CN105601041A - Advanced treatment device for oil refining wastewater - Google Patents
Advanced treatment device for oil refining wastewater Download PDFInfo
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- 239000002351 wastewater Substances 0.000 title claims abstract description 66
- 238000007670 refining Methods 0.000 title description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 163
- 239000004576 sand Substances 0.000 claims abstract description 80
- 238000005188 flotation Methods 0.000 claims abstract description 73
- 230000003647 oxidation Effects 0.000 claims abstract description 67
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 67
- 238000005273 aeration Methods 0.000 claims abstract description 55
- 238000004062 sedimentation Methods 0.000 claims abstract description 27
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 23
- 238000007667 floating Methods 0.000 claims description 24
- 239000013049 sediment Substances 0.000 claims description 9
- 238000004065 wastewater treatment Methods 0.000 claims description 8
- 230000000694 effects Effects 0.000 claims description 7
- 239000000945 filler Substances 0.000 claims description 7
- 238000007599 discharging Methods 0.000 claims description 6
- 238000009287 sand filtration Methods 0.000 claims description 6
- 239000004744 fabric Substances 0.000 claims description 4
- 230000005855 radiation Effects 0.000 claims description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims 15
- 206010016256 fatigue Diseases 0.000 claims 7
- 230000001174 ascending effect Effects 0.000 claims 6
- 238000006385 ozonation reaction Methods 0.000 claims 2
- 239000002699 waste material Substances 0.000 claims 2
- 239000011148 porous material Substances 0.000 claims 1
- 239000000377 silicon dioxide Substances 0.000 claims 1
- 238000000926 separation method Methods 0.000 abstract description 24
- 239000010802 sludge Substances 0.000 abstract description 23
- 238000005406 washing Methods 0.000 abstract description 22
- 230000001105 regulatory effect Effects 0.000 abstract description 17
- 239000002893 slag Substances 0.000 abstract description 10
- 238000002156 mixing Methods 0.000 abstract description 6
- 239000003921 oil Substances 0.000 description 35
- 238000000034 method Methods 0.000 description 16
- 238000011144 upstream manufacturing Methods 0.000 description 11
- 239000000126 substance Substances 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 4
- 239000003344 environmental pollutant Substances 0.000 description 4
- 230000005484 gravity Effects 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 231100000719 pollutant Toxicity 0.000 description 4
- 238000005842 biochemical reaction Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 239000013505 freshwater Substances 0.000 description 2
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- 239000007788 liquid Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 238000005191 phase separation Methods 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000010612 desalination reaction Methods 0.000 description 1
- 239000005446 dissolved organic matter Substances 0.000 description 1
- 238000000909 electrodialysis Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000012982 microporous membrane Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 150000002825 nitriles Chemical class 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 150000002989 phenols Chemical class 0.000 description 1
- 238000000053 physical method Methods 0.000 description 1
- 238000011268 retreatment Methods 0.000 description 1
- 238000012163 sequencing technique Methods 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 150000003568 thioethers Chemical class 0.000 description 1
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Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/36—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
- C02F2103/365—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
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- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
本发明涉及一种炼油废水深度处理装置,包括废水调节池、高效气浮池、高级氧化池、折流式曝气生化滤池、流砂滤池和清水池;高效气浮池从下至上依次为混合区和分离区,分离区包括集水区和位于集水区内的集油集渣区;高级氧化池包括曝气氧化区和沉淀区,曝气氧化区底部设置有臭氧曝气盘,臭氧曝气盘的上方设有高级氧化池布水支管,高级氧化池布水支管连接高级氧化池进水管,臭氧曝气盘通过曝气管连接有高级氧化池外的鼓风机,鼓风机通过管道连通臭氧发生器;折流式曝气生化滤池中上部为圆柱形、下部为圆锥形结构,包括下流区、上流区和污泥区;流砂滤池包括布水区、洗砂区和砂滤区。
The invention relates to a refinery wastewater advanced treatment device, comprising a wastewater regulating tank, a high-efficiency air flotation tank, an advanced oxidation tank, a baffle type aerated biochemical filter, a quicksand filter and a clear water tank; the high-efficiency air flotation tank is a mixing zone from bottom to top and the separation area, the separation area includes the water catchment area and the oil and slag collection area located in the water catchment area; the advanced oxidation tank includes the aeration oxidation area and the sedimentation area, the bottom of the aeration oxidation area is equipped with an ozone aeration plate, and the ozone aeration The water distribution branch pipe of the advanced oxidation tank is arranged on the top of the plate, and the water distribution branch pipe of the advanced oxidation tank is connected to the water inlet pipe of the advanced oxidation tank. The ozone aeration plate is connected to the blower outside the advanced oxidation tank through the aeration pipe, and the blower is connected to the ozone generator through the pipe; The upper part of the baffle type aerated biochemical filter is cylindrical and the lower part is conical, including the downstream area, the upper flow area and the sludge area; the quicksand filter includes the water distribution area, the sand washing area and the sand filter area.
Description
技术领域technical field
本发明涉及环保技术领域,具体涉及一种炼油废水深度处理装置。The invention relates to the technical field of environmental protection, in particular to an advanced treatment device for oil refining wastewater.
背景技术Background technique
随着社会的发展和人民生活水平的不断提高,对水资源的需求量也在日益增加。水资源的严重短缺和水污染问题已成为我国经济建设和社会发展的制约因素。污水回用是缓解我国水资源紧缺的重要途径之一。炼油加工企业是用水大户,也是污水排放大户。With the development of society and the continuous improvement of people's living standards, the demand for water resources is also increasing. The severe shortage of water resources and water pollution have become the restrictive factors of our country's economic construction and social development. Sewage reuse is one of the important ways to alleviate the shortage of water resources in my country. Oil refining and processing enterprises are major users of water consumption and discharge of sewage.
炼油废水是一种集悬浮油、乳化油、溶解性有机物及盐分于一体的多相体系,主要污染物包括石油类、硫化物、COD、BOD、悬浮物、挥发酚、氨氮以及氯离子等,悬浮物及盐出自电脱盐工艺,油及溶解于污水中的硫化物、酚、氰化物等与原油加工工艺有关,炼油废水不易降解、可生化性差,处理难度大。Refining wastewater is a multiphase system integrating suspended oil, emulsified oil, dissolved organic matter and salt. The main pollutants include petroleum, sulfide, COD, BOD, suspended solids, volatile phenol, ammonia nitrogen and chloride ions, etc. Suspended solids and salts come from the electric desalination process. Oil and sulfides, phenols, and cyanides dissolved in sewage are related to the crude oil processing process. Refinery wastewater is not easy to degrade, has poor biodegradability, and is difficult to treat.
炼油废水深度处理的方法分为物理方法、化学方法和生物处理方法。物理处理方法包括过滤、沉淀、膜分离、吸附和空气吹脱等。化学处理方法有絮凝、电渗析、离子交换、化学氧化、消毒、石灰处理、电化学和光化学处理等。生物处理技术包括活性污泥法、生物膜法和自然生物处理法。生物膜法包括传统的生物滤池、生物转盘、生物接触氧化、新型的生物流化床、移动床生物膜反应器和复合式生物膜反应器。复合式生物膜反应器主要有升流式厌氧污泥床、厌氧生物滤池、微孔膜生物反应器、序批式生物膜反应器和曝气生物滤池。炼油废水深度处理技术优选各种方法,形成组合工艺技术,将废水中的污染物质分离除去,或将其转化为无公害物质,使水体得到净化。The advanced treatment methods of oil refinery wastewater are divided into physical methods, chemical methods and biological treatment methods. Physical treatment methods include filtration, precipitation, membrane separation, adsorption and air stripping, etc. Chemical treatment methods include flocculation, electrodialysis, ion exchange, chemical oxidation, disinfection, lime treatment, electrochemical and photochemical treatment, etc. Biological treatment technologies include activated sludge method, biofilm method and natural biological treatment method. Biofilm methods include traditional biofilters, biological turntables, biological contact oxidation, new biological fluidized beds, moving bed biofilm reactors and composite biofilm reactors. Composite biofilm reactors mainly include upflow anaerobic sludge bed, anaerobic biological filter, microporous membrane bioreactor, sequencing batch biofilm reactor and aerated biological filter. The advanced treatment technology of oil refinery wastewater optimizes various methods to form a combined process technology to separate and remove the pollutants in the wastewater, or convert them into pollution-free substances, so as to purify the water body.
现有炼油厂废水的深度处理技术和装置存在着一些缺陷,如污染物去除不彻底、去除的污染物的种类单一,回用水的氯离子、氨氮、电导率都较新鲜水高,pH值较新鲜水低等。Existing refinery wastewater advanced treatment technologies and devices have some defects, such as incomplete removal of pollutants, single types of pollutants removed, chloride ions, ammonia nitrogen, and electrical conductivity of reused water are higher than those of fresh water, and the pH value is lower. Fresh water is low.
发明内容Contents of the invention
本发明要解决的技术问题是:为了解决上述炼油废水深度处理中的问题,本发明提供一种炼油废水深度处理装置。The technical problem to be solved by the present invention is: in order to solve the above-mentioned problems in the advanced treatment of oil refinery wastewater, the present invention provides an advanced treatment device for oil refinery wastewater.
本发明解决其技术问题所采用的技术方案是:一种炼油废水深度处理装置,包废水调节池、高效气浮池、高级氧化池、折流式曝气生化滤池、流砂滤池和清水池;废水调节池、高效气浮池、高级氧化池、折流式曝气生化滤池、流砂滤池和清水池依次连通。The technical solution adopted by the present invention to solve the technical problem is: a refinery wastewater advanced treatment device, including a wastewater regulating tank, a high-efficiency air flotation tank, an advanced oxidation tank, a baffle type aerated biochemical filter, a quicksand filter and a clear water tank; The wastewater regulating tank, the high-efficiency air flotation tank, the advanced oxidation tank, the baffle type aerated biochemical filter, the quicksand filter and the clear water tank are connected in sequence.
所述的废水调节池包括废水调节池进水管和废水调节池出水管,用于调节废水的水质和水量;The waste water regulating pond includes a waste water regulating pond inlet pipe and a waste water regulating pond outlet pipe for regulating the water quality and quantity of waste water;
所述的高效气浮池包括高效气浮池进水管和用于排出处理后水的高效气浮池出水管,所述的高效气浮池从下至上依次为混合区和分离区;所述的分离区包括集水区和位于集水区内的集油集渣区;所述高效气浮池的混合区的上部设置有高效气浮池曝气盘,所述的高效气浮池曝气盘的上方设有高效气浮池布水支管,所述的高效气浮池布水支管连接高效气浮池进水管,所述的高效气浮池曝气盘连接有高效气浮池外的高效气浮池鼓风机;所述的分离区内设有高效气浮池三相分离器,所述的高效气浮池三相分离器包括导流板和位于导流板下方与导流板配合使用的三角导流环,所述的三角导流环安装在高效气浮池的内壁上,所述的导流板的上部与分离区的形状相同,所述的导流板的下部呈喇叭状,所述的导流板的下部的内径大于三角导流环的内径;所述的分离区外壁的上部设有高效气浮池溢水堰,所述的高效气浮池溢水堰与高效气浮池出水管相连;所述的集油集渣区布设有油渣刮板和油渣槽;废水从下往上溢时,水、油与浮渣一起通过三角导流环进入导流板的下部,油与浮渣继续往上进入集油集渣区,水通过导流板与三角导流环之间的间隙进入集水区;为了废水处理的效果更好,所述的高效气浮池布水支管设置成同心圆形状或十字形状,布水支管上具有水平辐射出水口;进一步,所述的高效气浮池曝气盘是均匀设置有微孔的微孔式曝气盘。The high-efficiency air flotation tank includes a high-efficiency air flotation tank inlet pipe and a high-efficiency air flotation tank outlet pipe for discharging treated water. The high-efficiency air flotation tank is composed of a mixing zone and a separation zone from bottom to top; the separation zone includes a collection The water area and the oil and slag collection area located in the water collection area; the upper part of the mixing area of the high-efficiency air flotation tank is provided with a high-efficiency air flotation tank aeration disc, and the top of the high-efficiency air flotation tank aeration disc is provided with a high-efficiency air flotation tank Water distribution branch pipe, the water distribution branch pipe of the high-efficiency air flotation tank is connected to the water inlet pipe of the high-efficiency air flotation tank, and the aeration plate of the high-efficiency air flotation tank is connected to the blower of the high-efficiency air flotation tank outside the high-efficiency air flotation tank; The three-phase separator of the air flotation tank, the three-phase separator of the high-efficiency air flotation tank includes a deflector and a triangular guide ring located below the deflector and used in conjunction with the deflector. The triangular guide ring is installed on the high-efficiency gas On the inner wall of the floating pool, the top of the deflector has the same shape as the separation zone, the bottom of the deflector is trumpet-shaped, and the inner diameter of the lower part of the deflector is greater than the inner diameter of the triangular guide ring; The upper part of the outer wall of the separation area is provided with a high-efficiency air flotation tank overflow weir, and the high-efficiency air flotation tank overflow weir is connected with the high-efficiency air flotation tank outlet pipe; the oil and slag collection area is equipped with oil residue scrapers and oil residue tanks When the wastewater overflows from bottom to top, water, oil and scum enter the lower part of the deflector through the triangular guide ring, and the oil and scum continue to enter the oil and slag collection area upwards, and the water passes through the deflector and the triangular guide. The gap between the flow rings enters the catchment area; in order to achieve a better effect of wastewater treatment, the water distribution branch pipe of the high-efficiency air flotation pool is set in a concentric circle shape or a cross shape, and the water distribution branch pipe has a horizontal radiation outlet; further, the The aeration disc of the high-efficiency air flotation tank described above is a microporous aeration disc with micropores uniformly arranged therein.
所述的高效气浮池出水管与高级氧化池进水管连通。The outlet pipe of the high-efficiency air flotation tank is connected with the water inlet pipe of the advanced oxidation tank.
所述的高级氧化池包括曝气氧化区和沉淀区,曝气氧化区底部设置有臭氧曝气盘,所述的臭氧曝气盘的上方设有高级氧化池布水支管,所述的高级氧化池布水支管连接高级氧化池进水管,所述的臭氧曝气盘通过曝气管连接有高级氧化池外的臭氧鼓风机,臭氧鼓风机通过管道连通臭氧发生器;所述沉淀区内设有挡板,该挡板与沉淀池的内壁形成作为废水进入沉淀区的废水流道,沉淀区的出口上部设有高级氧化池溢水堰;沉淀区底部设计成锥形结构,在沉淀区底部设置有沉淀物排放阀。The advanced oxidation tank includes an aeration oxidation zone and a sedimentation zone, an ozone aeration pan is arranged at the bottom of the aeration oxidation zone, and an advanced oxidation tank water distribution branch is arranged above the ozone aeration pan. The pool water branch pipe is connected to the water inlet pipe of the advanced oxidation tank, and the ozone aeration pan is connected to the ozone blower outside the advanced oxidation tank through the aeration pipe, and the ozone blower is connected to the ozone generator through a pipeline; a baffle is provided in the precipitation area , the baffle and the inner wall of the sedimentation tank form a waste water flow channel for the wastewater to enter the sedimentation area. The upper part of the outlet of the sedimentation area is provided with an overflow weir of the advanced oxidation tank; the bottom of the sedimentation area is designed as a conical structure, and the sediment discharge valve.
所述折流式曝气生化滤池中上部为圆柱形、下部为圆锥形结构,包括下流区、上流区和污泥区;所述下流区位于折流式曝气生化滤池的圆柱形结构的中部,为圆柱形结构,下流区上部设有折流式曝气生化滤池进水管和折流式曝气生化滤池布水管,下流区中部设有下流区填料,下流区下部设有下流区曝气管,所述下流区的底部设有折流板,所述的折流板的纵断面呈喇叭状;所述上流区位于下流区的外围、折流板的上部,上流区中部设有上流区填料,下部设有上流区曝气管,上流区上部的出口处设有折流式曝气生化滤池溢水堰;所述污泥区位于折流式曝气生化滤池的底部、下流区和上流区的下部,污泥区的底部设有污泥排放阀。The upper part of the baffle type aerated biochemical filter is cylindrical and the lower part is a conical structure, including a downstream area, an upper flow area and a sludge area; the downstream area is located in the cylindrical structure of the baffled aerated biochemical filter The middle part is a cylindrical structure. The upper part of the downstream area is equipped with a baffle type aerated biochemical filter inlet pipe and a baffled aerated biochemical filter water distribution pipe. Area aeration pipe, the bottom of the downstream area is provided with a baffle plate, and the longitudinal section of the baffle plate is trumpet-shaped; There is filler in the upstream area, the lower part is equipped with an aeration pipe in the upstream area, and the outlet of the upper part of the upstream area is provided with an overflow weir of a baffled aerated biochemical filter; the sludge area is located at the bottom of the baffled biochemical aerated filter, Sludge discharge valves are provided at the bottom of the downflow zone and the upflow zone, and the bottom of the sludge zone.
所述流砂滤池包括流砂滤池进水管和用于排出处理后水的流砂滤池出水管,所述的流砂滤池包括布水区、洗砂区和砂滤区;所述的布水区位于流砂滤池的下部,布水区设有流砂滤池布水管,流砂滤池布水管连接流砂滤池进水管,为了废水处理的效果更好,所述的流砂滤池布水管设置成同心圆形状,流砂滤池布水管上具有向下辐射出水口;所述的洗砂区位于流砂滤池的中心,为圆柱形筒状结构,圆柱形筒状结构下端开口位于流砂滤池的最底部,圆柱形筒状结构上端开口位于流砂滤池的上部,洗砂区的中部设有气提管,气提管连接流砂滤池外的流砂滤池鼓风机,洗砂区的上部设有砂水沉淀分离区,砂水沉淀分离区的上部设有洗砂区溢水堰,洗砂区溢水堰连接洗砂水排放管和折流式曝气生化滤池进水管,砂水沉淀分离区的下部设有回砂通道;所述的砂滤区位于洗砂区的外围,砂滤区内充填有细砂,砂滤区上部设有砂滤区溢水堰,砂滤区溢水堰连接流砂滤池出水管,流砂滤池过滤处理后的水进入清水池回用。The quicksand filter includes a quicksand filter inlet pipe and a quicksand filter outlet pipe for discharging treated water, and the quicksand filter includes a water distribution area, a sand washing area and a sand filter area; the water distribution area Located at the lower part of the quicksand filter, the water distribution area is provided with a quicksand filter water distribution pipe, and the quicksand filter water distribution pipe is connected to the quicksand filter water inlet pipe. In order to achieve a better wastewater treatment effect, the quicksand filter water distribution pipes are arranged in concentric circles Shape, the water distribution pipe of the quicksand filter has a downward radiating water outlet; the sand washing area is located in the center of the quicksand filter, and is a cylindrical cylindrical structure, and the lower end opening of the cylindrical cylindrical structure is located at the bottom of the quicksand filter. The upper opening of the cylindrical cylindrical structure is located on the upper part of the quicksand filter, and the middle part of the sand washing area is equipped with an air lift pipe, which is connected to the quick sand filter blower outside the quick sand filter, and the upper part of the sand washing area is equipped with sand and water sedimentation and separation The upper part of the sand-water sedimentation and separation area is equipped with an overflow weir for the sand washing area, which is connected to the sand washing water discharge pipe and the inlet pipe of the baffle type aerated biochemical filter. Sand channel; the sand filter area is located at the periphery of the sand washing area, filled with fine sand in the sand filter area, the sand filter area overflow weir is provided on the upper part of the sand filter area, and the sand filter area overflow weir is connected to the outlet pipe of the quicksand filter, and the quicksand The water filtered and treated by the filter enters the clean water pool for reuse.
一种采用上述炼油废水深度处理装置进行废水处理的方法,具有如下步骤:A method for wastewater treatment using the above-mentioned refinery wastewater advanced treatment device has the following steps:
①废水通过废水调节池进水管进入废水调节池,调节水质和水量。①Wastewater enters the wastewater regulating tank through the inlet pipe of the wastewater regulating tank to adjust the water quality and quantity.
②然后废水通过高效气浮池进水管进入高效气浮池的中下部;位于高效气浮池进水管下方的高效气浮池曝气盘产生大量细小气泡,高效气浮池曝气盘产生的细小气泡与浮油、浮渣粘附形成混合体在浮力作用下上升,在高效气浮池三相分离器的作用下,混合体上升至集油集渣区,在油渣刮板的作用下,浮油和浮渣进入油渣槽并被清理外运;分离处理后的水在高效气浮池三相分离区导流板作用下进入高效气浮池集水区,通过高效气浮池溢水堰、高效气浮池出水管进入高级氧化池进水管。②Then the waste water enters the middle and lower part of the high-efficiency air flotation tank through the inlet pipe of the high-efficiency air flotation tank; The scum adheres to form a mixture that rises under the action of buoyancy. Under the action of the three-phase separator in the high-efficiency air flotation tank, the mixture rises to the oil and slag collection area. Under the action of the oil slag scraper, the slick oil and scum enter The oil residue tank is cleaned and shipped out; the water after separation and treatment enters the water collection area of the high-efficiency air flotation tank under the action of the deflector in the three-phase separation area of the high-efficiency air flotation tank, and enters the advanced oxidation through the overflow weir of the high-efficiency air flotation tank and the outlet pipe of the high-efficiency air flotation tank Pool inlet pipe.
③废水通过高级氧化池进水管以及高级氧化池布水支管进入高级氧化池的中下部;位于高级氧化池布水支管下方的臭氧曝气盘产生大量细小气泡把废水中的大分子物质氧化成易于吸收和吸附的小分子物质,氧化分解后的废水进入沉淀区的废水流道,高级氧化池三相分离器实现固液分离;沉淀物在重力的作用下下沉到高级氧化池沉淀区的下部,通过底部的沉淀物排放阀排出;废水通过高级氧化池溢水堰、高级氧化池出水管进入折流式曝气生化滤池进水管。③ The waste water enters the middle and lower part of the advanced oxidation tank through the water inlet pipe of the advanced oxidation tank and the water distribution branch pipe of the advanced oxidation tank; The small molecular substances absorbed and adsorbed, the oxidized and decomposed wastewater enters the wastewater flow channel of the sedimentation area, and the three-phase separator of the advanced oxidation tank realizes solid-liquid separation; the sediment sinks to the lower part of the sedimentation area of the advanced oxidation tank under the action of gravity , discharged through the sediment discharge valve at the bottom; waste water enters the water inlet pipe of the baffled aerated biochemical filter through the overflow weir of the advanced oxidation tank and the outlet pipe of the advanced oxidation tank.
④废水通过折流式曝气生化滤池进水管、折流式曝气生化滤池布水管进入折流式曝气生化滤池的下流区,下流区曝气管产生的空气与废水在下流区填料中交汇发生生化反应,同时下流区填料对废水进行过滤,废水通过折流板后进入上流区,在上流区填料中发生生化反应,同时上流区填料对废水进行过滤,下流区和上流区产生的污泥下沉到污泥区,通过污泥区底部的污泥排放阀排放出去,折流式曝气生化滤池处理后的水通过折流式曝气生化滤池溢水堰进入流砂滤池进水管。④Wastewater enters the downstream area of the baffled aerated biochemical filter through the water inlet pipe of the baffled aerated biochemical filter and the water distribution pipe of the baffled aerated biochemical filter. Biochemical reactions occur at the intersection of the fillers, and at the same time, the fillers in the downstream area filter the wastewater. The sludge sinks to the sludge area and is discharged through the sludge discharge valve at the bottom of the sludge area, and the water treated by the baffle type aerated biochemical filter enters the quicksand filter through the overflow weir of the baffle type aerated biochemical filter inlet pipe.
⑤废水通过流砂滤池进水管、流砂滤池布水管进入流砂滤池的下部,流砂滤池布水管实现均匀布水,废水进入砂滤区,废水中的污染物被进一步过滤,然后废水穿过砂滤区由砂滤区溢水堰和流砂滤池出水管进入清水池回用;流砂滤池鼓风机产生的气流带动洗砂区中的砂和水向上流动,同时对砂进行冲洗,气流带动洗砂区中的砂和水进入砂水沉淀分离区,由于砂和水的比重不同,细砂沉淀下去并通过回砂通道流入砂滤区,实现砂滤区中的细砂不断从上往下的移动,砂水沉淀分离区中的水通过洗砂区溢水堰和洗砂水排放管进入折流式曝气生化滤池进行再处理。⑤Wastewater enters the lower part of the quicksand filter through the water inlet pipe of the quicksand filter and the water distribution pipe of the quicksand filter. The water distribution pipe of the quicksand filter realizes uniform water distribution, and the waste water enters the sand filter area. In the sand filter area, the overflow weir in the sand filter area and the outlet pipe of the quicksand filter enter the clear water tank for reuse; the airflow generated by the blower in the quicksand filter drives the sand and water in the sand washing area to flow upwards, and at the same time the sand is washed, and the airflow drives the sand washing The sand and water in the zone enter the sand-water sedimentation and separation zone. Due to the different specific gravity of sand and water, the fine sand settles down and flows into the sand filter zone through the sand return channel, so that the fine sand in the sand filter zone moves from top to bottom continuously. , the water in the sand-water sedimentation and separation area enters the baffle type aerated biochemical filter for retreatment through the overflow weir in the sand washing area and the sand washing water discharge pipe.
⑥高级氧化池产生的沉淀物和折流式曝气生化滤池产生的污泥经浓缩、脱水后外运。⑥ The sediment produced by the advanced oxidation tank and the sludge produced by the baffle type aerated biochemical filter are concentrated and dehydrated before being transported abroad.
本发明的有益效果是:因地制宜,基建投资少,维护方便,能耗较低,对废水具有比较好的处理效果,能够实现污水资源化,对污水进行综合利用。The beneficial effects of the invention are: adapting measures to local conditions, less infrastructure investment, convenient maintenance, lower energy consumption, better treatment effect on waste water, realizing resource utilization of waste water and comprehensive utilization of waste water.
附图说明Description of drawings
下面结合附图和实施例对本发明进一步说明。The present invention will be further described below in conjunction with the accompanying drawings and embodiments.
图1是本发明实施例高效气浮池的结构示意图。Figure 1 is a schematic structural view of a high-efficiency air flotation tank according to an embodiment of the present invention.
图1中:1.高效气浮池,1-1.高效气浮池进水管,1-2.高效气浮池布水支管,1-3.混合区,1-4.集水区,1-5.集油集渣区,1-6.高效气浮池曝气盘,1-7.高效气浮池鼓风机,1-8.高效气浮池三相分离器,1-9.高效气浮池溢水堰,1-10.油渣刮板,1-11.油渣槽。In Figure 1: 1. High-efficiency air flotation tank, 1-1. High-efficiency air flotation tank inlet pipe, 1-2. High-efficiency air flotation tank water distribution branch pipe, 1-3. Mixing area, 1-4. Water collection area, 1-5. Oil collection and slag collection area, 1-6. High-efficiency air flotation tank aeration disc, 1-7. High-efficiency air flotation tank blower, 1-8. High-efficiency air flotation tank three-phase separator, 1-9. High-efficiency air flotation tank overflow weir, 1- 10. Oil residue scraper, 1-11. Oil residue tank.
图2是本发明实施例高级氧化池的结构示意图。Fig. 2 is a schematic structural diagram of an advanced oxidation pool according to an embodiment of the present invention.
图2中:2.高级氧化池,2-1.曝气氧化区,2-2.沉淀区,2-3.臭氧曝气盘,2-4.高级氧化池布水支管,2-5.高级氧化池进水管,2-6.臭氧鼓风机,2-7.臭氧发生器,2-8.挡板,2-9.高级氧化池三相分离器,2-10.高级氧化池溢水堰,2-11.沉淀物排放阀。In Figure 2: 2. Advanced oxidation tank, 2-1. Aeration oxidation zone, 2-2. Sedimentation zone, 2-3. Ozone aeration disc, 2-4. Advanced oxidation tank water branch pipe, 2-5. Advanced oxidation tank inlet pipe, 2-6. Ozone blower, 2-7. Ozone generator, 2-8. Baffle, 2-9. Advanced oxidation tank three-phase separator, 2-10. Advanced oxidation tank overflow weir, 2-11. Sediment discharge valve.
图3是本发明实施例折流式曝气生化滤池的结构示意图。Fig. 3 is a schematic structural view of a baffle type aerated biochemical filter according to an embodiment of the present invention.
图3中:3.折流式曝气生化滤池,3-1.下流区,3-2.上流区,3-3.污泥区,3-4.折流式曝气生化滤池进水管,3-5.折流式曝气生化滤池布水管,3-6.下流区填料,3-7.下流区曝气管,3-8.折流板,3-9.上流区填料,3-10.折流式曝气生化滤池溢水堰,3-11.污泥排放阀。Among Fig. 3: 3. baffle type aerated biochemical filter, 3-1. downstream area, 3-2. upflow area, 3-3. sludge area, 3-4. baffle type aerated biochemical filter enters Water pipe, 3-5. Distributing pipe of baffled aerated biochemical filter, 3-6. Filling in downstream area, 3-7. Aeration pipe in downstream area, 3-8. Baffle plate, 3-9. Filling in upstream area , 3-10. Baffled aerated biochemical filter overflow weir, 3-11. Sludge discharge valve.
图4是本发明实施例流砂滤池的结构示意图。Fig. 4 is a schematic structural view of a quicksand filter according to an embodiment of the present invention.
图4中:4.流砂滤池,4-1.流砂滤池进水管,4-2.流砂滤池布水管,4-3.气提管,4-4.流砂滤池鼓风机,4-5.洗砂区溢水堰,4-6.回砂通道,4-7.砂滤区溢水堰。Among Fig. 4: 4. quicksand filter, 4-1. quicksand filter inlet pipe, 4-2. quicksand filter cloth water pipe, 4-3. gas lift pipe, 4-4. quicksand filter air blower, 4-5 . Sand washing area overflow weir, 4-6. Sand return channel, 4-7. Sand filter area overflow weir.
图5是本发明实施例的工艺流程图。Fig. 5 is a process flow diagram of an embodiment of the present invention.
具体实施方式detailed description
现在结合附图对本发明作进一步详细的说明。这些附图均为简化的示意图,仅以示意方式说明本发明的基本结构,因此其仅显示与本发明有关的构成。The present invention is described in further detail now in conjunction with accompanying drawing. These drawings are all simplified schematic diagrams, and only illustrate the basic structure of the present invention in a schematic manner, so they only show the configurations related to the present invention.
实施例Example
如图1~图5所示,本发明一种炼油废水深度处理装置,包废水调节池、高效气浮池1、高级氧化池2、折流式曝气生化滤池3、流砂滤池4和清水池;废水调节池、高效气浮池1、高级氧化池2、折流式曝气生化滤池3、流砂滤池4和清水池依次连通。As shown in Figures 1 to 5, a refinery wastewater advanced treatment device of the present invention includes a wastewater regulating tank, a high-efficiency air flotation tank 1, an advanced oxidation tank 2, a baffle type aerated biochemical filter 3, a quicksand filter 4 and clear water pool; wastewater regulating pool, high-efficiency air flotation pool 1, advanced oxidation pool 2, baffle type aerated biochemical filter 3, quicksand filter 4 and clear water pool are connected in sequence.
所述的废水调节池包括废水调节池进水管和废水调节池出水管,用于调节废水的水质和水量;The waste water regulating pond includes a waste water regulating pond inlet pipe and a waste water regulating pond outlet pipe for regulating the water quality and quantity of waste water;
所述的高效气浮池1包括高效气浮池进水管1-1和用于排出处理后水的高效气浮池出水管,所述的高效气浮池从下至上依次为混合区1-3和分离区;所述的分离区包括集水区1-4和位于集水区内的集油集渣区1-5;所述高效气浮池的混合区1-3的上部设置有高效气浮池曝气盘1-6,所述的高效气浮池曝气盘的上方设有高效气浮池布水支管1-2,所述的高效气浮池布水支管连接高效气浮池进水管1-1,所述的高效气浮池曝气盘1-6连接有高效气浮池外的高效气浮池鼓风机;所述的分离区内设有高效气浮池三相分离器1-8,所述的高效气浮池三相分离器1-8包括导流板和位于导流板下方与导流板配合使用的三角导流环,所述的三角导流环安装在高效气浮池的内壁上,所述的导流板的上部与分离区的形状相同,所述的导流板的下部呈喇叭状,所述的导流板的下部的内径大于三角导流环的内径;所述的分离区外壁的上部设有高效气浮池溢水堰1-9,所述的高效气浮池溢水堰1-9与高效气浮池出水管相连;所述的集油集渣区1-5布设有油渣刮板1-10和油渣槽1-11;废水从下往上溢时,水、油与浮渣一起通过三角导流环进入导流板的下部,油与浮渣继续往上进入集油集渣区1-5,水通过导流板与三角导流环之间的间隙进入集水区1-4;为了废水处理的效果更好,所述的高效气浮池布水支管1-2设置成同心圆形状或十字形状,布水支管上具有水平辐射出水口;进一步,所述的高效气浮池曝气盘是均匀设置有微孔的微孔式曝气盘。The high-efficiency air flotation tank 1 includes a high-efficiency air flotation tank inlet pipe 1-1 and a high-efficiency air flotation tank outlet pipe for discharging treated water, and the high-efficiency air flotation tank is a mixing zone 1-3 and a separation zone from bottom to top; The separation zone includes a water collection area 1-4 and an oil and slag collection area 1-5 located in the water collection area; the upper part of the mixing area 1-3 of the high-efficiency air flotation tank is provided with an aeration disc 1 of the high-efficiency air flotation tank -6. The high-efficiency air flotation tank water distribution branch pipe 1-2 is arranged above the aeration disc of the high-efficiency air flotation tank. The floating tank aeration disc 1-6 is connected with a high-efficiency air flotation tank blower outside the high-efficiency air flotation tank; the described separation zone is provided with a high-efficiency air flotation tank three-phase separator 1-8, and the high-efficiency air flotation tank three-phase separator 1- 8 includes a deflector and a triangular deflector ring located below the deflector and used in conjunction with the deflector. The triangular deflector ring is installed on the inner wall of the high-efficiency air flotation pool. The upper part of the deflector and the separation area The shapes are the same, the lower part of the deflector is trumpet-shaped, and the inner diameter of the lower part of the deflector is larger than the inner diameter of the triangular guide ring; the upper part of the outer wall of the separation zone is provided with a high-efficiency air flotation tank overflow weir 1 -9, the overflow weir 1-9 of the high-efficiency air flotation tank is connected to the outlet pipe of the high-efficiency air flotation tank; the oil and residue collection area 1-5 is equipped with an oil residue scraper 1-10 and an oil residue tank 1-11; When the waste water overflows from the bottom to the top, water, oil and scum enter the lower part of the deflector through the triangular guide ring, and the oil and scum continue to enter the oil and slag collection area 1-5 upwards, and the water passes through the deflector and the scum. The gap between the triangular diversion rings enters the catchment area 1-4; in order to achieve a better wastewater treatment effect, the water distribution branch pipe 1-2 of the high-efficiency air flotation pool is set in a concentric circle shape or a cross shape, and the water distribution branch pipe has The water outlet is horizontally radiated; further, the aeration disc of the high-efficiency air flotation tank is a microporous aeration disc uniformly provided with micropores.
所述的高效气浮池出水管与高级氧化池进水管2-5连通。The outlet pipe of the high-efficiency air flotation tank communicates with the water inlet pipe 2-5 of the advanced oxidation tank.
所述的高级氧化池2包括曝气氧化区2-1和沉淀区2-2,曝气氧化区底部设置有臭氧曝气盘2-3,所述的臭氧曝气盘的上方设有高级氧化池布水支管2-4,所述的高级氧化池布水支管2-4连接高级氧化池进水管2-5,所述的臭氧曝气盘2-3通过曝气管连接有高级氧化池外的臭氧鼓风机2-6,臭氧鼓风机2-6通过管道连通臭氧发生器2-7;所述沉淀区内设有挡板2-8,该挡板与沉淀池的内壁形成作为废水进入沉淀区的废水流道,沉淀区的出口处设有高级氧化池三相分离器2-9,沉淀区的出口上部设有高级氧化池溢水堰2-10,沉淀区底部设计成锥形结构,在沉淀区底部设置有沉淀物排放阀2-11。The advanced oxidation tank 2 includes an aeration oxidation zone 2-1 and a precipitation zone 2-2, the bottom of the aeration oxidation zone is provided with an ozone aeration pan 2-3, and the top of the ozone aeration pan is provided with an advanced oxidation The water distribution branch pipe 2-4 of the pool, the water distribution branch pipe 2-4 of the advanced oxidation pool is connected to the water inlet pipe 2-5 of the advanced oxidation pool, and the ozone aeration plate 2-3 is connected to the outside of the advanced oxidation pool through the aeration pipe. The ozone blower 2-6, the ozone blower 2-6 communicates with the ozone generator 2-7 through the pipeline; The baffle plate 2-8 is provided in the described settling area, and this baffle plate forms with the inner wall of the settling tank as the waste water enters the settling area The wastewater flow channel, the outlet of the sedimentation area is provided with an advanced oxidation tank three-phase separator 2-9, the upper part of the outlet of the sedimentation area is equipped with an advanced oxidation tank overflow weir 2-10, and the bottom of the sedimentation area is designed as a conical structure. The bottom is provided with a sediment discharge valve 2-11.
所述折流式曝气生化滤池3的中上部为圆柱形、下部为圆锥形结构,包括下流区3-1、上流区3-2和污泥区3-3;所述下流区3-1位于折流式曝气生化滤池的圆柱形结构的中部,为圆柱形结构,下流区上部设有折流式曝气生化滤池进水管3-4和折流式曝气生化滤池布水管3-5,下流区中部设有下流区填料3-6,下流区下部设有下流区曝气管3-7,所述下流区的底部设有折流板3-8,所述的折流板3-8的纵断面呈喇叭状;所述上流区3-2位于下流区3-1的外围、折流板的上部,上流区中部设有上流区填料3-9,下部设有上流区曝气管,上流区上部的出口处设有折流式曝气生化滤池溢水堰3-10;所述污泥区3-3位于折流式曝气生化滤池的底部、下流区和上流区的下部,污泥区的底部设有污泥排放阀3-11。The middle and upper part of the baffle type aerated biochemical filter 3 is cylindrical, and the lower part is a conical structure, including a downstream area 3-1, an upstream area 3-2 and a sludge area 3-3; the downstream area 3- 1 Located in the middle of the cylindrical structure of the baffled aerated biochemical filter, it is a cylindrical structure, and the upper part of the downstream area is provided with the water inlet pipe 3-4 of the baffled aerated biochemical filter and the cloth of the baffled aerated biochemical filter The water pipe 3-5, the middle part of the downstream area is provided with the filling material 3-6 of the downstream area, the lower part of the downstream area is provided with the aeration pipe 3-7 of the downstream area, and the bottom of the downstream area is provided with a baffle plate 3-8. The vertical section of the flow plate 3-8 is trumpet-shaped; the upper flow area 3-2 is located on the periphery of the lower flow area 3-1 and the upper part of the baffle, the middle of the upper flow area is provided with an upper flow area filler 3-9, and the lower part is provided with an upper flow area. District aeration pipe, the outlet of the upper part of the upstream area is provided with a baffle type aerated biochemical filter overflow weir 3-10; the sludge area 3-3 is located at the bottom of the baffled type aerated biochemical filter, the downstream area and A sludge discharge valve 3-11 is provided at the bottom of the upstream zone and at the bottom of the sludge zone.
所述流砂滤池4包括流砂滤池进水管4-1和用于排出处理后水的流砂滤池出水管,所述的流砂滤池包括布水区、洗砂区和砂滤区;所述的布水区位于流砂滤池的下部,布水区设有流砂滤池布水管4-2,流砂滤池布水管4-2连接流砂滤池进水管4-1,为了废水处理的效果更好,所述的流砂滤池布水管4-2设置成同心圆形状,流砂滤池布水管上具有向下辐射出水口;所述的洗砂区位于流砂滤池的中心,为圆柱形筒状结构,圆柱形筒状结构下端开口位于流砂滤池的最底部,圆柱形筒状结构上端开口位于流砂滤池的上部,洗砂区的中部设有气提管4-3,气提管4-3连接流砂滤池外的流砂滤池鼓风机4-4,洗砂区的上部设有砂水沉淀分离区,砂水沉淀分离区的上部设有洗砂区溢水堰4-5,洗砂区溢水堰4-5连接洗砂水排放管和折流式曝气生化滤池进水管3-4,砂水沉淀分离区的下部设有回砂通道4-6;所述的砂滤区位于洗砂区的外围,砂滤区内充填有细砂,砂滤区上部设有砂滤区溢水堰4-7,砂滤区溢水堰4-7连接流砂滤池出水管,流砂滤池过滤处理后的水进入清水池回用。The quicksand filter 4 includes a quicksand filter inlet pipe 4-1 and a quicksand filter outlet pipe for discharging treated water, and the quicksand filter includes a water distribution area, a sand washing area and a sand filter area; The water distribution area is located in the lower part of the quicksand filter, and the water distribution area is provided with a quicksand filter water distribution pipe 4-2, and the quicksand filter water distribution pipe 4-2 is connected to the quicksand filter inlet pipe 4-1, so that the effect of wastewater treatment is better , the quicksand filter water distribution pipe 4-2 is arranged in the shape of concentric circles, and the quicksand filter water distribution pipe has a downward radiating water outlet; the described sand washing area is located in the center of the quicksand filter and is a cylindrical tubular structure , the lower opening of the cylindrical cylindrical structure is located at the bottom of the quicksand filter, the upper opening of the cylindrical cylindrical structure is located at the upper part of the quicksand filter, and the middle part of the sand washing area is provided with an air lift pipe 4-3, and an air lift pipe 4-3 Connect the quicksand filter blower 4-4 outside the quicksand filter. The upper part of the sand washing area is provided with a sand-water sedimentation separation area. The upper part of the sand-water sedimentation separation area is equipped with a sand washing area overflow weir 4-5. 4-5 Connect the sand washing water discharge pipe and the baffle type aerated biochemical filter inlet pipe 3-4, and the lower part of the sand-water sedimentation separation area is provided with a sand return channel 4-6; the sand filter area is located in the sand washing area The sand filter area is filled with fine sand, the upper part of the sand filter area is provided with a sand filter area overflow weir 4-7, and the sand filter area overflow weir 4-7 is connected to the outlet pipe of the quicksand filter, and the water after the quick sand filter is filtered Enter the clear water pool for reuse.
一种采用上述炼油废水深度处理装置进行废水处理的方法,具有如下步骤:A method for wastewater treatment using the above-mentioned refinery wastewater advanced treatment device has the following steps:
①废水通过废水调节池进水管进入废水调节池,调节水质和水量。①Wastewater enters the wastewater regulating tank through the inlet pipe of the wastewater regulating tank to adjust the water quality and quantity.
②然后废水通过高效气浮池进水管1-1进入高效气浮池的中下部;位于高效气浮池进水管下方的高效气浮池曝气盘1-6产生大量细小气泡,高效气浮池曝气盘1-6产生的细小气泡与浮油、浮渣粘附形成混合体在浮力作用下上升,在高效气浮池三相分离器1-8的作用下,混合体上升至集油集渣区1-5,在油渣刮板1-10的作用下,浮油和浮渣进入油渣槽1-11并被清理外运;分离处理后的水在高效气浮池三相分离区导流板作用下进入高效气浮池的集水区1-4,通过高效气浮池溢水堰1-9、高效气浮池出水管进入高级氧化池进水管2-5。② Then the waste water enters the middle and lower part of the high-efficiency air flotation tank through the inlet pipe 1-1 of the high-efficiency air flotation tank; the aeration disc 1-6 of the high-efficiency air flotation tank located below the water inlet pipe of the high-efficiency air flotation tank produces a large number of fine air bubbles, and the aeration disc 1-6 of the high-efficiency air flotation tank 6. The fine air bubbles produced adhere to the slick oil and scum to form a mixture that rises under the action of buoyancy. Under the action of the three-phase separator 1-8 in the high-efficiency air flotation tank, the mixture rises to the oil and slag collection area 1-5, Under the action of the oil residue scraper 1-10, the slick oil and scum enter the oil residue tank 1-11 and are cleaned and transported; the separated water enters the high-efficiency air flotation tank under the action of the deflector in the three-phase separation area of the high-efficiency air flotation tank. The water collection area 1-4 of the air flotation tank enters the water inlet pipe 2-5 of the advanced oxidation tank through the overflow weir 1-9 of the high-efficiency air flotation tank and the outlet pipe of the high-efficiency air flotation tank.
③废水通过高级氧化池进水管2-5以及高级氧化池布水支管2-4进入高级氧化池2的中下部;位于高级氧化池布水支管下方的臭氧曝气盘2-3产生大量细小气泡把废水中的大分子物质氧化成易于吸收和吸附的小分子物质,氧化分解后的废水进入沉淀区的废水流道,高级氧化池三相分离器2-9实现固液分离;沉淀物在在重力的作用下下沉到高级氧化池沉淀区2-2的下部,通过底部的沉淀物排放阀2-11排出;废水通过高级氧化池溢水堰2-10、高级氧化池出水管进入折流式曝气生化滤池进水管3-4。③Wastewater enters the middle and lower part of the advanced oxidation tank 2 through the water inlet pipe 2-5 of the advanced oxidation tank and the water distribution branch pipe 2-4 of the advanced oxidation tank; the ozone aeration plate 2-3 located below the water distribution branch pipe of the advanced oxidation tank produces a large number of fine air bubbles Oxidize the macromolecular substances in the wastewater into small molecular substances that are easy to absorb and absorb, and the oxidized and decomposed wastewater enters the wastewater flow channel in the sedimentation area, and the three-phase separator 2-9 in the advanced oxidation tank realizes solid-liquid separation; Under the action of gravity, it sinks to the lower part of the sedimentation zone 2-2 of the advanced oxidation tank, and is discharged through the sediment discharge valve 2-11 at the bottom; the waste water enters the baffle type through the overflow weir 2-10 of the advanced oxidation tank and the outlet pipe of the advanced oxidation tank. Aerated biochemical filter inlet pipe 3-4.
④废水通过折流式曝气生化滤池进水管3-4、折流式曝气生化滤池布水管3-5进入折流式曝气生化滤池的下流区3-1,下流区曝气管3-7产生的空气与废水在下流区填料3-6中交汇发生生化反应,同时下流区填料3-6对废水进行过滤,废水通过折流板3-8后进入上流区3-2,在上流区填料3-9中发生生化反应,同时上流区填料3-9对废水进行过滤,下流区和上流区产生的污泥下沉到污泥区3-3,通过污泥区底部的污泥排放阀3-11排放出去,折流式曝气生化滤池处理后的水通过折流式曝气生化滤池溢水堰3-10进入流砂滤池进水管。④Wastewater enters the downstream area 3-1 of the baffled aerated biochemical filter through the water inlet pipe 3-4 of the baffled aerated biochemical filter and the water distribution pipe 3-5 of the baffled aerated biochemical filter, and the downstream area is aerated The air generated by the pipe 3-7 and the waste water meet in the filler 3-6 in the downstream area to undergo a biochemical reaction. At the same time, the filler 3-6 in the downstream area filters the waste water, and the waste water enters the upstream area 3-2 after passing through the baffle plate 3-8. The biochemical reaction occurs in the packing 3-9 in the upstream area, and at the same time, the packing 3-9 in the upstream area filters the waste water, and the sludge produced in the downstream area and the upstream area sinks to the sludge area 3-3, and passes through the sludge at the bottom of the sludge area. The mud discharge valve 3-11 is discharged, and the water after the baffle type aerated biochemical filter is processed enters the quicksand filter water inlet pipe through the baffle type aerated biochemical filter overflow weir 3-10.
⑤废水通过流砂滤池进水管4-1、流砂滤池布水管4-2进入流砂滤池的下部,流砂滤池布水管4-2实现均匀布水,废水进入砂滤区,废水中的污染物被进一步过滤,然后废水穿过砂滤区,由砂滤区溢水堰4-7和流砂滤池出水管进入清水池回用;流砂滤池鼓风机4-4产生的气流带动洗砂区中的砂和水向上流动,同时对砂进行冲洗,然后砂和水进入砂水沉淀分离区,由于砂和水的比重不同,细砂沉淀下去并通过回砂通道4-6流入砂滤区,实现砂滤区中的细砂不断从上往下的移动,砂水沉淀分离区中的水通过洗砂区溢水堰4-5和洗砂水排放管进入折流式曝气生化滤池进行再处理。⑤ The waste water enters the lower part of the quicksand filter through the water inlet pipe 4-1 of the quicksand filter and the water distribution pipe 4-2 of the quicksand filter. The material is further filtered, and then the waste water passes through the sand filter area, and enters the clear water pool for reuse by the overflow weir 4-7 of the sand filter area and the outlet pipe of the quicksand filter; The sand and water flow upwards and wash the sand at the same time, and then the sand and water enter the sand-water sedimentation and separation area. Due to the different specific gravity of the sand and water, the fine sand settles down and flows into the sand filter area through the sand return channel 4-6 to realize sand filtration. The fine sand in the filter area moves continuously from top to bottom, and the water in the sand-water sedimentation separation area passes through the overflow weir 4-5 in the sand washing area and the sand washing water discharge pipe into the baffled aerated biochemical filter for further treatment.
⑥高级氧化池2产生的沉淀物和折流式曝气生化滤池3产生的污泥经浓缩、脱水后外运。⑥ The sediment produced in the advanced oxidation tank 2 and the sludge produced in the baffle type aerated biochemical filter 3 are concentrated and dehydrated before being transported outside.
以上述依据本发明的理想实施例为启示,通过上述的说明内容,相关工作人员完全可以在不偏离本项发明技术思想的范围内进行多样的变更以及修改。本项发明的技术性范围并不局限于说明书上的内容,必须要根据权利要求范围来确定其技术性范围。Inspired by the above-mentioned ideal embodiment according to the present invention, through the above-mentioned description content, relevant workers can make various changes and modifications within the scope of not departing from the technical idea of the present invention. The technical scope of the present invention is not limited to the content in the specification, but must be determined according to the scope of the claims.
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