detail below in conjunction with the accompanying drawings and specific embodiments, but not as a limitation of the utility model.
如图1所示,本实用新型的实施例公开的沉降除油罐,包括罐体101,罐体101内设置有中空的中心管柱102、配水室103、集油槽104和排泥装置105。中心管柱102竖直设于罐体101内并至少下端密封。本实施例的中心管柱102的下端与罐体101的底部连接并密封,上端与罐体101的顶部连接并密封。中心管柱102的上部连通有延伸至罐体101外的第一出水管106,下部连通有位于罐体101内的多个集水管路107,集水管路107上设置有入水口108。As shown in FIG. 1 , the subsidence oil removal tank disclosed in the embodiment of the utility model includes a tank body 101 in which a hollow central column 102 , a water distribution chamber 103 , an oil collection tank 104 and a mud discharge device 105 are arranged. The central column 102 is vertically arranged in the tank body 101 and at least its lower end is sealed. In this embodiment, the lower end of the central column 102 is connected and sealed to the bottom of the tank body 101 , and the upper end is connected to and sealed to the top of the tank body 101 . The upper part of the central column 102 communicates with a first water outlet pipe 106 extending outside the tank body 101 , and the lower part communicates with a plurality of water collecting pipelines 107 inside the tank body 101 , and the water collecting pipelines 107 are provided with water inlets 108 .
配水室103连接有位于罐体101内的多个配水管路109和延伸至罐体101外的第一进水管110,配水管路109上设置有出水口111。集油槽104围绕罐体101的内壁形成环形。集油槽104的开口向上,其截面为U型,具体参见图1。集油槽104上连通有出油管112,出油管112伸出罐体101外。排泥装置105设置于罐体101内的底部。The water distribution chamber 103 is connected with a plurality of water distribution pipelines 109 inside the tank body 101 and a first water inlet pipe 110 extending out of the tank body 101 , and a water outlet 111 is provided on the water distribution pipelines 109 . The oil sump 104 forms a ring around the inner wall of the tank body 101 . The opening of the oil collecting tank 104 is upward, and its cross section is U-shaped, see FIG. 1 for details. An oil outlet pipe 112 is communicated with the oil collecting tank 104 , and the oil outlet pipe 112 extends out of the tank body 101 . The mud discharge device 105 is disposed at the bottom of the tank body 101 .
作为本实用新型的一种优选方案,继续结合图1并参照图2,每个配水管路109包括垂直于中心管柱102并与中心管柱102内部连通的一根配水干管113、垂直连接于配水干管113上的一根配水主支管114和连接在配水主支管114上的多根配水分支管115,每根配水分支管115上分别具有出水口111。如图1所示,出水口111呈喇叭状并开口向上。As a preferred solution of the present utility model, in conjunction with Fig. 1 and with reference to Fig. 2, each water distribution pipeline 109 includes a water distribution main pipe 113 perpendicular to the central pipe column 102 and communicated with the central pipe column 102, vertically connected A water distribution main branch pipe 114 on the water distribution main pipe 113 and a plurality of water distribution branch pipes 115 connected to the water distribution main branch pipe 114, each water distribution branch pipe 115 has a water outlet 111 respectively. As shown in FIG. 1 , the water outlet 111 is trumpet-shaped and opens upward.
继续结合图1,为了使罐体101同一横截面上的配水均匀,应该将配水室103设置于罐体101的中部,本实施例中的中心管柱102位于罐体101的正中,配水室103设置在中心管柱102上,本实施例中的配水室103为环形,并套在中心管柱102上。多个配水管路109的多根配水干管113以均布的方式设于配水室103上。Continuing in conjunction with Fig. 1, in order to make the water distribution on the same cross section of the tank body 101 uniform, the water distribution chamber 103 should be arranged in the middle of the tank body 101, and the central column 102 in this embodiment is located in the middle of the tank body 101, and the water distribution chamber 103 It is arranged on the central pipe column 102 , and the water distribution chamber 103 in this embodiment is annular and sleeved on the central pipe column 102 . A plurality of water distribution main pipes 113 of a plurality of water distribution pipelines 109 are arranged on the water distribution chamber 103 in a uniform manner.
集水管路107采用与配水管路基本相同的结构,即每个集水管路107包括垂直于中心管柱102并与中心管柱102内部连通的一根集水干管、垂直连接于集水干管上的一根集水主支管和连接在集水主支管上的多根集水分支管,每根集水分支管上分别具有入水口108。集水管路107的结构可以参照图2进行理解。入水口108呈喇叭状并开口向下。The water collection pipeline 107 adopts basically the same structure as the water distribution pipeline, that is, each water collection pipeline 107 includes a main water collection pipe that is perpendicular to the central pipe column 102 and communicates with the interior of the central pipe column 102, and is vertically connected to the main water collection pipe. A water collection main branch pipe and a plurality of water collection branch pipes connected to the water collection main branch pipe, each water collection branch pipe has a water inlet 108 respectively. The structure of the water collecting pipeline 107 can be understood with reference to FIG. 2 . The water inlet 108 is trumpet-shaped and opens downward.
排泥装置105用于清除来液中的泥沙沉淀物。本实施例中的排泥装置采用中国专利授权公告号为CN2516279Y的一种油罐排污泥装置。The mud discharge device 105 is used to remove mud and sand deposits in the incoming liquid. The mud discharge device in this embodiment adopts a kind of oil tank sludge discharge device whose Chinese patent authorization announcement number is CN2516279Y.
另外,如图1所示,罐体101内设置有一端位于罐体101外的溢流管117,以在罐体101内液位过高时,通过溢流管117将罐体101内的水排出罐体101外。In addition, as shown in Figure 1, an overflow pipe 117 with one end located outside the tank body 101 is arranged in the tank body 101, so that when the liquid level in the tank body 101 is too high, the water in the tank body 101 is drained through the overflow pipe 117. out of the tank body 101.
下面结合图1对本实用新型的沉降除油罐的工作过程进行介绍:采出水通过第一进水管110流入配水室103,然后经配水管路109及出水口111流入罐体101内,水中粒径较大的油珠首先上浮至油层,粒径较小的油珠随水向下流动。在向下流动的过程中,一部分小油珠由于自身在静水中上浮速度不同及水流速度梯度的推动,不断碰撞聚结成大油珠而上浮,无上浮能力的部分油珠随水经入水口108进入集水管路107,然后进入中心管柱102,再经第一出水管106流出罐体101外,进入下一道程序;油层内的浮油流入集油槽104,再经出油管112流出;罐体101底部聚集的污泥进入排泥装置105,然后经排污管116排出。Below in conjunction with Fig. 1, the working process of the subsidence oil removal tank of the present utility model is introduced: the produced water flows into the water distribution chamber 103 through the first water inlet pipe 110, and then flows into the tank body 101 through the water distribution pipeline 109 and the water outlet 111. The larger oil droplets first float to the oil layer, and the smaller oil droplets flow down with the water. In the process of downward flow, some small oil droplets continuously collide and coalesce into large oil droplets due to the different floating speed in still water and the promotion of the water flow velocity gradient, and some oil droplets without floating ability pass through the water inlet with water 108 enters the water collection pipeline 107, then enters the central pipe column 102, and then flows out of the tank body 101 through the first water outlet pipe 106, and enters the next procedure; the floating oil in the oil layer flows into the oil collection tank 104, and then flows out through the oil outlet pipe 112; The sludge accumulated at the bottom of the body 101 enters the sludge discharge device 105 and is then discharged through the sewage pipe 116.
通过上述对沉降除油罐的描述,可知其有益效果为:Through the above description of the subsidence oil removal tank, it can be seen that its beneficial effects are:
1)由于配水管路的出水口111开口向上,当水从管口以一定速度流出后,油珠处理因自身的上浮力(因油水相对密度差所致)所获得的在水中的上浮速度外,还受水流向上垂直速度的推动,油珠将更快到达油层,所需的分离沉降时间缩短。1) Since the water outlet 111 of the water distribution pipeline opens upwards, when the water flows out from the pipe mouth at a certain speed, the oil droplets will deal with the floating speed in the water due to their own buoyancy (due to the relative density difference between oil and water). , also driven by the upward vertical velocity of the water flow, the oil droplets will reach the oil layer faster, and the required separation and settlement time will be shortened.
2)本实用新型中的沉降除油罐采用上配水、下集水的方式。最初因碰撞聚结而直径变大的上浮油珠与被水流夹带向下流动的油珠间,始终存在着对流碰撞聚结过程,这种过程对小颗粒的聚结十分有利。对流碰撞聚结的效率取决于单位体积中油珠的个数,单位体积中油珠的个数越多,则碰撞聚结机会越多,效率越高。2) The subsidence and degreasing tank in the utility model adopts the mode of upper water distribution and lower water collection. There is always a process of convective collision coalescence between the floating oil droplets whose diameter becomes larger due to collision coalescence and the oil droplets entrained by the water flow to flow downward. This process is very beneficial to the coalescence of small particles. The efficiency of convective collision coalescence depends on the number of oil droplets per unit volume. The more oil droplets per unit volume, the more chances of collision coalescence and the higher the efficiency.
3)集水管路的入水口和配水管路的出水口均采用辐射式喇叭口,能够保证配水、集水的均匀性,并且有着结构简单,安装方便、不易堵塞、运行平稳的优点。使从配水管路流出的水均匀的分配到罐体内的水平截面上,并均匀汇集起来流出罐体。由于配水管路设置成了配水干管、配水主支管和多根配水分支管的方式,使得流出的水按一定的速度梯度递减,降低了进入罐体内水的扰动性,不会产生扰流而影响油的上浮速度,更利用油珠的聚结。3) Both the water inlet of the water collection pipeline and the water outlet of the water distribution pipeline adopt radial bell mouths, which can ensure the uniformity of water distribution and collection, and have the advantages of simple structure, convenient installation, not easy to block, and stable operation. The water flowing out from the water distribution pipeline is evenly distributed to the horizontal section of the tank body, and evenly collected and flowed out of the tank body. Since the water distribution pipeline is set in the form of a water distribution main pipe, a water distribution main branch pipe and multiple water distribution branch pipes, the outflowing water decreases gradually according to a certain speed gradient, which reduces the turbulence of the water entering the tank and will not cause turbulence. Affect the floating speed of oil, and make use of the coalescence of oil droplets.
本实用新型同时公开了一种采出水处理系统,其包括除油罐和化学调整旋流反应分离装置,除油罐采用图1所示的沉降除油罐,沉降除油罐的第一出水管106连接至化学调整旋流反应分离装置。化学调整旋流反应分离装置是根据采出水的特性,筛选出需要投加的净水药剂,同时试验出净水药剂投加时间间隔与混合反应强度,再利用化学调整旋流反应分离装置的紊流逐级变小的涡流场,在工艺上为净水药剂与采出水的混合提供了动力,反应后出水通过混凝沉降的方式将反应产物絮体与水分离,实现水的净化。The utility model also discloses a produced water treatment system, which includes an oil removal tank and a chemically adjusted swirling reaction separation device. 106 is connected to the chemical adjustment cyclone reaction separation device. The chemical adjustment cyclone reaction separation device is based on the characteristics of the produced water, screens out the water purification agent that needs to be added, and at the same time tests the water purification agent dosing interval and the mixing reaction intensity, and then uses the chemical adjustment to the turbulence of the cyclone reaction separation device. The eddy current field where the flow becomes smaller step by step provides power for the mixing of water purification agents and produced water in the process. After the reaction, the effluent will separate the reaction product flocs from the water by coagulation and sedimentation to realize water purification.
本实用新型的化学调整旋流反应分离装置可以采用以下两种方式来实现,一种是合体式装置,为主要针对于常规水质条件下的旋流反应分离罐;第二种是分体式装置,主要针对复杂水性,由旋流反应器和除渣分离罐两个部分组成。The chemical adjustment cyclone reaction separation device of the present utility model can be realized in the following two ways, one is a combined device, which is mainly aimed at the cyclone reaction separation tank under conventional water quality conditions; the second is a split device, It is mainly aimed at complex water, and consists of two parts: a cyclone reactor and a slag removal separation tank.
化学调整旋流反应分离装置采用图3所示的旋流反应分离罐,旋流反应分离罐包括罐体201和纵向置于罐体201内的旋流反应中心筒,旋流反应中心筒的上端封闭并开设有油气出口214,下端与罐体201的内腔相连通,旋流反应中心筒从上到下依次分为第一级旋流反应段202、第二级旋流反应段203和第三级旋流反应段204。罐体201上固定连接有伸入到第一级旋流反应段202内的第二进水管205、伸入到第二级旋流反应段203内的第二净水剂管207和伸入到第三级旋流反应段204内的絮凝剂管208,第二进水管205上连通有第一净水剂管206。罐体201内的上部固定设置有集水管209和位于集水管的上方的集油管210,集水管209上开设有进水口(图中未示出),集水管209上连接有伸出罐体201外的第二出水管211;集油管210上开设有进油口(图中未示出),集油管210上连接有伸出罐体201外的出油管212。罐体201的底部连接有排泥管213。沉降除油罐的连接,经沉降除油罐处理后的水经第一出水管106和第二进水管205进入旋流反应分离罐进行化学处理。The chemical adjustment swirl reaction separation device adopts the swirl reaction separation tank shown in Figure 3, the swirl reaction separation tank includes a tank body 201 and a swirl reaction center cylinder vertically placed in the tank body 201, the upper end of the swirl reaction center cylinder Closed and opened with an oil and gas outlet 214, the lower end communicates with the inner cavity of the tank body 201, and the swirl reaction center cylinder is divided into the first-stage swirl reaction section 202, the second-stage swirl reaction section 203 and the second-stage swirl reaction section from top to bottom. Three-stage cyclone reaction section 204 . The tank body 201 is fixedly connected with the second water inlet pipe 205 extending into the first-stage cyclone reaction section 202, the second water purification agent pipe 207 extending into the second-stage cyclone reaction section 203 and the The flocculant pipe 208 in the third-stage cyclone reaction section 204 is connected with the first water purifying agent pipe 206 on the second water inlet pipe 205 . The top in the tank body 201 is fixedly provided with a water collecting pipe 209 and an oil collecting pipe 210 above the water collecting pipe. The water collecting pipe 209 is provided with a water inlet (not shown in the figure), and the water collecting pipe 209 is connected with a tank body 201 The outer second water outlet pipe 211; the oil collecting pipe 210 is provided with an oil inlet (not shown in the figure), and the oil collecting pipe 210 is connected with an oil outlet pipe 212 extending out of the tank body 201 . A mud discharge pipe 213 is connected to the bottom of the tank body 201 . The connection of the sedimentation oil removal tank, the water treated by the sedimentation oil removal tank enters the cyclone reaction separation tank through the first water outlet pipe 106 and the second water inlet pipe 205 for chemical treatment.
继续结合图3,为了便于集水和集油,集水管209和集油管210均为环形,集水管209和集油管210均固定套在旋流反应中心筒的上部外,进水口为均布于集水管209上的多个,进油口为均布于集油管210上的多个。为了使污水中产生的气体能排出罐体201外,在罐体201的顶端设有排气口215。Continuing with Figure 3, in order to facilitate water collection and oil collection, the water collection pipe 209 and the oil collection pipe 210 are ring-shaped, and the water collection pipe 209 and the oil collection pipe 210 are fixedly sleeved outside the upper part of the cyclone reaction center cylinder, and the water inlets are evenly distributed on the There are multiple oil inlets on the water collecting pipe 209 , and there are multiple oil inlets evenly distributed on the oil collecting pipe 210 . In order to make the gas generated in the sewage discharge out of the tank body 201 , an exhaust port 215 is provided at the top of the tank body 201 .
另外,第二进水管205的轴线方向与旋流反应中心筒的内壁相切。采用切向进水的方式,使水流在旋流反应中心筒内形成旋转流态,保持一定的水流速度,以便形成速度梯度场,进一步提高絮体聚并效果。In addition, the axial direction of the second water inlet pipe 205 is tangent to the inner wall of the cyclone reaction center cylinder. The way of tangential water inlet is adopted to make the water flow form a swirling flow state in the swirl reaction center tube, maintain a certain water flow velocity, so as to form a velocity gradient field, and further improve the effect of floc aggregation.
由沉降除油罐来的水通过第二进水管205进入到第一级旋流反应段202内,水在进入第一级旋流反应段202之前通过第一净水剂管206加入第一种净水药剂,在第一级旋流反应段202内反应;第一级旋流反应段202内可分离出油及气体,分离出的油及气体可从油气出口214排到罐体201内并从排气口215排出罐体201外。然后进入到第二级旋流反应段203内,通过第二净水剂管207向第二级旋流反应段203内投加第二种净水药剂,再次絮凝反应;最后水进入到第三级旋流反应段204内,同时通过絮凝剂管208向第三级旋流反应段204内投加有机高分子絮凝剂,网扑及吸附形成小絮体;初步形成松散的絮体经旋流反应中心筒的底部进入到罐体1内,由于水流的上流及重力压缩,在第一级旋流反应段202、第二级旋流反应段203和第三级旋流反应段204与罐体201之间形成污泥床216,继续过滤、网扑及吸附小絮体,同时压缩污泥间的间隙水,形成密实污泥而沉降到罐体2011的底部。污水通过污泥床后,充分利用了净水药剂的剩余电位,小油珠的负电位得到降低,而聚并成大油珠上浮,进入罐体201顶部的集油管210内,再从出油管212排出;净化后的水进入集水管209并从第二出水管211排出;通过定时打开罐体201底部的排泥管213上的阀门,可将污泥排出。The water from the settling oil removal tank enters the first-stage cyclone reaction section 202 through the second water inlet pipe 205, and the water enters the first-stage cyclone reaction section 202 through the first water-purifying agent pipe 206 before entering the first-stage cyclone reaction section 202. The water purification agent reacts in the first-stage cyclone reaction section 202; oil and gas can be separated in the first-stage cyclone reaction section 202, and the separated oil and gas can be discharged into the tank body 201 from the oil-gas outlet 214 and The gas is discharged from the tank body 201 through the exhaust port 215 . Then enter the second-stage cyclone reaction section 203, add the second water purification agent to the second-stage cyclone reaction section 203 through the second water purification agent pipe 207, and flocculate again; finally, the water enters the third stage. In the first-stage cyclone reaction section 204, organic polymer flocculants are added to the third-stage cyclone reaction section 204 through the flocculant pipe 208 at the same time, and small flocs are formed by netting and adsorption; the initially formed loose flocs are passed through the cyclone The bottom of the reaction center tube enters the tank body 1, due to the upflow of water flow and gravity compression, the first-stage swirl reaction section 202, the second-stage swirl reaction section 203 and the third-stage swirl reaction section 204 are connected to the tank body. A sludge bed 216 is formed between the tanks 201 to continue filtering, fluttering and absorbing small flocs, while compressing the interstitial water between the sludge to form dense sludge and settle to the bottom of the tank 2011. After the sewage passes through the sludge bed, the residual potential of the water purification agent is fully utilized, the negative potential of the small oil droplets is reduced, and they are aggregated into large oil droplets to float up, enter the oil collecting pipe 210 at the top of the tank body 201, and then flow from the oil outlet pipe 212 is discharged; the purified water enters the water collecting pipe 209 and is discharged from the second outlet pipe 211; by regularly opening the valve on the mud discharge pipe 213 at the bottom of the tank body 201, the sludge can be discharged.
本实用新型中的旋流反应分离罐结构合理而紧凑,能快速有效的净化污水、清除污泥并收集油珠,因而极大的提高了处理含油污水的工作效率和工作质量。The cyclone reaction separation tank in the utility model has a reasonable and compact structure, can quickly and effectively purify sewage, remove sludge and collect oil droplets, thus greatly improving the working efficiency and quality of treating oily sewage.
本实用新型的采出水处理系统中的化学调整旋流反应分离装置的第二种分体式装置包括旋流反应器和除渣分离罐;如图4所示,旋流反应器包括罐体301,罐体301内设置隔板307,,隔板307将罐体301分隔为位于下部的第一级反应腔302和位于上部的第二级反应腔303的;对应第一级反应腔303的罐体301上开设有进水口,进水口内设置有伸入第一级反应腔303内的第三进水管304,第三进水管304与沉降除油罐的第一出水管106连接。对应第二级反应腔303的罐体301上开设有净水药剂投加口和出水口,净水药剂投加口内设置有伸入第二级反应腔303内的药剂投加管305,出水口内设置有伸入第二级反应腔303内的第三出水管306,药剂投加管305位于第二级反应腔303的下部并紧邻隔板307,第三出水管306位于第二级反应腔303的上部。隔板307上开设有通孔,通孔内设置连接管308,连接管308与药剂投加管305连通。The second split device of the chemically adjusted swirl reaction separation device in the produced water treatment system of the present invention includes a swirl reactor and a slag removal separation tank; as shown in Figure 4, the swirl reactor includes a tank body 301, A partition 307 is arranged in the tank body 301, and the partition board 307 divides the tank body 301 into a first-stage reaction chamber 302 located at the lower part and a second-stage reaction chamber 303 located at the upper part; corresponding to the tank body of the first-stage reaction chamber 303 301 is provided with a water inlet, and a third water inlet pipe 304 extending into the first stage reaction chamber 303 is arranged in the water inlet, and the third water inlet pipe 304 is connected with the first water outlet pipe 106 of the settling oil removal tank. The tank body 301 corresponding to the second-stage reaction chamber 303 is provided with a water purification agent dosing port and a water outlet, and the water purification agent dosing port is provided with a drug dosing pipe 305 extending into the second-stage reaction chamber 303. A third water outlet pipe 306 extending into the second-stage reaction chamber 303 is provided, the drug dosing pipe 305 is located at the lower part of the second-stage reaction chamber 303 and is close to the partition 307, and the third water outlet pipe 306 is located in the second-stage reaction chamber 303 the upper part. A through hole is opened on the partition 307 , and a connecting pipe 308 is arranged in the through hole, and the connecting pipe 308 communicates with the medicament dosing pipe 305 .
隔板307上可以进设置通孔,而不设置连接管308,第一级反应腔302内的水直接进入第二级反应腔303。设置连接管308可以使由第一级反应腔302来的水能够与药剂投加管305投加的净水药剂充分反应。A through hole may be provided on the separator 307 instead of a connecting pipe 308 , and the water in the first-stage reaction chamber 302 directly enters the second-stage reaction chamber 303 . The connection pipe 308 is provided so that the water from the first-stage reaction chamber 302 can fully react with the water purification agent fed by the agent dosing pipe 305 .
本实施例中的第三进水管304、第三出水管306和药剂投加管305均水平设置,而连接管308竖直设置。In this embodiment, the third water inlet pipe 304 , the third water outlet pipe 306 and the medicament dosing pipe 305 are all arranged horizontally, while the connecting pipe 308 is arranged vertically.
如图4所示,从沉降除油罐的第一出水管106来的水加入第一种净水药剂后通过第三进水管304进入旋流反应器下部的第一级反应腔302,净水药剂与污水充分混合、反应后,穿过隔板307上的通孔进入第二级反应腔303,在进入第二级反应腔303时与药剂投加管305相接,污水中混入第二种净水药剂,第二种净水药剂与第一种净水药剂反应后水在第二级反应腔303中充分混合、反应,絮体进一步长大,絮体沉降到罐体301的底部,最后少量浮油与水通第三出水管306进入除渣分离罐进行进一步处理。旋流反应器的顶部设有安全排气口310,底部设有排污放空口309。As shown in Figure 4, the water from the first outlet pipe 106 of the settling oil removal tank enters the first stage reaction chamber 302 at the bottom of the cyclone reactor through the third water inlet pipe 304 after adding the first water purification agent, and the water purification After the medicament and sewage are fully mixed and reacted, they enter the second-stage reaction chamber 303 through the through hole on the partition 307, and connect with the medicament dosing pipe 305 when entering the second-stage reaction chamber 303, and the second-stage reaction chamber 305 is mixed into the sewage. Water purification agent, after the second water purification agent reacts with the first water purification agent, the water is fully mixed and reacted in the second reaction chamber 303, the flocs grow further, and the flocs settle to the bottom of the tank 301, and finally A small amount of slick oil and water pass through the third outlet pipe 306 and enter the slag removal separation tank for further treatment. The top of the cyclone reactor is provided with a safety exhaust port 310, and the bottom is provided with a sewage discharge port 309.
本实用新型的采出水处理系统中的除渣分离罐可以采用喷雾除渣分离罐,也可以采用负压除渣分离罐。The slag removal separation tank in the produced water treatment system of the utility model can adopt a spray slag removal separation tank, and can also adopt a negative pressure slag removal separation tank.
如图5所示,喷雾除渣分离罐包括罐体401、中心旋流筒402、喷雾除渣装置、收油装置、排泥装置和收水装置。中心旋流筒402的上端敞口,下端固定在罐体401的底部并密封,中心旋流筒402与罐体401之间形成环腔,中心旋流筒402的下部具有至少一个与罐体401的内腔相连通的连通口403,中心旋流筒402的中部连接有第四进水管404,第四进水管404的一端位于中心旋流筒402内,另一端与旋流反应器的第三出水管306连接。喷雾除渣装置设置于中心旋流筒402的上部外侧。收油装置设置于中心旋流筒402上端对应的罐体401的内壁上。排泥装置设置于罐体401的底部对应连通口403的位置。收水装置包括安装于罐体401的外侧上部的外挂水箱405和收水管,收水管的下端位于罐体401内并与罐体401连通,收水管的上端与外挂水箱405相连通;外挂水箱405的下部固定连接有第四出水管406。As shown in Figure 5, the spray slag removal separation tank includes a tank body 401, a central cyclone 402, a spray slag removal device, an oil collection device, a sludge discharge device and a water collection device. The upper end of the central swirl tube 402 is open, and the lower end is fixed on the bottom of the tank body 401 and sealed. An annular cavity is formed between the central swirl tube 402 and the tank body 401. The lower part of the central swirl tube 402 has at least one The inner cavity of the central swirl tube 402 is connected to the communication port 403, and the middle part of the central swirl tube 402 is connected with a fourth water inlet pipe 404. One end of the fourth water inlet tube 404 is located in the center swirl tube 402, and the other end is connected with the third swirl reactor. Outlet pipe 306 is connected. The spray slag removal device is arranged outside the upper part of the central cyclone tube 402 . The oil collector is arranged on the inner wall of the tank body 401 corresponding to the upper end of the central swirl cylinder 402 . The mud discharge device is arranged at the bottom of the tank body 401 at a position corresponding to the communication port 403 . The water collection device comprises an external water tank 405 and a water collection pipe installed on the outer upper part of the tank body 401. The lower end of the water collection pipe is located in the tank body 401 and communicates with the tank body 401. The upper end of the water collection pipe communicates with the external water tank 405; the external water tank 405 A fourth water outlet pipe 406 is fixedly connected to the lower part.
通过喷雾除渣装置和收油装置能够持续有效地将罐体401内顶部积聚的浮渣与处理后的水分离并排出罐体401外。而且喷雾除渣装置能够喷出水雾,有效去除浮渣,避免罐体401顶部积聚的浮渣经第四出水管406流出,减小浮渣对出水水质和后段流程的影响。The scum accumulated on the top of the tank body 401 can be continuously and effectively separated from the treated water by the spray slag removal device and the oil collector and discharged out of the tank body 401 . Moreover, the spray scum removal device can spray water mist to effectively remove scum, prevent the scum accumulated on the top of the tank body 401 from flowing out through the fourth outlet pipe 406, and reduce the impact of scum on the quality of the effluent and subsequent processes.
继续结合图5,第四进水管404的轴线方向与中心旋流筒402的内壁相切,且第四进水管404的出口位于中心旋流筒402的内壁上。第四进水管404的轴向方向与中心旋流筒402的内壁相切,能够使待处理的水沿切线进入中心旋流筒402内,产生高速涡流,加快待处理污水与净水药剂的混合。Continuing with FIG. 5 , the axial direction of the fourth water inlet pipe 404 is tangent to the inner wall of the central swirl tube 402 , and the outlet of the fourth water inlet pipe 404 is located on the inner wall of the central swirl tube 402 . The axial direction of the fourth water inlet pipe 404 is tangent to the inner wall of the central swirl tube 402, so that the water to be treated can enter the central swirl tube 402 along the tangent line, generating a high-speed vortex, and speeding up the mixing of the sewage to be treated and the water purification agent .
继续参见图5,收水管包括收水环管407和L状引管408,收水环管407套于中心旋流筒的中部外并通过筋板与罐体401的外壁固定,收水环管407朝下的一侧均匀设置有多个收水进口409。L状引管408的一端与收水环管407连通,另一端穿出罐体401并伸入外挂水箱405内。L状引管408位于所述外挂水箱405内的一端(下文中将该端命名为上端)上安装有过滤器。净化后的水先由收水进口409流入收水环管407,再从收水环管407流入L状引管408,保证了罐体401捏净化后的水均匀流出。Continuing to refer to Fig. 5, the water collection pipe includes a water collection ring pipe 407 and an L-shaped guide pipe 408. The water collection ring pipe 407 is set outside the middle of the central swirl tube and fixed to the outer wall of the tank body 401 by ribs. The water collection ring pipe A plurality of water collection inlets 409 are uniformly arranged on the downward side of 407 . One end of the L-shaped guide pipe 408 communicates with the water receiving ring pipe 407, and the other end passes through the tank body 401 and extends into the external water tank 405. One end of the L-shaped guide pipe 408 located in the external water tank 405 (hereinafter the end is named as the upper end) is provided with a filter. The purified water first flows into the water receiving ring pipe 407 from the water receiving inlet 409, and then flows into the L-shaped lead pipe 408 from the water receiving ring pipe 407, which ensures that the tank body 401 pinches the purified water to flow out evenly.
如图5所示,外挂水箱405内设置有水位调节器,水位调节器包括外筒410、调节内筒(图中未示出)、丝杆412、安装架413、手轮414和手轮座415,外筒410固定于外挂水箱405内的底部,L状引管408的上端位于外筒410内,第四出水管406位于外筒410的外部;调节内筒套装于外筒410内并能够上下移动,在调节内筒移动的过程中,调节内筒的外壁与外筒410的内壁保持密封,调节内筒上固定有丝杆412,安装架413设置于外挂水箱405内并位于外筒410的上方,手轮座415的下端固定安装于安装架413上,手轮座415的上端安装手轮414,手轮414中部安装有螺母,丝杆412的上端穿过螺母。As shown in Figure 5, a water level regulator is provided in the external water tank 405, and the water level regulator includes an outer cylinder 410, an adjustment inner cylinder (not shown in the figure), a screw rod 412, a mounting frame 413, a handwheel 414 and a handwheel seat 415, the outer cylinder 410 is fixed on the bottom of the external water tank 405, the upper end of the L-shaped guide pipe 408 is located in the outer cylinder 410, and the fourth outlet pipe 406 is located outside the outer cylinder 410; the adjustment inner cylinder is set in the outer cylinder 410 and can Move up and down, during the process of adjusting the movement of the inner cylinder, the outer wall of the adjustment inner cylinder is kept sealed with the inner wall of the outer cylinder 410, the screw rod 412 is fixed on the adjustment inner cylinder, and the mounting bracket 413 is set in the external water tank 405 and located on the outer cylinder 410 Above, the lower end of the handwheel seat 415 is fixedly installed on the mounting bracket 413, the upper end of the handwheel seat 415 is equipped with a handwheel 414, the middle part of the handwheel 414 is equipped with a nut, and the upper end of the screw mandrel 412 passes through the nut.
水位调节器能够调节外挂水箱405内水位的高度,生产过程中根据实际对水质和水量变化的需求,转动手轮414带动丝杆412上下移动,丝杆412带动调节内筒在外筒410内上下滑动,以调节外挂水箱405的出水高度。当罐体401内的排油排渣需要高液位时,可提高调节内筒的高度,使外挂水箱405的水位提高;当罐体401内需要低液位排水时,可降低调节内筒的高度,以利于罐体401内水的排出。通过水位调节器,使得罐体401内的浮油全部通过收油装置排出,不会在罐体401内停留积累,从而进一步改善出水水质。The water level regulator can adjust the height of the water level in the external water tank 405. During the production process, according to the actual demand for water quality and water quantity changes, the hand wheel 414 is turned to drive the screw rod 412 to move up and down, and the screw rod 412 drives the adjustable inner cylinder to slide up and down in the outer cylinder 410 , to adjust the water outlet height of the external water tank 405. When the oil discharge and slag discharge in the tank body 401 requires a high liquid level, the height of the inner cylinder can be adjusted to increase the water level of the external water tank 405; height, to facilitate the discharge of water in the tank body 401. Through the water level regulator, all floating oil in the tank body 401 is discharged through the oil collector, and will not stay and accumulate in the tank body 401, thereby further improving the quality of the effluent water.
本实施例中的收油装置为围绕罐体401的内壁形成的环形的收油槽424,收油槽424的截面为开口向上的U型,收油槽424上连接有伸出罐体401外的收油管416。The oil collection device in this embodiment is an annular oil collection groove 424 formed around the inner wall of the tank body 401. The cross section of the oil collection groove 424 is U-shaped with an upward opening, and the oil collection groove 424 is connected with an oil collection pipe extending outside the tank body 401. 416.
继续结合图5,喷雾除渣装置包括收渣槽417、集渣斗418、收渣管419和冲洗水管420;收渣槽417仅上端敞口,底面开设有用于使中心旋流筒402的上端穿过的孔,中心旋流筒402与孔壁之间密封,中心旋流筒402的上端位于收渣槽417内,收渣槽417的底面为一端高一端低的斜面,即图5中的左端低、右端高;集渣斗418设置于收渣槽417的底端(即左端)的外部;收渣管419连接于集渣斗418上并伸出罐体401外,并且收渣槽417、集渣斗418和收渣管419均相连通。冲洗水管420的上端固定于中心旋流筒402的上方,冲洗水管420上连接有喷雾喷头,冲洗水管420的下端穿出罐体401外并与自来水连接。Continuing in conjunction with Fig. 5, the spray slag removal device includes a slag collecting tank 417, a slag collecting hopper 418, a slag collecting pipe 419 and a flushing water pipe 420; The hole passed through is sealed between the central cyclone cylinder 402 and the hole wall. The upper end of the central cyclone cylinder 402 is located in the slag collection tank 417. The bottom surface of the slag collection tank 417 is a slope with one end high and the other end low, that is, the The left end is low and the right end is high; the slag collecting hopper 418 is arranged outside the bottom end (ie the left end) of the slag collecting tank 417; , the slag collecting bucket 418 and the slag collecting pipe 419 are all connected. The upper end of the flushing water pipe 420 is fixed on the top of the central swirl tube 402, and the flushing water pipe 420 is connected with a spray nozzle, and the lower end of the flushing water pipe 420 passes out of the tank body 401 and is connected with running water.
继续结合图5,本实施例中的喷雾喷头包括上层喷雾喷头421和下层喷雾喷头422。上层喷雾喷头421至少为两个,并环绕冲洗水管420的上端外侧均匀安装,相邻两个上层喷雾喷头421之间的下方的冲洗水管420上设置一个下层喷雾喷头422。上层喷雾喷头421和下层喷雾喷头422呈上下两层并错位布置,使冲洗效果更好。实际生产运行时,当中心旋流筒402上部的浮渣厚度较小、密度较轻时,可仅利用下层喷雾喷头422;当浮渣厚度较厚时,则上层喷雾喷头421和下层喷雾喷头422可同时使用。Continuing with FIG. 5 , the spray nozzles in this embodiment include an upper spray nozzle 421 and a lower spray nozzle 422 . There are at least two upper spray nozzles 421, and they are uniformly installed around the upper end of the flushing water pipe 420, and a lower spray nozzle 422 is arranged on the flushing water pipe 420 below between two adjacent upper spray nozzles 421. The upper layer spray nozzle 421 and the lower layer spray nozzle 422 are two layers up and down and arranged in a dislocation, so that the flushing effect is better. During actual production and operation, when the thickness of the scum on the upper part of the central cyclone 402 is small and the density is light, only the lower spray nozzle 422 can be used; when the thickness of the scum is thick, the upper spray nozzle 421 and the lower spray nozzle 422 Can be used simultaneously.
如图5所示,排泥装置可以采用中国专利授权公告号为CN2516279Y的一种油罐排污泥装置。其结构和原理在此不再赘述。另外,靠近收渣槽417外侧上端位置的罐体401内部固定有溢流管423,溢流管423的上端口与罐体401的内腔相连通,溢流管423的中部穿过罐体401伸至罐体401外,溢流管423的下端连接到污水处理站的排污线上,当第四进水管404的来水量突然增大,短时间内超过喷雾除渣分离罐的处理负荷时,多余的水从溢流管423流出罐体401外,防止未处理的水直接进入外挂水箱405,造成出水水质变差。As shown in Figure 5, the sludge discharge device can adopt a kind of oil tank sludge discharge device whose Chinese patent authorization announcement number is CN2516279Y. Its structure and principle will not be repeated here. In addition, an overflow pipe 423 is fixed inside the tank body 401 near the upper end of the slag collection tank 417, the upper port of the overflow pipe 423 communicates with the inner cavity of the tank body 401, and the middle part of the overflow pipe 423 passes through the tank body 401 Extending to the outside of the tank body 401, the lower end of the overflow pipe 423 is connected to the sewage treatment station's sewage line. When the incoming water volume of the fourth water inlet pipe 404 suddenly increases and exceeds the processing load of the spray slag removal separation tank in a short period of time, Excess water flows out of the tank body 401 from the overflow pipe 423, preventing untreated water from directly entering the external water tank 405, resulting in poor water quality.
下面结合图5对喷雾除渣分离罐的工作过程进行介绍:首先,由旋流反应器处理后的采出水经第三出水管306进入第四进水管404,然后进入中心旋流筒402内的中部,水流在中心旋流筒402内部旋转向下流动,采出水与净水药剂充分混合后反应形成油渣,油渣在中心旋流筒402内与处理后的水流逐渐分离并向上移动,上升至中心旋流筒402顶部的油渣形成浮渣层;采出水与净水药剂反应生成的浮油进入收油槽424,并通过收油管416排出罐体401外。采出水的泥沙等杂质,以及采出水与净水药剂反应生成的污泥沉积到罐体401的底部,通过负压排泥器收集并经排泥管425排出罐体401外部。来自冲洗水管420的有压水通过喷雾喷头喷出,将聚集在中心旋流筒402顶部的浮渣吹扫至收渣槽417内,收渣槽417内的浮渣沿收渣槽417的底部斜面逐渐滑移至集渣斗418中,通过收渣管419排出罐体401外。最后,处理后的水由连通口403流入罐体401内,并经收水环管407和L型引管408进入调节内筒,由调节内筒上端流出的水进入外挂水箱405,并经第四出水管406排出进入后续处理设备。The working process of the spray slag removal separation tank is introduced below in conjunction with Fig. 5: first, the produced water processed by the cyclone reactor enters the fourth water inlet pipe 404 through the third water outlet pipe 306, and then enters the water in the central cyclone cylinder 402. In the middle part, the water flow rotates inside the central cyclone 402 and flows downward. The produced water and the water purification agent are fully mixed and react to form oil residue. The oil residue is gradually separated from the treated water in the central cyclone 402 and moves upward. The oil residue on the top of the central cyclone tube 402 forms a scum layer; the floating oil generated by the reaction of the produced water and the water purification agent enters the oil collection tank 424 and is discharged out of the tank body 401 through the oil collection pipe 416 . Impurities such as silt and other impurities in the produced water, as well as sludge generated by the reaction of the produced water and the water purification agent are deposited at the bottom of the tank body 401 , collected by a negative pressure sludge discharge device and discharged outside the tank body 401 through the sludge discharge pipe 425 . The pressurized water from the flushing water pipe 420 is sprayed out through the spray nozzle, and the scum gathered on the top of the central cyclone 402 is blown into the slag collection tank 417, and the scum in the slag collection tank 417 moves along the bottom of the slag collection tank 417. The inclined surface gradually slides into the slag collecting bucket 418 and is discharged out of the tank body 401 through the slag collecting pipe 419 . Finally, the treated water flows into the tank body 401 through the communication port 403, and enters the regulating inner cylinder through the water collection ring pipe 407 and the L-shaped introduction pipe 408, and the water flowing out from the upper end of the regulating inner cylinder enters the external water tank 405, and passes through the second The four outlet pipes 406 are discharged into subsequent treatment equipment.
如图6所示,除渣分离罐为负压除渣分离罐,负压除渣分离罐包括罐体501和位于罐体501内的筒体502,筒体502的上端敞口,下端与罐体501固定并密封,罐体501与筒体502之间形成环腔517,筒体502的下部具有至少一个与罐体501的内腔相连通的出口503;筒体502内的上部固定安装有收渣漏斗504,收渣漏斗504的底部连接有伸出罐体501外的排渣管505;筒体502的中部连接有第五进水管506,第五进水管506沿筒体502的切线方向伸入筒体502内;罐体501的上部内壁上形成环形的收油槽508,收油槽508的截面为U型,并开口朝上,收油槽508上连接有伸出罐体501外的收油管509;环腔517的中部固定有环形的填料层507,填料层507上方的环腔517内设置环形的收水管510,收水管510上连接有伸出罐体501外的第五出水管511。As shown in Figure 6, the slag removal separation tank is a negative pressure slag removal separation tank. The negative pressure slag removal separation tank includes a tank body 501 and a cylinder body 502 located in the tank body 501. The upper end of the cylinder body 502 is open, and the lower end is connected to the tank body. The body 501 is fixed and sealed, and an annular cavity 517 is formed between the tank body 501 and the cylinder body 502. The lower part of the cylinder body 502 has at least one outlet 503 communicating with the inner cavity of the tank body 501; the upper part of the cylinder body 502 is fixedly installed with Slagging funnel 504, the bottom of slagging funnel 504 is connected with slag discharge pipe 505 protruding from the tank body 501; the middle of cylinder body 502 is connected with fifth water inlet pipe 506, and fifth water inlet pipe 506 is along the tangential direction of cylinder body 502 Extend into the cylinder 502; the upper inner wall of the tank body 501 forms an annular oil collection tank 508, the cross section of the oil collection tank 508 is U-shaped, and the opening faces upwards, and the oil collection tank 508 is connected with an oil collection pipe extending outside the tank body 501 509; an annular packing layer 507 is fixed in the middle of the ring chamber 517, and an annular water collection pipe 510 is arranged in the ring chamber 517 above the packing layer 507, and the water collection pipe 510 is connected with a fifth outlet pipe 511 extending outside the tank body 501.
继续结合图6,罐体501的底部固定有位于环腔517内的第一环形吸泥管512,本实施例中第一吸泥管512为上下布置的两个。填料层507上方固定有第二环形吸泥管513。第一环形吸泥管512和第二环形吸泥管513的下底面上均分布有吸泥孔。第一环形吸泥管512和第二环形吸泥管513上分别连通有伸出罐体501外的排泥管514。两个第一环形吸泥管512可以连通后共用一根排泥管514,也可以各用一根排泥管514。第一环形吸泥管512和第二环形吸泥管513结构相同并为现有技术中公知公用的设备,在此不再赘述。Continuing with FIG. 6 , the bottom of the tank body 501 is fixed with a first annular dredge pipe 512 located in the annular cavity 517 , and in this embodiment, there are two first annular dredge pipes 512 arranged up and down. A second annular dredge pipe 513 is fixed above the packing layer 507 . Suction holes are distributed on the lower bottom surfaces of the first annular dredge pipe 512 and the second annular dredge pipe 513 . The first annular mud suction pipe 512 and the second annular mud suction pipe 513 are respectively connected with a mud discharge pipe 514 extending out of the tank body 501 . The two first annular mud suction pipes 512 can be connected to share a mud discharge pipe 514 , or each can use a mud discharge pipe 514 . The first annular dredge pipe 512 and the second annular dredge pipe 513 have the same structure and are well-known and commonly used devices in the prior art, and will not be repeated here.
另外,如图6所示,在环形的收水管510的上方的罐体501内设置有溢流口,溢流口上固定连接有溢流管515,当负压除渣分离罐内进水量过大时,可以通过溢流管515排出罐外,防止未经处理的水直接进入收水管510,影响出水水质。而且,罐体501的中部内壁上固定有环形挡环516,填料层507座在环形挡环516上,环形挡环516起到支撑固定和限位填料层507的作用。填料层507上固定安装有U型通气平衡管217,U型通气平衡管217穿过填料层507使其一部分位于填料层507的上部,一部分位于填料层507的下部。U型通气平衡管217用于平衡填料层507上部和下部的环腔517之间的压力,防止憋压。In addition, as shown in Figure 6, an overflow port is provided in the tank body 501 above the annular water collection pipe 510, and an overflow pipe 515 is fixedly connected to the overflow port. , can be discharged out of the tank through the overflow pipe 515 to prevent untreated water from directly entering the water collection pipe 510 and affecting the quality of the effluent. Moreover, an annular retaining ring 516 is fixed on the inner wall of the middle part of the tank body 501 , and the packing layer 507 is seated on the annular retaining ring 516 , and the annular retaining ring 516 plays a role of supporting, fixing and limiting the packing layer 507 . A U-shaped ventilation balance pipe 217 is fixedly installed on the packing layer 507, and the U-shaped ventilation balancing pipe 217 passes through the packing layer 507 so that a part thereof is located at the top of the packing layer 507, and a part is located at the bottom of the packing layer 507. The U-shaped ventilation balance pipe 217 is used to balance the pressure between the upper and lower annular chambers 517 of the packing layer 507 to prevent pressure from being suppressed.
填料层507可以采用乙丙共聚斜板填料层,乙丙共聚斜板具有优良的化学性能、稳定性能好、比重小、表面光滑和滑泥效果好,避免填料破碎流失现象。The filler layer 507 can be made of ethylene-propylene copolymer slanted plate filler layer. The ethylene-propylene copolymer slanted plate has excellent chemical properties, good stability, small specific gravity, smooth surface and good slippery effect, so as to avoid the phenomenon of filler breaking and loss.
下面结合图6对负压除渣分离罐的工作过程进行介绍:由旋流反应器处理后的采出水经第三出水管306进入第五进水管506,并通过第五进水管506切向进入筒体502内,采出水在筒体502内通过水力旋流与净水药剂充分反应,使反应生成的絮体借助污水中释放的溶解气上浮至水面凝聚成浮渣,下部的水流自筒体502的出口503进入环腔517,然后经沉降分离的清水自下而上穿过填料层507后,进一步拦截水中的絮体,使水经过填料层507后进一步净化,填料层507上方的净化后的清水进入收水管510,最后经第五出水管511排出罐体501外。上浮的浮渣先进入收渣漏斗504中,然后通过排渣管505排出罐体501外。浮油通过收油槽508收集后由收油管509排出罐体501外。罐体501底部和填料层507上部沉积的污泥分别通过第一环形吸泥管512和第二环形吸泥管513定期排出罐体501外。The working process of the negative pressure slag removal separation tank is introduced below in conjunction with Fig. 6: the produced water treated by the cyclone reactor enters the fifth water inlet pipe 506 through the third water outlet pipe 306, and enters tangentially through the fifth water inlet pipe 506 In the cylinder 502, the produced water fully reacts with the water purification agent through the hydrocyclone in the cylinder 502, so that the flocs formed by the reaction float up to the water surface with the help of the dissolved gas released in the sewage to condense into scum, and the water in the lower part flows from the cylinder. The outlet 503 of 502 enters the annular cavity 517, and then the clear water separated by sedimentation passes through the packing layer 507 from bottom to top, and further intercepts the flocs in the water, so that the water is further purified after passing through the packing layer 507, and the purified water above the packing layer 507 The clear water enters the water collection pipe 510, and finally is discharged outside the tank body 501 through the fifth water outlet pipe 511. The floating scum first enters the slag collection funnel 504 and then is discharged out of the tank body 501 through the slag discharge pipe 505 . The floating oil is collected by the oil collection tank 508 and discharged out of the tank body 501 by the oil collection pipe 509 . The sludge deposited on the bottom of the tank body 501 and on the top of the packing layer 507 is regularly discharged out of the tank body 501 through the first annular mud suction pipe 512 and the second annular mud suction pipe 513 respectively.
本实用新型同时公开了一种采出水处理方法,包括如下步骤:The utility model also discloses a method for treating produced water, which comprises the following steps:
1)沉降除油:采用图1所示的沉降除油罐利用采出水中油、水和悬浮物密度的不同,大部分的油上浮、悬浮物下沉而被自然分离,剩余的少部分油和悬浮物进行下一程序;1) Oil removal by sedimentation: The oil removal tank shown in Figure 1 is used to utilize the difference in density of oil, water, and suspended matter in the produced water. Most of the oil floats up and the suspended matter sinks and is naturally separated. The remaining small part of oil and Suspended matter proceeds to the next procedure;
2)旋流反应除油:经步骤1)处理后的采出水进入如前所述的化学调整旋流反应分离装置,并添加2-3种净水药剂进行化学旋流反应,采出水中的油和悬浮物被净水药剂有效捕捉和聚并长大,污泥下沉,浮渣上浮,并有效分离,实现出水水质的净化。2) Cyclone reaction deoiling: the produced water treated in step 1) enters the chemical adjustment cyclone reaction separation device as mentioned above, and adds 2-3 kinds of water purification agents to carry out chemical cyclone reaction, and the produced water The oil and suspended solids are effectively captured and aggregated by the water purification agent, the sludge sinks, the scum floats up, and is effectively separated to achieve the purification of the effluent water quality.
本实用新型的采出水处理方法利用两级处理设施,第一级为利用沉降除油罐的物理法处理,第二级为利用旋流反应化学调整旋流反应分离装置的化学法处理,以弥补单纯物理法处理的不足,能够兼顾水质净化和水质稳定,满足采出水处理后达标回用日益严格的环保要求。The produced water treatment method of the utility model utilizes two-stage treatment facilities, the first stage is the physical method treatment using the sedimentation oil removal tank, and the second stage is the chemical method treatment using the swirl reaction chemistry to adjust the swirl reaction separation device, so as to compensate The shortcomings of pure physical treatment can take into account both water purification and water quality stability, and meet the increasingly stringent environmental protection requirements for the standard reuse of produced water after treatment.
具体的,稠油开采高温采出水首先进入立式竖流式的沉降除油罐,沉降除油罐设置均匀的集配水系统,并且采用上配水、下集水的方式,配水和集水均采用辐射式喇叭口,保证配水和集水的均匀性。在竖流状态下采出水从配水管向上以一定速度流出后,油除了因自身的上浮所获得的在水中的上浮速度外,还受水流向上垂直速度的推动,油将更快到达油层,所需的分离沉降时间缩短。而且油在上升的过程中碰撞聚结而形成上浮油珠并直接变大,并在上浮的过程中与被水流夹带向下流动的油珠间始终存在着对流碰撞聚结的过程,使油聚结成大的油珠而更利于上浮,缩短上浮时间,提高除油效率,上浮至采出水上表面的油进入沉降除油罐的槽壁的收油槽内,然后排出沉降除油罐。采出水中的污泥沉淀至沉降除油罐的底部经负压排泥器排出。Specifically, the high-temperature produced water from heavy oil exploitation first enters the vertical vertical flow oil removal tank, and the oil removal tank is equipped with a uniform water collection and distribution system, and adopts the method of upper water distribution and lower water collection. The radial bell mouth ensures the uniformity of water distribution and collection. After the produced water flows out from the water distribution pipe at a certain speed in the vertical flow state, in addition to the oil’s own floating speed in the water, it is also pushed by the vertical speed of the water flow, so the oil will reach the oil layer faster, so The required separation and settling time is shortened. Moreover, the oil collides and coalesces in the process of rising to form floating oil droplets and directly becomes larger, and there is always a process of convective collision and coalescence between the oil droplets entrained by the water flow and flowing downwards during the upward floating process, so that the oil gathers Forming large oil droplets is more conducive to floating, shortening the floating time and improving the oil removal efficiency. The oil that floats up to the upper surface of the produced water enters the oil receiving tank on the tank wall of the settlement oil removal tank, and then is discharged out of the settlement oil removal tank. The sludge in the produced water settles to the bottom of the sedimentation oil removal tank and is discharged through a negative pressure sludge discharger.
经沉降除油罐处理后的采出水进入化学调整旋流反应分离装置,根据采出水的特性,筛选出需要投加的净水药剂,同时试验出投加时间间隔与混合反应强度,再利用化学调整旋流反应分离装置的紊流逐级变小的涡流场,在工艺上为净水药剂与采出水的混合提供了动力,反应后通过混凝沉降的方式将反应产物絮体与水分离,实现水的净化。同时采出水中含的少量的油上浮并被收集。The produced water treated by the settling oil removal tank enters the chemical adjustment cyclone reaction separation device, and according to the characteristics of the produced water, the water purification agent to be added is screened out, and the time interval of the addition and the mixing reaction intensity are tested at the same time, and then the chemical Adjusting the vortex field where the turbulent flow of the cyclone reaction separation device gradually becomes smaller provides power for the mixing of the water purification agent and the produced water in the process. After the reaction, the flocs of the reaction product are separated from the water by coagulation and sedimentation. Realize water purification. At the same time, a small amount of oil contained in the produced water floats up and is collected.
化学调整旋流反应分离装置可以采用合体式的(仅有一个装置,即图3中示出的旋流反应分离罐),也可以采用分体式的(包含两个装置,即图4中示出的旋流反应器与图5中示出的喷雾除渣分离罐或图6中示出的负压除渣分离罐的结合)。针对含聚合物、超稠油、SAGD采出水油珠粒径小、粘度大,油水不易分离;含气采出水由于水中溶解气较高且不稳定,以上原因易造成絮体上浮,且浮渣层在罐顶部长期聚集使得浮渣层厚度增大,浮渣经出水口流出进入下一段流程,造成罐出水含油、悬浮物含量超标,并为后段流程带来处理压力的情况,采用图5中示出的喷雾除渣分离罐。在罐顶设收渣槽,收渣槽中心设水雾喷嘴。由喷雾将浮渣吹扫至收渣槽内,然后再排出罐外,污泥沉降至喷雾除渣分离罐的底部,并经负压排泥装置排出罐外。图6所示的负压除渣分离罐则是靠负压作用收集上浮至罐液面的浮渣,并排出罐外,污泥沉降至负压除渣分离罐的底部,并经负压排泥装置排出罐外,确保出水水质。The chemically adjusted cyclone reaction separation device can be integrated (only one device, the cyclone reaction separation tank shown in Figure 3), or split (comprising two devices, namely the cyclone reaction separation tank shown in Figure 4). The combination of the cyclone reactor and the spray deslagging separation tank shown in Figure 5 or the negative pressure deslagging separation tank shown in Figure 6). For water containing polymers, ultra-heavy oil, and SAGD production, the oil beads have small particle size and high viscosity, and oil and water are not easy to separate; gas-containing production water is high in dissolved gas and unstable, and the above reasons are likely to cause flocs to float up and scum The long-term accumulation of layers on the top of the tank increases the thickness of the scum layer, and the scum flows out through the water outlet into the next process, causing the tank effluent to contain oil and suspended solids exceeding the standard, and bring treatment pressure to the latter process, as shown in Figure 5 The spray deslagging separation tank shown in. A slag collecting tank is set on the top of the tank, and a water mist nozzle is set in the center of the slag collecting tank. The scum is blown into the slag collecting tank by the spray, and then discharged out of the tank. The sludge settles to the bottom of the spray slag removal separation tank, and is discharged out of the tank through the negative pressure sludge discharge device. The negative pressure slag removal separation tank shown in Figure 6 relies on negative pressure to collect the scum that floats up to the liquid surface of the tank and discharges it out of the tank. The sludge settles to the bottom of the negative pressure slag removal separation tank and is discharged through negative pressure. The mud device is discharged out of the tank to ensure the quality of the effluent.
采出水经过本实用新型的两级处理后,出水含油和悬浮物可达到15mg/L以内,后端辅以过滤即可满足回用要求。解决了高温低油水密度差高乳化度采出水油珠粒径小、油水稳定性强、常规处理流程难度大的问题,使稠油开发中产生的采出水能够达标处理并回用于锅炉,避免稠油开发中产生的采出水(污水)外排污染环境,同时节约了清水产生巨大的经济效益。After the produced water undergoes two-stage treatment of the utility model, the oil and suspended solids in the effluent can reach within 15 mg/L, and the rear end can be supplemented with filtration to meet the reuse requirements. It solves the problems of high temperature, low oil-water density difference, high emulsification degree, small particle size of produced water, strong oil-water stability, and difficult conventional treatment process, so that the produced water generated in the development of heavy oil can be treated up to the standard and reused in the boiler, avoiding The produced water (sewage) produced in the development of heavy oil is discharged to pollute the environment, and at the same time, the clean water is saved to generate huge economic benefits.
本实用新型的代表性实施例得到了详细的描述。这些详细的描述不用于对本实用新型的范围进行限制。本领域技术人员可以在本实用新型的实质和保护范围内,对本实用新型做出各种修改或等同替换,这种修改或等同替换也应视为落在本实用新型的保护范围内。因此,在前述详细描述中的特征的结合不是必要的用于在最宽广的范围内实施本实用新型,并且可替换地仅对本实用新型的特别详细描述的代表性实施例给出教导。此外,为了获得本实用新型的附加有用实施例,在说明书中给出教导的各种不同的特征可通过多种方式结合,然而这些方式没有特别地被例举出来。Representative embodiments of the present invention have been described in detail. These detailed descriptions are not intended to limit the scope of the present invention. Those skilled in the art can make various modifications or equivalent replacements to the utility model within the spirit and protection scope of the utility model, and such modifications or equivalent replacements should also be deemed to fall within the protection scope of the utility model. Therefore, no combination of features in the foregoing detailed description is necessary to practice the invention in its broadest scope, and are instead taught only to particularly detailed representative embodiments of the invention. Furthermore, the various features taught in the specification may be combined in ways not specifically enumerated, in order to obtain additional useful embodiments of the invention.
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