CN105330099B - An integrated wastewater treatment device and petrochemical secondary effluent treatment method - Google Patents

An integrated wastewater treatment device and petrochemical secondary effluent treatment method Download PDF

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CN105330099B
CN105330099B CN201510708367.3A CN201510708367A CN105330099B CN 105330099 B CN105330099 B CN 105330099B CN 201510708367 A CN201510708367 A CN 201510708367A CN 105330099 B CN105330099 B CN 105330099B
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pipeline
ozone
reactor
denitrification zone
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CN105330099A (en
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周岳溪
吴昌永
丁岩
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Chinese Research Academy of Environmental Sciences
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F2003/001Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36Nature 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
    • C02F2103/365Nature 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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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/78Details relating to ozone treatment devices
    • C02F2201/782Ozone generators
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/10Solids, e.g. total solids [TS], total suspended solids [TSS] or volatile solids [VS]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/14NH3-N
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/16Total nitrogen (tkN-N)
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
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  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

The invention discloses Integral waste water processing means, including the reactor of upward flowing type, ozone generator (7), water tank (1), Venturi tube (8);Wherein, described reactor includes denitrification zone (3), catalytic ozonation district (4) and BAF district (5) from bottom to up successively, the bottom of described denitrification zone (3) is provided with water inlet (18), and reactor head is provided with delivery port (10);It is provided with the first refluxing opening (16) and the second refluxing opening (17) on the top of described reactor;Described water inlet (18) is connected with described water tank (1) by the first pipeline (13), is connected with described first refluxing opening (16) by the second pipeline (14).The invention also discloses the processing method using described Integral waste water processing means to carry out petrochemical wastewater.The present invention reaches preferable organic matter and the effect of total nitrogen removal when Advanced Treatment of Petrochemical Wastewater.

Description

一种一体式废水处理装置及石化二级出水处理方法An integrated wastewater treatment device and petrochemical secondary effluent treatment method

技术领域technical field

本发明涉及废水处理领域,特别是涉及一种一体式废水处理装置及采用该装置进行石化二级出水处理的方法。The invention relates to the field of wastewater treatment, in particular to an integrated wastewater treatment device and a method for using the device to treat secondary petrochemical effluent.

背景技术Background technique

石化化工行业是国家经济的重点行业,同时也是一个高消耗,高污染的行业。石化工业废水的排放水量随着石油炼制加工深度不同而各不相同,每吨原油的提炼产生的废水量约为2.86吨;加工每吨石油化工产品产生的废水量为117吨;加工每吨石油化纤产品产生的废水量为161.8吨;生产每吨化肥产品产生的废水量为4.25吨。2008年,我国石油和化工行业规模以上企业排放工业废水43.82亿吨,占全国工业规模以上企业废水排放量的20.2%,位居工业水排放首位。此外,石化废水具有废水水量大、污染成分复杂、水质水量波动大的特点,对环境污染严重。一般石化废水经污水厂进行生物处理,出水可以达到《污水综合排放标准》(GB 8978-1996)中的排放标准(COD≤100mg·L-1)。但2015年发布的《石油化学工业污染物排放标准》(GB 31571-2015),规定在国土开发密度已经较高、环境承载能力开始减弱,或水环境容量较小、生态环境脆弱,容易发生严重水环境污染问题而需要采取特别保护措施的地区,直接排至受纳水体的COD最高值为50mg·L-1、总氮的最高值为30mg·L-1。所以对石化废水的深度处理已经迫在眉睫。The petrochemical industry is a key industry in the national economy, and it is also a high-consumption and high-pollution industry. The amount of wastewater discharged from the petrochemical industry varies with the depth of petroleum refining and processing. The amount of wastewater generated per ton of crude oil refining is about 2.86 tons; the amount of wastewater generated per ton of petrochemical products is 117 tons; the amount of wastewater generated per ton of processing The amount of waste water generated by petroleum and chemical fiber products is 161.8 tons; the amount of waste water generated by each ton of chemical fertilizer products is 4.25 tons. In 2008, enterprises above designated size in my country's petroleum and chemical industries discharged 4.382 billion tons of industrial wastewater, accounting for 20.2% of the total amount of wastewater discharged by enterprises above designated size in the country, ranking first in industrial water discharge. In addition, petrochemical wastewater has the characteristics of large wastewater volume, complex pollution components, and large fluctuations in water quality and volume, which seriously pollutes the environment. General petrochemical wastewater is biologically treated by the sewage plant, and the effluent can meet the discharge standard (COD≤100mg·L -1 ) in the "Integrated Wastewater Discharge Standard" (GB 8978-1996). However, the "Petrochemical Industry Pollutant Discharge Standard" (GB 31571-2015) issued in 2015 stipulates that the development density of the land is already high, the environmental carrying capacity has begun to weaken, or the water environment capacity is small, the ecological environment is fragile, and serious pollution is prone to occur. In areas where special protection measures are required due to water pollution problems, the highest value of COD discharged directly to the receiving water body is 50mg·L -1 , and the highest value of total nitrogen is 30mg·L -1 . Therefore, the advanced treatment of petrochemical wastewater is imminent.

曝气生物滤池是一种常见的生物膜处理工艺,具有占地面积小、出水水质好、产泥量少、造价低,并且具有模块化结构、自动化程度高等特点。曝气生物滤池充分借鉴了污水处理接触氧化法和给水快滤池的设计思路,将生物降解与吸附过滤两种处理过程合并在同一单元反应器中。以滤池中填装的粒状填料(如陶粒、焦炭、石英砂、活性炭等)为载体,在滤池内部进行曝气,使滤料表面生长着大量生物膜,当污水流经时,利用滤料上所附生物膜中高浓度的活性微生物强氧化分解作用以及滤料粒径较小的特点,充分发挥微生物的生物代谢、生物絮凝、生物膜和填料的物理吸附和截留以及反应器内沿水流方向食物链的分级捕食作用,实现污染物的高效清除在一个单元反应器内同时完成了生物氧化和固液分离的功能,在污水深度处理领域得到了广泛应用。但传统BAF通常只能去除污水中易生物降解的有机物,拥有把污水中氨氮氧化成硝氮的作用,单独用该工艺对水中难生物降解的有机物以及总氮的去除效果不佳。而臭氧具有强氧化性,可以把石化废水中难降解的有机物氧化成易被生物降解的有机物,采用臭氧与BAF结合,并在反应柱设计反硝化区的方法则有效的弥补了BAF的缺点。Biological aerated filter is a common biofilm treatment process, which has the characteristics of small footprint, good effluent quality, low sludge production, low cost, modular structure, and high degree of automation. The biological aerated filter fully draws on the design ideas of the contact oxidation method of sewage treatment and the fast water filter, and combines the two treatment processes of biodegradation and adsorption filtration in the same unit reactor. With the granular filler filled in the filter (such as ceramsite, coke, quartz sand, activated carbon, etc.) The high concentration of active microorganisms in the biofilm attached to the filter material has strong oxidative decomposition and the characteristics of the small particle size of the filter material, giving full play to the biological metabolism of microorganisms, bioflocculation, physical adsorption and retention of biofilm and fillers, and the along the edge of the reactor. The graded predation effect of the food chain in the direction of water flow realizes the efficient removal of pollutants. The functions of biological oxidation and solid-liquid separation are simultaneously completed in one unit reactor, and it has been widely used in the field of advanced sewage treatment. However, traditional BAF can only remove easily biodegradable organic matter in sewage, and has the function of oxidizing ammonia nitrogen in sewage to nitrate nitrogen. The removal effect of this process alone on difficult biodegradable organic matter and total nitrogen in water is not good. Ozone has strong oxidizing properties and can oxidize refractory organic matter in petrochemical wastewater into easily biodegradable organic matter. The combination of ozone and BAF and the design of the denitrification zone in the reaction column can effectively make up for the shortcomings of BAF.

发明内容Contents of the invention

本发明要解决的技术问题是提供一种一体式废水处理装置及采用该装置进行石化二级出水处理的方法。解决用单独的BAF工艺深度处理工业废水时,难降解有机物和总氮的去除效率不高的问题。从强化难降解有机物的去除效果,提高反应运行的脱氮效果两方面,研究、发明本方法,可使BAF工艺在深度处理石化二级出水时达到较好的有机物和总氮去除的效果。The technical problem to be solved by the present invention is to provide an integrated wastewater treatment device and a method for using the device to treat secondary effluent of petrochemical industry. It solves the problem that the removal efficiency of refractory organic matter and total nitrogen is not high when using a single BAF process for advanced treatment of industrial wastewater. From the two aspects of strengthening the removal effect of refractory organic matter and improving the denitrification effect of reaction operation, the research and invention of this method can make the BAF process achieve better organic matter and total nitrogen removal effect in the advanced treatment of petrochemical secondary effluent.

一种一体式废水处理装置,包括反应器、臭氧发生器、水箱、文丘里管;其中,为改善曝气生物滤池工艺去除石化二级出水中难降解有机物及脱氮效果,将传统BAF设计三个区域,所述反应器从下至上依次包括反硝化区、臭氧催化氧化区和曝气生物滤池区,在所述反硝化区的底部设置有入水口,顶部设置有出水口;在所述反应器的上部设置有第一回流口和第二回流口;所述入水口通过第一管路与所述水箱相连,通过第二管路与所述第一回流口相连;An integrated wastewater treatment device, including a reactor, an ozone generator, a water tank, and a venturi tube; among them, in order to improve the biological aerated filter process to remove refractory organic matter and denitrification in petrochemical secondary effluent, the traditional BAF design Three areas, the reactor includes a denitrification area, an ozone catalytic oxidation area and a biological aerated filter area from bottom to top, a water inlet is provided at the bottom of the denitrification area, and a water outlet is provided at the top; The upper part of the reactor is provided with a first return port and a second return port; the water inlet is connected to the water tank through a first pipeline, and connected to the first return port through a second pipeline;

本发明所述的一体式废水处理装置,其中,在所述第一管路上设置有进水泵和第一阀门,在所述第二管路上设置有第一回流泵和第二阀门,在所述第三管路上设置有第二回流泵和第三阀门。In the integrated wastewater treatment device of the present invention, an inlet pump and a first valve are arranged on the first pipeline, a first return pump and a second valve are arranged on the second pipeline, and A second return pump and a third valve are arranged on the third pipeline.

本发明所述的一体式废水处理装置,其中,在所述反硝化区、所述臭氧催化氧化区和所述曝气生物滤池区的下部均设置有滤料承托层和取料口,方便反应器内滤料的更换,在所述反应器的下部设置有放空口;方便反应器内废水的排空。所述反硝化区、所述臭氧催化氧化区和所述曝气生物滤池区的体积比为1:1:4。In the integrated wastewater treatment device of the present invention, a filter material support layer and a material intake are all provided at the lower part of the denitrification zone, the ozone catalytic oxidation zone and the biological aerated filter zone, It is convenient to replace the filter material in the reactor, and a vent port is arranged at the lower part of the reactor; it is convenient to empty the waste water in the reactor. The volume ratio of the denitrification zone, the ozone catalytic oxidation zone and the biological aerated filter zone is 1:1:4.

本发明所述的一体式废水处理装置,其中,所述反硝化区和所述曝气生物滤池区的填料为火山岩,粒径2-5mm;所述臭氧催化氧化区的填料为负载过渡金属氧化物,粒径2-5mm;所述反硝化区和所述臭氧催化氧化区的填料填充率为85%,所述曝气生物滤池区的填料填充率为80%。The integrated wastewater treatment device of the present invention, wherein, the fillers in the denitrification zone and the biological aerated filter zone are volcanic rocks with a particle size of 2-5 mm; the fillers in the ozone catalytic oxidation zone are loaded transition metals The oxides have a particle size of 2-5mm; the filling rate of the denitrification zone and the ozone catalytic oxidation zone is 85%, and the filling rate of the biological aerated filter zone is 80%.

本发明所述的一体式废水处理装置,其中,所述负载过渡金属氧化物为Al2O3或CuO的固体催化填料。In the integrated wastewater treatment device of the present invention, the transition metal oxide supported is a solid catalytic filler of Al 2 O 3 or CuO.

由于火山岩价格低廉,并且具有发达的孔隙结构,孔大小不均,质轻,由于孔间大大小小表面粗糙,比表面积大,具有惰性、抗腐蚀在参与生物膜在环境中发生物化学反应相对稳定,其表面亲水强,粗糙多孔,附着的生物膜速度快量多,带有正电荷,有利于生物膜生长,是生物膜很好的载体,对所固定的微生物元素,无抑制性作用,不影响微生物的活性,可为微生物的着床提供良好的条件;臭氧催化氧化区内的催化氧化填料可使臭氧与石化二级出水充分混合接触,增强臭氧的氧化效果,提高臭氧的利用率。Due to the low price of volcanic rocks and the developed pore structure, the pores are uneven in size and light in weight. Due to the large and small pores, the surface is rough and the specific surface area is large. It is inert and corrosion-resistant. Stable, its surface is highly hydrophilic, rough and porous, and the attached biofilm is fast and large, with positive charges, which is conducive to the growth of biofilm. It is a good carrier for biofilm and has no inhibitory effect on the fixed microbial elements. , does not affect the activity of microorganisms, and can provide good conditions for the implantation of microorganisms; the catalytic oxidation filler in the ozone catalytic oxidation zone can fully mix and contact ozone with petrochemical secondary effluent, enhance the oxidation effect of ozone, and improve the utilization rate of ozone .

采用本发明所述的一体式废水处理装置进行石化二级出水处理的方法,其包括如下步骤:The method for carrying out petrochemical secondary effluent treatment using the integrated wastewater treatment device of the present invention comprises the following steps:

水箱中的废水通过进水泵进入到反应器中,依次通过反硝化区、臭氧催化氧化区和曝气生物滤池区,从出水口流出,同时,存在两条回流线路,一条通过第一回流口、第一回流泵和第二管路实现回流,第二条通过第二回流口、第二回流泵和第三管路到达文丘里管,回流废水在所述文丘里管中与臭氧发生器产生的臭氧混合后进入所述臭氧催化氧化区的下部,实现回流。The wastewater in the water tank enters the reactor through the water inlet pump, passes through the denitrification zone, the ozone catalytic oxidation zone and the biological aerated filter zone in turn, and flows out from the water outlet. At the same time, there are two return lines, one through the first return flow port , the first reflux pump and the second pipeline realize reflux, and the second one reaches the Venturi tube through the second reflux port, the second reflux pump and the third pipeline, and the reflux waste water is generated with the ozone generator in the Venturi tube The mixed ozone enters the lower part of the ozone catalytic oxidation zone to realize backflow.

本发明所述的废水处理方法,其中,在所处理石化二级出水COD低于100mg/L,TN低于30mg/L时,所述臭氧催化氧化区的回流量为100%-200%,所述反硝化区的回流量为100%,所述反应器的停留时间为3h,臭氧的投量在10mg/L。The wastewater treatment method of the present invention, wherein, when the treated petrochemical secondary effluent COD is lower than 100mg/L and TN is lower than 30mg/L, the reflux rate of the ozone catalytic oxidation zone is 100%-200%, so The reflux rate of the denitrification zone is 100%, the residence time of the reactor is 3h, and the dosage of ozone is 10mg/L.

本发明一体式废水处理装置与现有技术不同之处在于:本发明一体式废水处理装置及采用该装置进行石化二级出水处理的方法具有如下优点:The difference between the integrated waste water treatment device of the present invention and the prior art is that the integrated waste water treatment device of the present invention and the method of using the device for petrochemical secondary effluent treatment have the following advantages:

1)在反应器设置反硝化区和臭氧催化氧化区,提高了反应器处理石化二级出水中难降解有机物和总氮的效果,使得出水更有保障。1) The denitrification zone and ozone catalytic oxidation zone are set in the reactor, which improves the effect of the reactor on treating refractory organic matter and total nitrogen in the petrochemical secondary effluent, making the effluent more secure.

2)在反应器内设有回流装置,提高了预氧化时,臭氧与石化二级出水的接触时间,提高了臭氧的利用率。2) There is a reflux device in the reactor, which increases the contact time between ozone and petrochemical secondary effluent during pre-oxidation, and improves the utilization rate of ozone.

3)臭氧在与废水的反应过程中,生成氧气,为后续的BAF单元提供了曝气,消除了传统BAF工艺运行过程中曝气的装置,节省了运行成本。3) Ozone generates oxygen during the reaction process with wastewater, which provides aeration for the subsequent BAF unit, eliminates the aeration device during the operation of the traditional BAF process, and saves operating costs.

4)本发明把传统的反硝化装置、臭氧混合装置和BAF装置组合在一个反应器里,减小了反应器的占地面积,降低了投资成本。4) The present invention combines the traditional denitrification device, ozone mixing device and BAF device in one reactor, which reduces the floor area of the reactor and reduces the investment cost.

5)臭氧投量小,节省能耗,且经过臭氧催化氧化区和曝气生物滤池区后出气中臭氧含量低,无需安装臭氧破坏装置。5) The dosage of ozone is small, which saves energy consumption, and the ozone content in the exhaust gas after passing through the ozone catalytic oxidation zone and the biological aerated filter zone is low, so there is no need to install an ozone destruction device.

本发明的技术原理如下:Technical principle of the present invention is as follows:

一体式废水处理装置及石化废水处理二级出水处理方法,是将臭氧的化学氧化、生物降解、好氧硝化和厌氧反硝化四种技术结合在一起的一体式组合工艺。石化二级出水先经过反硝化区、臭氧催化氧化区和BAF区,一条支流再由回流泵经由文丘里管与臭氧混合后流入臭氧催化氧化区,这一条支流利用了臭氧的氧化作用,把石化二级出水中难降解的有机物氧化成易被生物降解的有机物,提高了后续BAF单元生物降解难降解有机物的效果,并且臭氧在与废水的反应过程中生成了氧气,为后续的BAF单元提供了供微生物硝化作用所用的氧气,从而代替了传统了曝气设备,节省了运行成本;另一路支流经由回流泵把BAF单元的废水回流至反硝化区,使得废水中的硝酸根离子和亚硝酸根离子经由附着在火山岩上面的反硝化菌的作用,产生氮气,从而达到进一步去除总氮的效果。The integrated wastewater treatment device and the secondary effluent treatment method of petrochemical wastewater treatment are an integrated combination process that combines four technologies of ozone chemical oxidation, biodegradation, aerobic nitrification and anaerobic denitrification. The petrochemical secondary effluent first passes through the denitrification zone, ozone catalytic oxidation zone and BAF zone, and then a branch stream flows into the ozone catalytic oxidation zone through the return pump through the Venturi tube, and then flows into the ozone catalytic oxidation zone. The refractory organic matter in the secondary effluent is oxidized into easily biodegradable organic matter, which improves the effect of subsequent BAF unit biodegradation of refractory organic matter, and ozone generates oxygen during the reaction process with wastewater, which provides the follow-up BAF unit The oxygen used for microbial nitrification replaces the traditional aeration equipment and saves operating costs; another branch stream returns the wastewater from the BAF unit to the denitrification area through the return pump, so that the nitrate ions and nitrite in the wastewater Ions generate nitrogen through the action of denitrifying bacteria attached to the volcanic rock, so as to achieve the effect of further removing total nitrogen.

下面结合附图对本发明的一体式废水处理装置及采用该装置进行石化二级出水处理的方法作进一步说明。The integrated wastewater treatment device of the present invention and the method of using the device for petrochemical secondary effluent treatment will be further described below in conjunction with the accompanying drawings.

附图说明Description of drawings

图1为本发明一体式废水处理装置的结构示意图。Fig. 1 is a schematic structural view of the integrated wastewater treatment device of the present invention.

其中,1—水箱,2—进水泵,3—反硝化区,4—臭氧催化氧化区,5—曝气生物滤池区,6—第二回流泵,7—臭氧发生器,8—文丘里管,9—第一回流泵,10—出水口,11—放空口,12—取料口,13—第一管路,14—第二管路,15—第三管路,16—第一回流口,17—第二回流口,18—入水口。Among them, 1—water tank, 2—inlet pump, 3—denitrification zone, 4—ozone catalytic oxidation zone, 5—biological aerated filter zone, 6—second return pump, 7—ozone generator, 8—venturi Pipe, 9—first return pump, 10—water outlet, 11—venting port, 12—feeding port, 13—first pipeline, 14—second pipeline, 15—third pipeline, 16—first Return port, 17—second return port, 18—water inlet.

具体实施方式detailed description

实施例1Example 1

如图1所示,本发明一体式废水处理装置包括反应器、臭氧发生器7、水箱1、文丘里管8;其中,所述反应器从下至上依次包括反硝化区3、臭氧催化氧化区4和曝气生物滤池区5,在所述反硝化区3的底部设置有入水口18,顶部设置有出水口10;在所述反应器的上部设置有第一回流口16和第二回流口17;所述入水口18通过第一管路13与所述水箱1相连,通过第二管路14与所述第一回流口16相连;As shown in Figure 1, the integrated wastewater treatment device of the present invention includes a reactor, an ozone generator 7, a water tank 1, and a Venturi tube 8; wherein, the reactor includes a denitrification zone 3 and an ozone catalytic oxidation zone from bottom to top. 4 and biological aerated filter zone 5, a water inlet 18 is provided at the bottom of the denitrification zone 3, and a water outlet 10 is provided at the top; a first return port 16 and a second return port are provided at the top of the reactor Port 17; the water inlet 18 is connected to the water tank 1 through the first pipeline 13, and connected to the first return port 16 through the second pipeline 14;

所述臭氧发生器7与所述文丘里管8相连,所述文丘里管8的入水口与所述第二回流口17通过第三管路15相连,所述文丘里管8的出水口与所述臭氧催化氧化区4的下部相连。Described ozone generator 7 is connected with described Venturi tube 8, and the water inlet of described Venturi tube 8 is connected with described second return port 17 by the 3rd pipeline 15, and the water outlet of described Venturi tube 8 is connected with The lower part of the ozone catalytic oxidation zone 4 is connected.

在所述第一管路13上设置有进水泵2和第一阀门,在所述第二管路14上设置有第一回流泵9和第二阀门,在所述第三管路15上设置有第二回流泵6和第三阀门。The first pipeline 13 is provided with an inlet pump 2 and a first valve, the second pipeline 14 is provided with a first return pump 9 and a second valve, and the third pipeline 15 is provided with There is a second return pump 6 and a third valve.

在所述反硝化区3、所述臭氧催化氧化区4和所述曝气生物滤池区5的下部均设置有滤料承托层和取料口12,在所述反应器的下部设置有放空口11;所述反硝化区3、所述臭氧催化氧化区4和所述曝气生物滤池区5的体积比为1:1:4。In the lower part of the denitrification zone 3, the ozone catalytic oxidation zone 4 and the biological aerated filter zone 5, a filter support layer and a material intake 12 are arranged, and in the lower part of the reactor, a The volume ratio of the vent 11 ; the denitrification zone 3 , the ozone catalytic oxidation zone 4 and the biological aerated filter zone 5 is 1:1:4.

所述反硝化区3和所述曝气生物滤池区5的填料为火山岩,粒径2-5mm;所述臭氧催化氧化区4的填料为负载过渡金属氧化物,如Al2O3或CuO的固体催化填料,粒径2-5mm;所述反硝化区3和所述臭氧催化氧化区4的填料填充率为85%,所述曝气生物滤池区5的填料填充率为80%。The fillers in the denitrification zone 3 and the biological aerated filter zone 5 are volcanic rocks with a particle size of 2-5 mm; the fillers in the ozone catalytic oxidation zone 4 are loaded transition metal oxides, such as Al 2 O 3 or CuO The solid catalytic packing with a particle size of 2-5 mm; the packing rate of the denitrification zone 3 and the ozone catalytic oxidation zone 4 is 85%, and the packing rate of the biological aerated filter zone 5 is 80%.

实施例2Example 2

采用本发明所述的一体式废水处理装置进行石化二级出水处理的方法,包括如下步骤:The method for carrying out petrochemical secondary effluent treatment using the integrated wastewater treatment device of the present invention comprises the following steps:

水箱1中的废水通过进水泵2进入到反应器中,依次通过反硝化区3、臭氧催化氧化区4和曝气生物滤池区5,从出水口10流出,同时,存在两条回流线路,一条通过第一回流口16、第一回流泵9和第二管路14实现回流,第二条通过第二回流口17、第二回流泵6和第三管路15到达文丘里管8,回流废水在所述文丘里管8中与臭氧发生器7产生的臭氧混合后进入所述臭氧催化氧化区4的下部,实现回流。The wastewater in the water tank 1 enters the reactor through the water inlet pump 2, passes through the denitrification zone 3, the ozone catalytic oxidation zone 4 and the biological aerated filter zone 5 in turn, and flows out from the water outlet 10. At the same time, there are two return lines, One realizes reflux through the first reflux port 16, the first reflux pump 9 and the second pipeline 14, and the second one reaches the Venturi tube 8 through the second reflux port 17, the second reflux pump 6 and the third pipeline 15, and the reflux The waste water enters the lower part of the ozone catalytic oxidation zone 4 after being mixed with the ozone generated by the ozone generator 7 in the venturi tube 8 to realize reflux.

优选的是,所述臭氧催化氧化区4的回流量为100%-200%,所述反硝化区3的回流量为100%,所述反应器的停留时间为3h,臭氧的投量在10mg/L。Preferably, the reflux of the ozone catalytic oxidation zone 4 is 100%-200%, the reflux of the denitrification zone 3 is 100%, the residence time of the reactor is 3h, and the dosage of ozone is 10mg /L.

实施例3Example 3

本实施例以某典型石化废水二级出水为处理对象,废水水质指标如下:COD在60~120mg/L之间,BOD5在0.95~4mg/L之间,UV254在0.6~0.81/cm之间,NH4 +-N浓度在2mg/L以下,TN的含量为20mg/L左右,pH介于7~8之间,SS在20~27mg/L之间,TP在1.0-1.5mg/L之间。采用臭氧投量为10mg/L,臭氧催化氧化单元回流比为200%,反硝化单元回流比为100%,上述石化废水经本工艺处理后,出水指标COD为50mg/L左右,NH4 +-N浓度在0.5mg/L以下,TN的含量为15mg/L左右。In this example, the secondary effluent of a typical petrochemical wastewater is treated as the treatment object. The wastewater quality indicators are as follows: COD is between 60-120mg /L, BOD5 is between 0.95-4mg/L, and UV 254 is between 0.6-0.81/cm The concentration of NH 4 + -N is below 2 mg/L, the content of TN is about 20 mg/L, the pH is between 7 and 8, the SS is between 20 and 27 mg/L, and the TP is between 1.0 and 1.5 mg/L between. The dosage of ozone is 10mg/L, the reflux ratio of ozone catalytic oxidation unit is 200%, and the reflux ratio of denitrification unit is 100%. The N concentration is below 0.5mg/L, and the TN content is about 15mg/L.

所述反硝化区和BAF区所用填料均为火山岩,臭氧催化氧化单元所用催化氧化填料为负载Al2O3的催化剂填料,废水在整个工艺的停留时间HRT为3h。The fillers used in the denitrification zone and the BAF zone are all volcanic rocks, the catalytic oxidation fillers used in the ozone catalytic oxidation unit are catalyst fillers loaded with Al 2 O 3 , and the residence time HRT of wastewater in the whole process is 3h.

以上所述的实施例仅仅是对本发明的优选实施方式进行描述,并非对本发明的范围进行限定,在不脱离本发明设计精神的前提下,本领域普通技术人员对本发明的技术方案作出的各种变形和改进,均应落入本发明权利要求书确定的保护范围内。The above-mentioned embodiments are only descriptions of preferred implementations of the present invention, and are not intended to limit the scope of the present invention. Variations and improvements should fall within the scope of protection defined by the claims of the present invention.

Claims (4)

1. an Integral waste water processing means, it is characterised in that: include reactor, ozone generator (7), water tank (1), literary composition mound In pipe (8);Wherein, described reactor includes that denitrification zone (3), catalytic ozonation district (4) and aeration are raw from bottom to up successively Thing filter tank district (5), is provided with water inlet (18) in the bottom of described denitrification zone (3), and top is provided with delivery port (10);Institute The top stating reactor is provided with the first refluxing opening (16) and the second refluxing opening (17);Described water inlet (18) passes through the first pipeline (13) it is connected with described water tank (1), be connected with described first refluxing opening (16) by the second pipeline (14);
Described ozone generator (7) is connected with described Venturi tube (8), the water inlet of described Venturi tube (8) and described second Refluxing opening (17) is connected by the 3rd pipeline (15), the delivery port of described Venturi tube (8) and described catalytic ozonation district (4) Bottom be connected;
It is all provided with in the bottom in described denitrification zone (3), described catalytic ozonation district (4) and described BAF district (5) It is equipped with filtrate supporting layer and material taking mouth (12), be provided with drain (11) in the bottom of described reactor;Described denitrification zone (3), the volume ratio in described catalytic ozonation district (4) and described BAF district (5) is 1:1:4;
The filler in described denitrification zone (3) and described BAF district (5) is volcanic rock, particle diameter 2-5mm;Described ozone is urged The filler changing zoneofoxidation (4) is carrying transition metal oxide, particle diameter 2-5mm;Described denitrification zone (3) and described ozone catalytic The media-filling rate of zoneofoxidation (4) is 85%, and the media-filling rate of described BAF district (5) is 80%;
Described Integral waste water processing means is for the process of petrochemical industry secondary effluent.
2. Integral waste water processing means according to claim 1, it is characterised in that: set on described first pipeline (13) It is equipped with intake pump (2) and the first valve, described second pipeline (14) is provided with the first reflux pump (9) and the second valve, It is provided with the second reflux pump (6) and the 3rd valve on described 3rd pipeline (15).
3. Integral waste water processing means according to claim 2, it is characterised in that: described carrying transition metal oxide For Al2O3Or the solid catalysis filler of CuO.
4. use the Integral waste water processing means described in any one in claims 1 to 3 to carry out petrochemical industry secondary effluent process Method, it is characterised in that: comprise the steps:
Waste water in water tank (1) enters in reactor by intake pump (2), passes sequentially through denitrification zone (3), ozone catalytic oxygen Changing district (4) and BAF district (5), flowing out from delivery port (10), concurrently there are two reflux lines, one article is passed through the One refluxing opening (16), the first reflux pump (9) and the second pipeline (14) realize backflow, Article 2 by the second refluxing opening (17), the Two reflux pumps (6) and the 3rd pipeline (15) reach Venturi tube (8), and backflow waste water is sent out with ozone in described Venturi tube (8) The bottom of described catalytic ozonation district (4) is entered, it is achieved backflow after the ozone mixing that raw device (7) produces;Described in processing Petrochemical industry secondary effluent COD is less than 100mg/L, and when TN is less than 30mg/L, the capacity of returns of described catalytic ozonation district (4) is 100%-200%, the capacity of returns of described denitrification zone (3) is 100%, and the time of staying of described reactor is 3h, the throwing of ozone Amount is at 10mg/L.
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