CN108083579A - Handle the modularization integrated system and technique of non-fermented class bean product production waste water - Google Patents
Handle the modularization integrated system and technique of non-fermented class bean product production waste water Download PDFInfo
- Publication number
- CN108083579A CN108083579A CN201711444827.1A CN201711444827A CN108083579A CN 108083579 A CN108083579 A CN 108083579A CN 201711444827 A CN201711444827 A CN 201711444827A CN 108083579 A CN108083579 A CN 108083579A
- Authority
- CN
- China
- Prior art keywords
- anaerobic
- reactor
- outlet
- inlet
- design
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- 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
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F1/40—Devices for separating or removing fatty or oily substances or similar floating material
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- 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
- C02F2103/32—Nature of the water, waste water, sewage or sludge to be treated from the food or foodstuff industry, e.g. brewery waste waters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/04—Disinfection
-
- 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
-
- 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
- C02F3/28—Anaerobic digestion processes
-
- 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
- C02F3/28—Anaerobic digestion processes
- C02F3/2833—Anaerobic digestion processes using fluidized bed reactors
Landscapes
- 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)
- Separation Using Semi-Permeable Membranes (AREA)
- Physical Water Treatments (AREA)
Abstract
本发明涉及一种处理非发酵类豆制品生产废水的模块化集成系统及工艺,包括一级预处理模块、二级生化模块和三级深度处理模块,一级预处理模块设置细网格筛和气浮隔油沉淀调节水池,去除悬浮物、浮油和调节水量水质;二级生化模块设置厌氧单元和好氧单元,去除废水中主要污染物;三级深度处理模块设置微砂沉淀池、活性砂滤池、动态膜过滤系统和紫外线消毒反应器,去除SS和消毒。针对高浓度非发酵类豆制品生产废水,进行工艺集成与参数化设计,根据进水水质条件,选择运行不同单元。本发明工艺具有灵活、高效、便捷、智能等特点,能够保证废水处理设施经济、有效、稳定的运行。
The invention relates to a modular integrated system and process for treating wastewater produced by non-fermented soybean products, including a first-level pretreatment module, a second-level biochemical module and a third-level advanced treatment module. The floating oil separation and sedimentation adjustment pool removes suspended solids and oil slicks and adjusts water quality and water quality; the secondary biochemical module is equipped with anaerobic units and aerobic units to remove main pollutants in wastewater; the tertiary advanced treatment module is equipped with micro sand sedimentation tanks, active Sand filter, dynamic membrane filtration system and ultraviolet disinfection reactor, SS removal and disinfection. For high-concentration non-fermented soybean product production wastewater, process integration and parameterization design are carried out, and different units are selected to operate according to the water quality conditions of the influent. The process of the invention has the characteristics of flexibility, high efficiency, convenience, intelligence and the like, and can ensure the economical, effective and stable operation of waste water treatment facilities.
Description
技术领域technical field
本发明涉及高浓度有机废水集成化处理技术领域,特别涉及处理非发酵类豆制品生产废水的模块化集成系统及工艺。The invention relates to the technical field of integrated treatment of high-concentration organic wastewater, in particular to a modular integrated system and process for treating wastewater produced by non-fermented soybean products.
背景技术Background technique
近几年,我国豆制品行业发展迅猛,发展起来了一批豆制品生产加工的大企业,改变了一直以来的作坊式的生产方式。截至2010年,全国豆制品加工企业2000余家,日加工能力500t/d的企业117家,世界范围内年加工能力达180万吨的12家企业中,我国就占了6家。In recent years, my country's bean product industry has developed rapidly, and a number of large enterprises in the production and processing of bean products have developed, which has changed the traditional workshop-style production mode. As of 2010, there were more than 2,000 soybean product processing enterprises nationwide, and 117 enterprises with a daily processing capacity of 500 t/d. Among the 12 enterprises with an annual processing capacity of 1.8 million tons worldwide, my country accounted for 6 of them.
豆制品主要分为两大类,一类是发酵性豆制品,另一类是非发酵性豆制品。发酵性豆制品指以大豆为原料,经微生物发酵而制成的豆制品,如酱油、豆腐乳、豆豉、豆瓣等。而非发酵性豆制品则指利用大豆和其它杂豆为原料,经一定的工艺方法制成的豆制品,例如豆腐、豆浆、豆奶等。Soy products are mainly divided into two categories, one is fermented soy products and the other is non-fermented soy products. Fermented soy products refer to soy products made from soybeans through microbial fermentation, such as soy sauce, fermented bean curd, tempeh, and watercress. Non-fermented soy products refer to soy products made from soybeans and other miscellaneous beans through certain processes, such as tofu, soy milk, and soy milk.
非发酵类豆制品生产工艺,以豆腐为例,流程为:初选—水洗—浸泡—磨浆—煮浆—点卤—压滤—成品。其中水洗到压滤均产生废水。非发酵类豆制品废水是一种高浓度的有机废水,其中含有大量的蛋白质、脂肪、淀粉等有机物,COD值和BOD值较高,总氮和氨氮也较高。在加工过程中排出的黄浆水中,固体含量在1%以上,其中蛋白质含量约占0.3%,脂肪含量约占0.08%,还原糖含量约占0.15%。除此之外,废水中还含有大豆异黄酮、大豆皂苷等多种功能性成分,目前我国大多数企业将黄浆水直接排放,这样既浪费资源又污染环境,不利于清洁生产和增加大豆加工附加值。The production process of non-fermented soy products, taking tofu as an example, the process is: primary selection—washing—soaking—refining—boiling—simmering—press filtration—finished product. Wherein water washing to pressure filtration all produce waste water. Non-fermented soybean product wastewater is a kind of high-concentration organic wastewater, which contains a large amount of organic matter such as protein, fat, starch, etc., with high COD and BOD values, and high total nitrogen and ammonia nitrogen. In the yellow pulp water discharged during processing, the solid content is more than 1%, wherein the protein content accounts for about 0.3%, the fat content accounts for about 0.08%, and the reducing sugar content accounts for about 0.15%. In addition, wastewater also contains soybean isoflavones, soybean saponins and other functional components. At present, most enterprises in my country directly discharge yellow pulp water, which wastes resources and pollutes the environment, which is not conducive to clean production and increased soybean processing. added value.
国外从20世纪60年代开始研究豆制品废水的处理,并且应用于工程实践中,我国也于70年代开始大量研究并应用于实践。豆制品废水的处理可以分为厌氧生物处理法、好氧生物处理法、厌氧—好氧相结合的处理工艺三种方法。其中厌氧生物工艺的研究与应用最多。主要采用的厌氧处理工艺包括:AB(厌氧滤床)工艺、UASB(上流式厌氧污泥床)工艺、AFB(厌氧流化床)给你工艺、ABR(厌氧折流板反应器)工艺、两相厌氧处理工艺等。但是经厌氧处理后的出水需要辅以好氧处理,才能满足排放标准。主要采用的好氧处理工艺包括AB法、传统活性污泥法、SBR(序批式活性污泥法)、MBR(膜生物反应器)法。目前,应用于非发酵性豆制品废水的处理工艺种类十分繁多,也取得了一定成效,但是还存在以下几个问题:Foreign countries began to study the treatment of soybean product wastewater in the 1960s and applied it to engineering practice. my country also began a large number of researches and applied it to practice in the 1970s. The treatment of soybean product wastewater can be divided into three methods: anaerobic biological treatment, aerobic biological treatment, and anaerobic-aerobic combined treatment process. Among them, the research and application of anaerobic biological process are the most. The main anaerobic treatment processes include: AB (anaerobic filter bed) process, UASB (upflow anaerobic sludge bed) process, AFB (anaerobic fluidized bed) for you process, ABR (anaerobic baffle reaction device) process, two-phase anaerobic treatment process, etc. However, the effluent after anaerobic treatment needs to be supplemented with aerobic treatment in order to meet the discharge standards. The main aerobic treatment processes include AB method, traditional activated sludge method, SBR (sequenced batch activated sludge method), MBR (membrane bioreactor) method. At present, there are many kinds of treatment processes applied to non-fermented soybean product wastewater, and some achievements have been made, but there are still the following problems:
(1)目前的水处理系统难以适应水量变化特别大的情况。非发酵类豆制品生产废水具有明显的季节性特点,即有所谓淡、旺季,有些厂在淡季时甚至停产,所以非发酵类豆制品生产废水的排放量在一年之中变化是很大的;目前采用的处理系统基本上按照平均水量或最大水量进行设计,这样设计的后果是,水量低时,系统负荷不足,导致微生物大量死亡;水量高时,系统负荷过高,出水水质不达标。(1) The current water treatment system is difficult to adapt to the situation where the water volume changes greatly. Wastewater from the production of non-fermented soy products has obvious seasonal characteristics, that is, there are so-called low and peak seasons, and some factories even stop production during the off-season, so the discharge of non-fermented soy product production wastewater varies greatly in a year The treatment system currently used is basically designed according to the average water volume or the maximum water volume. The consequence of this design is that when the water volume is low, the system load is insufficient, resulting in a large number of microbial deaths; when the water volume is high, the system load is too high, and the effluent water quality is not up to standard.
(2)目前的水处理系统难以适应水质变化大的情况。非发酵类豆制品生产废水由于生产和加工工艺的不同,废水水质不尽相同,即使时同一企业,不同加工阶段的废水水质也有很大差异。有时候废水的COD范围在1500—3000范围内,有时候又高达8000—20000。因此,在设计时,一般采用同一套系统处理水质变化极大的废水,水质的明显变化会对污水处理系统产生冲击负荷,导致系统变得不稳定,出水指标也会变差。(2) The current water treatment system is difficult to adapt to the situation of large changes in water quality. Due to the different production and processing techniques, the wastewater quality of non-fermented soy products is not the same. Even if it is the same enterprise, the wastewater quality of different processing stages is also very different. Sometimes the COD range of wastewater is in the range of 1500-3000, and sometimes it is as high as 8000-20000. Therefore, at the time of design, the same system is generally used to treat wastewater with great changes in water quality. Significant changes in water quality will cause impact loads on the sewage treatment system, causing the system to become unstable and the effluent indicators to deteriorate.
(3)季节性废水对厌氧系统有冲击,加重企业负担。非发酵类豆制品生产废水是典型的有机废水,一般生化阶段采用厌氧和好氧联合处理系统,但非发酵类豆制品生产废水具有季节性特点,冬季无水的情况下,厌氧系统会受到极大影响,可能会导致厌氧细菌全部死亡,第二年要面对厌氧系统的重新启动,增大企业的治理负担。(3) Seasonal wastewater has an impact on the anaerobic system and increases the burden on enterprises. Wastewater from non-fermented soy products is a typical organic wastewater. In general, a combined anaerobic and aerobic treatment system is used in the biochemical stage. However, non-fermented soy products have seasonal characteristics. In the absence of water in winter, the anaerobic system will If it is greatly affected, it may lead to the death of all anaerobic bacteria. In the second year, the anaerobic system will be restarted, which will increase the management burden of the enterprise.
(4)资源回收利用率低。豆制品废水中含有氧化型酵母菌生产所需要的碳、氮、磷及微量金属元素。酵母菌在氧气充足的情况下可将糖类全部分解为二氧化碳和水,同时产生大量含蛋白质的菌丝体,它可回收作为饲料蛋白。利用厌氧法处理豆制品废水时,每去除1kgCOD,便可以获得0.6~0.8m3沼气,沼气经处理后可用作发电或燃气。但是在目前采用的处理工艺中,主要重视对于水的处理,而这部分资源的回收利用率十分低。(4) The recycling rate of resources is low. Soy product wastewater contains carbon, nitrogen, phosphorus and trace metal elements required for the production of oxidative yeasts. In the case of sufficient oxygen, yeast can decompose all sugars into carbon dioxide and water, and at the same time produce a large amount of protein-containing mycelium, which can be recycled as feed protein. When the soybean product wastewater is treated by anaerobic method, 0.6-0.8m 3 of biogas can be obtained for every 1kg of COD removed, and the biogas can be used for power generation or fuel gas after treatment. However, in the currently used treatment process, the main emphasis is on the treatment of water, and the recycling rate of this part of resources is very low.
因此,本发明提出一种模块化集成工艺,针对非发酵类豆制品生产废水的特点和目前处理系统存在的问题,筛选效果优良、节能降耗的先进处理工艺,进行工艺耦合集成与参数化设计,实现工艺模块化、智能化、集成化。Therefore, the present invention proposes a modular integration process, aiming at the characteristics of non-fermented soy product production wastewater and the problems existing in the current treatment system, screening advanced treatment processes with excellent effect, energy saving and consumption reduction, process coupling integration and parametric design , to achieve process modularization, intelligence and integration.
发明内容Contents of the invention
为解决上述技术问题,本发明提供一种用于非发酵类豆制品生产废水处理的模块化集成工艺方法,包括一级预处理模块、二级生化模块和三级深度处理模块,一级预处理模块设置细网格筛和气浮隔油沉淀调节水池,去除悬浮物、浮油和调节水量水质;二级生化模块设置厌氧单元和好氧单元,去除废水中主要污染物;三级深度处理模块设置微砂沉淀池、活性砂滤池、动态膜过滤系统和紫外线消毒反应器,去除SS和消毒。针对高浓度非发酵类豆制品生产废水,进行工艺集成与参数化设计,根据进水水质条件,选择运行不同单元。本发明工艺具有灵活、高效、便捷、智能等特点,能够保证废水处理设施经济、有效、稳定的运行。In order to solve the above technical problems, the present invention provides a modular integrated process method for the treatment of non-fermented soybean product production wastewater, including a first-level pretreatment module, a second-level biochemical module and a third-level advanced treatment module, and a first-level pretreatment module The module is equipped with a fine mesh screen and an air flotation oil separation sedimentation adjustment pool to remove suspended solids, oil slicks and adjust water quality and water quality; the secondary biochemical module is equipped with anaerobic units and aerobic units to remove main pollutants in wastewater; the third-level advanced treatment module Set micro-sand sedimentation tank, active sand filter, dynamic membrane filtration system and ultraviolet disinfection reactor to remove SS and disinfect. For high-concentration non-fermented soybean product production wastewater, process integration and parameterization design are carried out, and different units are selected to operate according to the water quality conditions of the influent. The process of the invention has the characteristics of flexibility, high efficiency, convenience, intelligence and the like, and can ensure the economical, effective and stable operation of waste water treatment facilities.
根据生产废水的特点,以及废水处理工艺的要求,秉持技术成熟可靠、运行稳定、维护管理方便及经济适用的原则,对非发酵类豆制品生产废水处理工艺进行优化集成,并开发出一套适用差别水质的运行方法。豆制品废水是一种有机物含量较高的废水,BOD/COD之比高达0.55~0.65,C、N、P之比为100:4.7:0.2。pH较低,废水中基本不含有毒有害的物质。因此,豆制品废水适宜采用生物法进行处理。According to the characteristics of production wastewater and the requirements of wastewater treatment process, adhering to the principles of mature and reliable technology, stable operation, convenient maintenance and management, and economical applicability, optimize and integrate non-fermented soybean product production wastewater treatment process, and develop a set of applicable Different water quality operation methods. Soy product wastewater is a kind of wastewater with high organic matter content, the ratio of BOD/COD is as high as 0.55-0.65, and the ratio of C, N, and P is 100:4.7:0.2. The pH is low, and the wastewater basically does not contain toxic and harmful substances. Therefore, soybean wastewater is suitable for biological treatment.
具体技术方案如下:The specific technical scheme is as follows:
处理非发酵类豆制品生产废水的模块化集成系统,包括一级预处理模块、二级生化模块和三级深度处理模块;一级预处理模块设置细网格筛和气浮隔油沉淀调节水池;二级生化模块设置厌氧单元和好氧单元,厌氧单元包括厌氧流化床反应器和厌氧连续搅拌反应器,好氧单元包括生物接触氧化反应器和缺氧-好氧曝气生物滤池反应器;三级深度处理模块设置微砂沉淀池、活性砂滤池、动态膜过滤系统和紫外线消毒反应器。A modular integrated system for treating non-fermented soybean product production wastewater, including a first-level pretreatment module, a second-level biochemical module and a third-level advanced treatment module; the first-level pretreatment module is equipped with a fine mesh screen and an air flotation oil separation sedimentation adjustment pool; The secondary biochemical module is equipped with anaerobic unit and aerobic unit. The anaerobic unit includes anaerobic fluidized bed reactor and anaerobic continuous stirring reactor. The aerobic unit includes biological contact oxidation reactor and anoxic-aerobic aerated organism Filter reactor; the three-level advanced treatment module is equipped with micro-sand sedimentation tank, active sand filter, dynamic membrane filtration system and ultraviolet disinfection reactor.
所述一级预处理模块细网格筛进口连接非发酵类豆制品生产废水入口,出口连接所述气浮隔油沉淀调节水池进口;所述气浮隔油沉淀调节水池出口连接所述二级生化模块进口;The inlet of the fine mesh sieve of the primary pretreatment module is connected to the inlet of non-fermented bean product production wastewater, and the outlet is connected to the inlet of the air flotation oil separation and sedimentation adjustment pool; the outlet of the air flotation oil separation sedimentation adjustment water pool is connected to the secondary Biochemical module import;
所述二级生化模块的厌氧单元进口连接所述一级预处理模块气浮隔油沉淀调节水池出口;所述厌氧流化床进口连接所述厌氧单元进口,所述厌氧流化床出口连接所述厌氧单元出口,所述厌氧连续搅拌反应器进口连接所述厌氧单元进口,所述厌氧连续搅拌反应器出口连接所述厌氧单元出口;所述厌氧单元出口连接所述好氧单元进口;所述好氧单元出口连接所述三级深度处理模块进口,所述生物接触氧化反应池进口连接所述好氧单元进口,所述生物接触氧化反应池出口连接所述好氧单元出口,所述缺氧-好氧曝气生物滤池进口连接所述好氧单元进口,所述缺氧-好氧曝气生物滤池出口连接所述好氧单元出口;The inlet of the anaerobic unit of the secondary biochemical module is connected to the outlet of the air flotation, oil separation and sedimentation adjustment tank of the primary pretreatment module; the inlet of the anaerobic fluidized bed is connected to the inlet of the anaerobic unit, and the anaerobic fluidized bed The outlet of the bed is connected to the outlet of the anaerobic unit, the inlet of the anaerobic continuous stirring reactor is connected to the inlet of the anaerobic unit, the outlet of the anaerobic continuous stirring reactor is connected to the outlet of the anaerobic unit; the outlet of the anaerobic unit Connect the inlet of the aerobic unit; the outlet of the aerobic unit is connected to the inlet of the three-stage advanced treatment module, the inlet of the biological contact oxidation reaction tank is connected to the inlet of the aerobic unit, and the outlet of the biological contact oxidation reaction tank is connected to the The outlet of the aerobic unit, the inlet of the anoxic-aerobic biological aerated filter is connected to the inlet of the aerobic unit, and the outlet of the anoxic-aerobic biological aerated filter is connected to the outlet of the aerobic unit;
所述三级深度处理模块的微砂沉淀池入口连接所述二级生化处理模块出口,出口连接所述活性砂滤池入口;所述活性砂滤池出口连接至所述动态膜过滤反应器入口;所述动态膜过滤系统出口连接所述紫外线消毒反应器入口;所述紫外线消毒反应器出口连接至水处理系统总出口;The inlet of the micro-sand sedimentation tank of the third-level advanced treatment module is connected to the outlet of the second-level biochemical treatment module, and the outlet is connected to the inlet of the active sand filter; the outlet of the active sand filter is connected to the inlet of the dynamic membrane filtration reactor ; The outlet of the dynamic membrane filtration system is connected to the inlet of the ultraviolet disinfection reactor; the outlet of the ultraviolet disinfection reactor is connected to the total outlet of the water treatment system;
所述厌氧流化床反应器、厌氧连续搅拌反应器、生物接触氧化反应池、缺氧-好氧曝气生物滤池和动态膜过滤系统进口前设置监测装置和电动阀门,根据运行水质条件,自动选择运行不同单元;The anaerobic fluidized bed reactor, anaerobic continuous stirring reactor, biological contact oxidation reaction tank, anoxic-aerobic biological aerated filter and dynamic membrane filtration system are equipped with monitoring devices and electric valves before the import, according to the operating water quality Conditions, automatically select different units to run;
处理非发酵类豆制品生产废水的模块化集成工艺,包括以下步骤:A modular integrated process for treating non-fermented soybean product production wastewater, comprising the following steps:
(1)启动运行一级预处理模块,将非发酵类豆制品生产废水引入总污水处理系统中,废水首先经过在细网格筛,除去废水中的较大物质;(1) Start the operation of the first-level pretreatment module, and introduce the non-fermented soy product production wastewater into the total sewage treatment system. The wastewater first passes through a fine mesh screen to remove larger substances in the wastewater;
(2)启动气浮隔油沉淀调节水池,除去水中的油、悬浮物和调节水质水量;(2) Start the air flotation oil separation sedimentation adjustment pool to remove oil and suspended solids in the water and adjust the water quality and quantity;
(3)在线监测分析气浮隔油沉淀调节水池中的废水COD值,结合实际水量Q实与设计水量Q设的关系选择不同运行单元;(3) On-line monitoring and analysis of the COD value of wastewater in the air flotation, oil separation and sedimentation adjustment pool, and the selection of different operating units in combination with the relationship between the actual water volume Q and the design water volume Q;
(4)当Q实≥1/2Q设,且COD≥2000时,运行步骤(5),否则运行步骤(6);(4) When Q is greater than or equal to 1/2Q, and COD is greater than or equal to 2000, execute step (5), otherwise execute step (6);
(5)启动厌氧连续搅拌反应器,去除水中的污染物,运行步骤(7);(5) start the anaerobic continuous stirring reactor, remove pollutants in water, and run step (7);
(6)启动厌氧流化床反应器,去除水中的污染物;(6) Start the anaerobic fluidized bed reactor to remove pollutants in the water;
(7)在线监测分析厌氧单元出水的COD值、BOD值和氨氮值,当COD>500mg/L,或BOD>300mg/L,或氨氮>40mg/L时,进入步骤(8),否则进入步骤(10);(7) On-line monitoring and analysis of the COD value, BOD value and ammonia nitrogen value of the effluent of the anaerobic unit. When COD>500mg/L, or BOD>300mg/L, or ammonia nitrogen>40mg/L, enter step (8), otherwise enter step (10);
(8)启动缺氧-好氧曝气生物滤池,去除水中的污染物;(8) Start the anoxic-aerobic biological aerated filter to remove pollutants in the water;
(9)在线监测分析厌氧流化床反应器出水的COD值、BOD值和氨氮值,当COD>100mg/L,或BOD>30mg/L,或氨氮>15mg/L时,进入步骤(10),否则进入步骤(11);(9) On-line monitoring and analysis of the COD value, BOD value and ammonia nitrogen value of the anaerobic fluidized bed reactor effluent, when COD>100mg/L, or BOD>30mg/L, or when ammonia nitrogen>15mg/L, enter step (10 ), otherwise enter step (11);
(10)启动生物接触氧化反应器,去除水中的污染物;(10) start the biological contact oxidation reactor to remove pollutants in the water;
(11)启动微砂沉淀池,对废水进行沉淀排泥;(11) Start the micro-sand sedimentation tank to sediment and discharge the waste water;
(12)启动活性砂滤池,对废水进行过滤处理;(12) Start the active sand filter to filter the waste water;
(13)根据出水水质要求,当出水水质要求SS<15mg/L,进入步骤(14),否则进入步骤(15);(13) According to the effluent water quality requirement, when the effluent water quality requirement SS<15mg/L, enter step (14), otherwise enter step (15);
(14)启动动态膜过滤反应器,对废水进行过滤处理;(14) Start the dynamic membrane filtration reactor to filter the waste water;
(15)启动紫外线消毒反应器,对废水进行消毒处理。(15) Start the ultraviolet disinfection reactor to disinfect the waste water.
所述细网格筛设计格网尺寸采用10mm;所述气浮隔油沉淀调节水池,气浮区反应区设计停留时间为5min,气浮区接触室设计流速为0.05m/s,接触室设计停留时间为2min,气浮区分离室表面负荷为6~8m3/(m2·h);隔油区,设计2级隔油下挡板,1级隔油上挡板,1台浮子撇油器,浮子撇油器设置在隔油上挡板前;沉淀区,包括沉渣斗2~4个,排渣系统1套;调节水池设计停留时间为12~24h;The design grid size of the fine mesh sieve is 10mm; the air flotation oil separation sedimentation adjustment pool, the design residence time of the reaction zone in the air flotation zone is 5min, the design flow velocity of the contact chamber in the air flotation zone is 0.05m/s, and the design of the contact chamber is 0.05m/s. The residence time is 2 minutes, and the surface load of the separation chamber in the air flotation area is 6~8m 3 /(m 2 h); in the oil separation area, the lower baffle plate for 2-stage oil separation, the upper baffle plate for 1-stage oil separation, and 1 set of float skimmer are designed. The oiler and the float oil skimmer are set in front of the upper baffle plate of the oil separator; the sedimentation area includes 2 to 4 sediment buckets, and 1 set of slag discharge system; the designed residence time of the adjustment pool is 12 to 24 hours;
所述厌氧流化床反应器设计负荷为5~8kgCOD/(m3·d),设计最大上升流速为8~10m/h;所述厌氧连续搅拌反应器设计停留时间20d;所述生物接触氧化反应器设计BOD负荷为1.5kg/(m3·d);所述缺氧-好氧曝气生物滤池反应器,缺氧区设计停留时间为3h,硝化液回流比为200%,设计BOD负荷为1.8~2.0kgBOD/(m3·d);The design load of the anaerobic fluidized bed reactor is 5-8kgCOD/(m 3 ·d), and the design maximum ascending flow rate is 8-10m/h; the design residence time of the anaerobic continuous stirring reactor is 20d; the biological The design BOD load of the contact oxidation reactor is 1.5kg/(m 3 ·d); the anoxic-aerobic biological aerated filter reactor, the designed residence time in the anoxic zone is 3h, and the reflux ratio of the nitrifying liquid is 200%. The design BOD load is 1.8~2.0kgBOD/(m 3 ·d);
所述微砂沉淀池设计表面负荷为10~14m3/(m2·h);所述活性砂滤池设计平均滤速为6m/h;所述动态膜过滤系统,设计滤速为12~15m/h;采用尼龙筛网、涤纶无纺布和硅藻土作为成膜物质,尼龙筛网尺寸为1cm╳1cm,设计网眼尺寸为10目,涤纶无纺布尺寸为1cm╳1cm,单位面积质量为250~300g/m2,硅藻土设计渗透率为0.15~0.25Darcy,尼龙筛网、涤纶无纺布和硅藻土的质量比为10:1:5。The design surface load of the micro-sand sedimentation tank is 10-14m 3 /(m 2 h); the design average filtration rate of the active sand filter is 6m/h; the design filtration rate of the dynamic membrane filtration system is 12- 15m/h; Nylon screen, polyester non-woven fabric and diatomite are used as film-forming materials, the size of nylon screen is 1cm╳1cm, the design mesh size is 10 mesh, the size of polyester non-woven fabric is 1cm╳1cm, unit area The mass is 250-300g/m 2 , the design permeability of diatomite is 0.15-0.25Darcy, and the mass ratio of nylon mesh, polyester non-woven fabric and diatomite is 10:1:5.
本方法的优点是:The advantages of this method are:
(1)适用于水质水量变化较大的非发酵类豆制品生产场高浓度废水处理;可以解决非发酵类豆制品生产废水具有季节性特点这一技术问题。(1) It is suitable for the treatment of high-concentration wastewater from non-fermented soy product production fields with large changes in water quality and quantity; it can solve the technical problem that non-fermented soy product production wastewater has seasonal characteristics.
(2)本发明中采用的多个单元串联形式,通过改变设备运行参数自动控制转换工艺,能适应水质水量变化较大的系统,同时节省运行能耗和费用;最大限度节省了占地面积的同时节省造价;本发明工艺组合模块化程度高,有利于技术转化为集成设备,节省空间;工艺组合技术先进,稳定达标。(2) The multiple units connected in series form adopted in the present invention can adapt to systems with large changes in water quality and quantity by changing the equipment operating parameters to automatically control the conversion process, while saving energy consumption and expenses in operation; saving floor area to the greatest extent At the same time, the cost is saved; the process combination of the invention has a high degree of modularization, which is conducive to the transformation of technology into integrated equipment and saves space; the process combination technology is advanced and stable up to the standard.
(3)本发明一级预处理模块中,细网格筛安装在气浮隔油沉淀调节水池进口处,用来去除可能堵塞水泵机组及管道阀门的悬浮物,并保证后续处理设施能正常运行;气浮隔油沉淀调节水池,同时具有除油、除悬浮物和调节水质水量的功能。(3) In the first-level pretreatment module of the present invention, the fine mesh screen is installed at the inlet of the air flotation, oil separation and sedimentation adjustment pool to remove suspended matter that may block the water pump unit and pipeline valves, and to ensure the normal operation of subsequent treatment facilities ; The air flotation, oil separation and sedimentation adjustment pool has the functions of removing oil, removing suspended solids and adjusting water quality and quantity.
(4)本发明二级生化模块中的厌氧单元采用厌氧流化床反应器和厌氧连续搅拌反应器。厌氧流化床反应器,是一种高效的生物膜法处理方法,利用砂等大表面积的物质为载体。厌氧微生物以膜形式结在砂或其它载体的表面,在污水中成流动状态,微生物与污水中的有机物进行接触吸附分解有机物,从而达到处理的目的与传统厌氧反应器相比,厌氧流化床反应器在低温条件下对有机废水和低负荷有机废水有很好的去除效果,因此不需要额外的保温系统,也更能适应水质水量变化较大的水处理系统;厌氧连续搅拌反应器,是一种使发酵原料和微生物处于完全混合状态的厌氧处理技术,在一个密闭罐体内完成料液的发酵、沼气产生的过程,消化器内安装有搅拌装置,使发酵原料和微生物处于完全混合状态,投料方式采用恒温连续投料或半连续投料运行,新进入的原料由于搅拌作用很快与发酵器内的全部发酵液菌种混合,使发酵底物浓度始终保持相对较低状态,厌氧连续搅拌反应器可以处理高悬浮固体含量的原料,消化器内物料均匀分布,避免了分层状态,增加了物料和微生物接触的机会,利用产生沼气发电余热对反应器外部的保温加热系统进行保温,大大提高了产气率和投资利用率,同时使得反应器一年四季均可正常工作,降低占地面积和运行成本。(4) The anaerobic unit in the secondary biochemical module of the present invention adopts an anaerobic fluidized bed reactor and an anaerobic continuous stirring reactor. The anaerobic fluidized bed reactor is an efficient biofilm treatment method, using materials with large surface areas such as sand as carriers. Anaerobic microorganisms are bound on the surface of sand or other carriers in the form of a film, and they are in a flowing state in the sewage. The microorganisms contact with the organic matter in the sewage, absorb and decompose the organic matter, so as to achieve the purpose of treatment. Compared with traditional anaerobic reactors, anaerobic The fluidized bed reactor has a good removal effect on organic wastewater and low-load organic wastewater under low temperature conditions, so no additional insulation system is needed, and it is more suitable for water treatment systems with large changes in water quality and quantity; anaerobic continuous stirring The reactor is an anaerobic treatment technology that makes the fermentation raw materials and microorganisms in a completely mixed state. The fermentation of the feed liquid and the generation of biogas are completed in a closed tank. A stirring device is installed in the digester to make the fermentation raw materials and microorganisms It is in a completely mixed state, and the feeding method adopts constant temperature continuous feeding or semi-continuous feeding operation. The newly entered raw materials are quickly mixed with all the fermentation broth bacteria in the fermenter due to the stirring effect, so that the concentration of the fermentation substrate is always kept relatively low. The anaerobic continuous stirring reactor can handle raw materials with high suspended solid content. The material in the digester is evenly distributed, avoiding the stratification state, increasing the chance of contact between the material and microorganisms, and utilizing the waste heat generated from biogas to generate electricity for the thermal insulation and heating system outside the reactor. Thermal insulation greatly improves the gas production rate and investment utilization rate, and at the same time enables the reactor to work normally throughout the year, reducing floor space and operating costs.
本发明二级生化模块中的好氧单元采用生物接触氧化反应器和缺氧-好氧曝气生物滤池反应器。生物接触氧化反应器,是一种好氧处理污水的生物反应器,内装填一定数量的填料,利用生长在填料上的生物膜和供应充足的氧气去除污染物;缺氧-好氧曝气生物滤池反应器,在传统曝气生物滤池反应器的基础上,前面设置缺氧单元,生物滤池反应器后设硝化液回流系统。The aerobic unit in the secondary biochemical module of the present invention adopts a biological contact oxidation reactor and an anoxic-aerobic aerated biological filter tank reactor. Biological contact oxidation reactor is a bioreactor for aerobic treatment of sewage. It is filled with a certain amount of filler, and removes pollutants by using the biofilm grown on the filler and sufficient oxygen supply; anoxic-aerobic aerated biological The filter reactor, on the basis of the traditional biological aerated filter reactor, is equipped with anoxic unit in front, and a nitrification liquid return system is installed behind the biological filter reactor.
(5)本发明二级生化模块中采用的厌氧工艺均为快速启动型,并且无外部增温系统的先进厌氧工艺,适合冬季无水时停运,停运后快速启动的废水处理系统,并且大大降低运行费用;采用厌氧连续搅拌反应器系统充分利用非发酵类豆制品生产废水的特点,产生沼气资源并实现回收利用,提高资源回收利用率,降低运行成本。(5) The anaerobic process adopted in the secondary biochemical module of the present invention is a quick-start type, and there is no advanced anaerobic process of an external warming system, which is suitable for shutting down when there is no water in winter, and a waste water treatment system that starts quickly after shutting down , and greatly reduce operating costs; the anaerobic continuous stirring reactor system makes full use of the characteristics of non-fermented soybean product production wastewater, generates biogas resources and realizes recycling, improves resource recycling and utilization rates, and reduces operating costs.
(6)本发明三级深度处理模块中,微砂沉淀工艺,是一种紧凑、高效、灵活的快速沉淀技术,其特点是利用微砂与高分子絮凝剂共同作用,使污染物与微砂聚合成直径150μm以上的大颗粒絮体而加速沉淀分离,同时结合斜板沉淀原理减少沉淀池面积及沉淀时间,保持良好稳定的出水效果;活性砂滤池,是一种集絮凝、澄清、过滤为一体的连续接触过滤设备,目的是将沉淀后污水进一步实现泥水分离,保证出水SS达标;动态膜过滤系统,利用微米级孔径的微网材料实现固液分离,其截留能力可达微滤或超滤水平;紫外线消毒,利用适当波长的紫外线能够破坏微生物机体细胞中的DNA(脱氧核糖核酸)或RNA(核糖核酸)的分子结构,造成生长性细胞死亡和(或)再生性细胞死亡,达到杀菌消毒的效果。(6) In the three-level advanced treatment module of the present invention, the micro-sand precipitation process is a compact, efficient, and flexible rapid precipitation technology, which is characterized in that the micro-sand and polymer flocculant act together to make the pollutants and micro-sand Aggregate into large particle flocs with a diameter of 150 μm or more to accelerate sedimentation and separation, and at the same time combine the principle of inclined plate sedimentation to reduce the area of the sedimentation tank and the sedimentation time, and maintain a good and stable water outlet effect; the active sand filter is a collection of flocculation, clarification, filtration Integrated continuous contact filtration equipment, the purpose is to further realize the separation of sludge and water after sedimentation, and ensure that the effluent SS reaches the standard; the dynamic membrane filtration system uses micro-mesh materials with micron-sized pores to achieve solid-liquid separation, and its retention capacity can reach microfiltration or Ultrafiltration level; ultraviolet disinfection, the use of ultraviolet rays of appropriate wavelengths can destroy the molecular structure of DNA (deoxyribonucleic acid) or RNA (ribonucleic acid) in the cells of microorganisms, causing growth cell death and (or) regenerative cell death, reaching The effect of sterilization and disinfection.
(7)本发明资源回收利用率高,节能降耗,环境友好。(7) The resource recycling rate of the present invention is high, energy saving and consumption reducing, and environment friendly.
附图说明Description of drawings
图1为本发明工艺路线图;Fig. 1 is process roadmap of the present invention;
图2为本发明中气浮隔油沉淀调节水池示意图。Fig. 2 is a schematic diagram of the air flotation, oil separation and sedimentation adjustment tank in the present invention.
图中,1—一级预处理模块;2—二级生化模块;3—三级深度处理模块;4—调节水池;5—进水管;6—气浮反应区;7—搅拌器;8—接触室;9—溶气水;10—气浮分离室;11—隔油区;12—隔油下挡板;13—隔油上挡板;14—浮子撇油器;15—沉淀区;16—沉渣斗;17—排渣系统;18—污水泵;19—出水管。In the figure, 1—first-level pretreatment module; 2—second-level biochemical module; 3—third-level advanced treatment module; 4—regulating pool; 5—inlet pipe; 6—air flotation reaction zone; 7—agitator; 8— Contact chamber; 9—dissolved air water; 10—air flotation separation chamber; 11—oil separation area; 12—oil separation lower baffle; 13—oil separation upper baffle; 14—float oil skimmer; 15—sedimentation area; 16—sediment bucket; 17—slag discharge system; 18—sewage pump; 19—water outlet pipe.
具体实施方式Detailed ways
下面结合附图对本发明进行详细说明,但本发明的保护范围不受实施例所限。The present invention will be described in detail below in conjunction with the accompanying drawings, but the protection scope of the present invention is not limited by the embodiments.
图1为本发明工艺路线图,如图所示,处理非发酵类豆制品生产废水的模块化集成系统,包括一级预处理模块1、二级生化模块2和三级深度处理模块3;一级预处理模块1设置细网格筛和气浮隔油沉淀调节水池;二级生化模块2设置厌氧单元和好氧单元,厌氧单元包括厌氧流化床反应器和厌氧连续搅拌反应器,好氧单元包括生物接触氧化反应器和缺氧-好氧曝气生物滤池反应器;三级深度处理模块3设置微砂沉淀池、活性砂滤池、动态膜过滤系统和紫外线消毒反应器。Fig. 1 is a process roadmap of the present invention, as shown in the figure, the modular integrated system for processing non-fermented bean product production wastewater includes a first-level pretreatment module 1, a second-level biochemical module 2 and a third-level advanced treatment module 3; The first stage pretreatment module is equipped with fine mesh screen and air flotation oil separation sedimentation adjustment tank; the second level biochemical module 2 is equipped with anaerobic unit and aerobic unit, and the anaerobic unit includes anaerobic fluidized bed reactor and anaerobic continuous stirring reactor , the aerobic unit includes biological contact oxidation reactor and anoxic-aerobic biological aerated filter reactor; three-level advanced treatment module 3 is equipped with micro-sand sedimentation tank, active sand filter, dynamic membrane filtration system and ultraviolet disinfection reactor .
一级预处理模块1细网格筛进口连接非发酵类豆制品生产废水入口,出口连接气浮隔油沉淀调节水池进口;气浮隔油沉淀调节水池出口连接二级生化模块进口;The inlet of the first-level pretreatment module 1 fine mesh screen is connected to the inlet of non-fermented bean product production wastewater, and the outlet is connected to the inlet of the air flotation oil separation sedimentation adjustment tank; the outlet of the air flotation oil separation sedimentation adjustment tank is connected to the inlet of the secondary biochemical module;
二级生化模块2的厌氧单元进口连接一级预处理模块气浮隔油沉淀调节水池出口;厌氧流化床进口连接厌氧单元进口,所述厌氧流化床出口连接厌氧单元出口,厌氧连续搅拌反应器进口连接厌氧单元进口,厌氧连续搅拌反应器出口连接厌氧单元出口;厌氧单元出口连接好氧单元进口;好氧单元出口连接三级深度处理模块进口,生物接触氧化反应池进口连接好氧单元进口,生物接触氧化反应池出口连接好氧单元出口,缺氧-好氧曝气生物滤池进口连接好氧单元进口,缺氧-好氧曝气生物滤池出口连接好氧单元出口;The inlet of the anaerobic unit of the secondary biochemical module 2 is connected to the outlet of the air flotation, oil separation and sedimentation adjustment pool of the first-level pretreatment module; the inlet of the anaerobic fluidized bed is connected to the inlet of the anaerobic unit, and the outlet of the anaerobic fluidized bed is connected to the outlet of the anaerobic unit , the inlet of the anaerobic continuously stirred reactor is connected to the inlet of the anaerobic unit, the outlet of the anaerobic continuously stirred reactor is connected to the outlet of the anaerobic unit; the outlet of the anaerobic unit is connected to the inlet of the aerobic unit; the outlet of the aerobic unit is connected to the inlet of the three-stage advanced treatment module The inlet of the contact oxidation reaction tank is connected to the inlet of the aerobic unit, the outlet of the biological contact oxidation reaction tank is connected to the outlet of the aerobic unit, the inlet of the anoxic-aerobic biological aerated filter is connected to the inlet of the aerobic unit, and the anoxic-aerobic biological aerated filter The outlet is connected to the outlet of the aerobic unit;
三级深度处理模块3的微砂沉淀池入口连接所述二级生化处理模块出口,出口连接所述活性砂滤池入口;所述活性砂滤池出口连接至所述动态膜过滤反应器入口;所述动态膜过滤系统出口连接所述紫外线消毒反应器入口;所述紫外线消毒反应器出口连接至水处理系统总出口;The inlet of the micro-sand sedimentation tank of the third-level advanced treatment module 3 is connected to the outlet of the secondary biochemical treatment module, and the outlet is connected to the inlet of the active sand filter; the outlet of the active sand filter is connected to the inlet of the dynamic membrane filtration reactor; The outlet of the dynamic membrane filtration system is connected to the inlet of the ultraviolet disinfection reactor; the outlet of the ultraviolet disinfection reactor is connected to the total outlet of the water treatment system;
厌氧流化床反应器、厌氧连续搅拌反应器、生物接触氧化反应池、缺氧-好氧曝气生物滤池和动态膜过滤系统进口前设置监测装置和电动阀门,根据运行水质条件,自动选择运行不同单元。Anaerobic fluidized bed reactors, anaerobic continuous stirring reactors, biological contact oxidation reaction tanks, anoxic-aerobic aerated biological filters and dynamic membrane filtration systems are equipped with monitoring devices and electric valves before the import. According to the operating water quality conditions, Automatic selection of different units to run.
处理非发酵类豆制品生产废水的模块化集成工艺,包括以下步骤:A modular integrated process for treating non-fermented soybean product production wastewater, comprising the following steps:
(1)启动运行一级预处理模块,将非发酵类豆制品生产废水引入总污水处理系统中,废水首先经过在细网格筛,除去废水中的较大物质;(1) Start the operation of the first-level pretreatment module, and introduce the non-fermented soy product production wastewater into the total sewage treatment system. The wastewater first passes through a fine mesh screen to remove larger substances in the wastewater;
(2)启动气浮隔油沉淀调节水池,除去水中的油、悬浮物和调节水质水量;(2) Start the air flotation oil separation sedimentation adjustment pool to remove oil and suspended solids in the water and adjust the water quality and quantity;
(3)在线监测分析气浮隔油沉淀调节水池中的废水COD值,结合实际水量Q实与设计水量Q设的关系选择不同运行单元;(3) On-line monitoring and analysis of the COD value of wastewater in the air flotation, oil separation and sedimentation adjustment pool, and the selection of different operating units in combination with the relationship between the actual water volume Q and the design water volume Q;
(4)当Q实≥1/2Q设,且COD≥2000时,运行步骤(5),否则运行步骤(6);(4) When Q is greater than or equal to 1/2Q, and COD is greater than or equal to 2000, execute step (5), otherwise execute step (6);
(5)启动厌氧连续搅拌反应器,去除水中的污染物,运行步骤(7);(5) start the anaerobic continuous stirring reactor, remove pollutants in water, and run step (7);
(6)启动厌氧流化床反应器,去除水中的污染物;(6) Start the anaerobic fluidized bed reactor to remove pollutants in the water;
(7)在线监测分析厌氧单元出水的COD值、BOD值和氨氮值,当COD>500mg/L,或BOD>300mg/L,或氨氮>40mg/L时,进入步骤(8),否则进入步骤(10);(7) On-line monitoring and analysis of the COD value, BOD value and ammonia nitrogen value of the effluent of the anaerobic unit. When COD>500mg/L, or BOD>300mg/L, or ammonia nitrogen>40mg/L, enter step (8), otherwise enter step (10);
(8)启动缺氧-好氧曝气生物滤池,去除水中的污染物;(8) Start the anoxic-aerobic biological aerated filter to remove pollutants in the water;
(9)在线监测分析厌氧流化床反应器出水的COD值、BOD值和氨氮值,当COD>100mg/L,或BOD>30mg/L,或氨氮>15mg/L时,进入步骤(10),否则进入步骤(11);(9) On-line monitoring and analysis of the COD value, BOD value and ammonia nitrogen value of the anaerobic fluidized bed reactor effluent, when COD>100mg/L, or BOD>30mg/L, or when ammonia nitrogen>15mg/L, enter step (10 ), otherwise enter step (11);
(10)启动生物接触氧化反应器,去除水中的污染物;(10) start the biological contact oxidation reactor to remove pollutants in the water;
(11)启动微砂沉淀池,对废水进行沉淀排泥;(11) Start the micro-sand sedimentation tank to sediment and discharge the waste water;
(12)启动活性砂滤池,对废水进行过滤处理;(12) Start the active sand filter to filter the waste water;
(13)根据出水水质要求,当出水水质要求SS<15mg/L,进入步骤(14),否则进入步骤(15);(13) According to the effluent water quality requirement, when the effluent water quality requirement SS<15mg/L, enter step (14), otherwise enter step (15);
(14)启动动态膜过滤反应器,对废水进行过滤处理;(14) start the dynamic membrane filtration reactor to filter the waste water;
(15)启动紫外线消毒反应器,对废水进行消毒处理。(15) Start the ultraviolet disinfection reactor to disinfect the waste water.
实施例1:Example 1:
本实施例采用图1所示的模块化集成工艺系统及方法对沈阳某非发酵类豆制品加工厂的废水进行处理,处理过程中:细网格筛设计格网尺寸采用10mm;气浮隔油沉淀调节水池,气浮区反应区设计停留时间为5min,气浮区接触室设计流速为0.05m/s,接触室设计停留时间为2min,气浮区分离室表面负荷为6m3/(m2·h);隔油区,设计2级隔油下挡板,1级隔油上挡板,1台浮子撇油器,浮子撇油器设置在隔油上挡板前;沉淀区,包括沉渣斗2个,排渣系统1套;调节水池设计停留时间为12h;In this embodiment, the modularized integrated process system and method shown in Figure 1 are used to treat the wastewater of a non-fermented bean product processing factory in Shenyang. During the treatment process: the designed mesh size of the fine mesh screen is 10 mm; Settling adjustment pool, the design residence time of the reaction zone in the air flotation area is 5min, the design flow velocity of the contact chamber in the air flotation area is 0.05m/s, the design residence time of the contact chamber is 2min, and the surface load of the separation chamber in the air flotation area is 6m 3 /(m 2 h); oil separation area, design 2-stage oil separation lower baffle, 1st-stage oil separation upper baffle, 1 float oil skimmer, the float oil skimmer is set in front of the oil separation upper baffle; sedimentation area, including sediment 2 buckets, 1 set of slag discharge system; the design residence time of the regulating pool is 12h;
厌氧流化床反应器设计负荷为5kgCOD/(m3·d),设计最大上升流速为8m/h;厌氧连续搅拌反应器设计停留时间20d;生物接触氧化反应器设计BOD负荷为1.5kg/(m3·d);缺氧-好氧曝气生物滤池反应器,缺氧区设计停留时间为3h,硝化液回流比为200%,设计BOD负荷为1.8kgBOD/(m3·d);The design load of the anaerobic fluidized bed reactor is 5kgCOD/(m 3 d), and the design maximum rising velocity is 8m/h; the design residence time of the anaerobic continuous stirring reactor is 20d; the design BOD load of the biological contact oxidation reactor is 1.5kg /(m 3 ·d); anoxic-aerobic biological aerated filter reactor, the design residence time in the anoxic zone is 3h, the reflux ratio of nitrifying liquid is 200%, and the design BOD load is 1.8kgBOD/(m 3 ·d );
微砂沉淀池设计表面负荷为10m3/(m2·h);活性砂滤池设计平均滤速为6m/h。The design surface load of the micro-sand sedimentation tank is 10m 3 /(m 2 ·h); the design average filtration rate of the active sand filter is 6m/h.
经过本实施例的集成工艺系统及方法处理后的废水的水质检测结果如表1所示。Table 1 shows the water quality testing results of the wastewater treated by the integrated process system and method of this embodiment.
表1Table 1
实施例2:Example 2:
本实施例采用图1所示的模块化集成工艺系统及方法对沈阳某非发酵类豆制品加工厂的废水进行处理,处理过程中:细网格筛设计格网尺寸采用10mm;气浮隔油沉淀调节水池,气浮区反应区设计停留时间为5min,气浮区接触室设计流速为0.05m/s,接触室设计停留时间为2min,气浮区分离室表面负荷为7m3/(m2·h);隔油区,设计2级隔油下挡板,1级隔油上挡板,1台浮子撇油器,浮子撇油器设置在隔油上挡板前;沉淀区,包括沉渣斗3个,排渣系统1套;调节水池设计停留时间为20h;In this embodiment, the modularized integrated process system and method shown in Figure 1 are used to treat the wastewater of a non-fermented bean product processing factory in Shenyang. During the treatment process: the designed mesh size of the fine mesh screen is 10 mm; Settling adjustment pool, the design residence time of the reaction zone in the air flotation area is 5min, the design flow velocity of the contact chamber in the air flotation area is 0.05m/s, the design residence time of the contact chamber is 2min, and the surface load of the separation chamber in the air flotation area is 7m 3 /(m 2 h); oil separation area, design 2-stage oil separation lower baffle, 1st-stage oil separation upper baffle, 1 float oil skimmer, the float oil skimmer is set in front of the oil separation upper baffle; sedimentation area, including sediment 3 buckets, 1 set of slag discharge system; the design residence time of the regulating pool is 20h;
厌氧流化床反应器设计负荷为6kgCOD/(m3·d),设计最大上升流速为9m/h;生物接触氧化反应器设计BOD负荷为1.5kg/(m3·d);The design load of the anaerobic fluidized bed reactor is 6kgCOD/(m 3 ·d), and the design maximum rising flow rate is 9m/h; the design BOD load of the biological contact oxidation reactor is 1.5kg/(m 3 ·d);
微砂沉淀池设计表面负荷为10~14m3/(m2·h);活性砂滤池设计平均滤速为6m/h;动态膜过滤系统,设计滤速为13m/h;采用尼龙筛网、涤纶无纺布和硅藻土作为成膜物质,尼龙筛网尺寸为1cm╳1cm,设计网眼尺寸为10目,涤纶无纺布尺寸为1cm╳1cm,单位面积质量为270g/m2,硅藻土设计渗透率为0.2Darcy,尼龙筛网、涤纶无纺布和硅藻土的质量比为10:1:5。The design surface load of the micro-sand sedimentation tank is 10-14m 3 /(m 2 h); the design average filtration rate of the active sand filter is 6m/h; the design filtration rate of the dynamic membrane filtration system is 13m/h; nylon screen is used , polyester non-woven fabric and diatomite as film-forming material, nylon mesh size is 1cm╳1cm, design mesh size is 10 mesh, polyester non-woven fabric size is 1cm╳1cm, mass per unit area is 270g/m 2 , silicon The design permeability of diatomite is 0.2Darcy, and the mass ratio of nylon mesh, polyester non-woven fabric and diatomite is 10:1:5.
经过本实施例的集成工艺系统及方法处理后的废水的水质检测结果如表2所示。Table 2 shows the water quality testing results of the wastewater treated by the integrated process system and method of this embodiment.
表2Table 2
实施例3:Example 3:
本实施例采用图1所示的模块化集成工艺系统及方法对沈阳某非发酵类豆制品加工厂的废水进行处理,处理过程中:细网格筛设计格网尺寸采用10mm;气浮隔油沉淀调节水池,气浮区反应区设计停留时间为5min,气浮区接触室设计流速为0.05m/s,接触室设计停留时间为2min,气浮区分离室表面负荷为8m3/(m2·h);隔油区,设计2级隔油下挡板,1级隔油上挡板,1台浮子撇油器,浮子撇油器设置在隔油上挡板前;沉淀区,包括沉渣斗4个,排渣系统1套;调节水池设计停留时间为24h;In this embodiment, the modularized integrated process system and method shown in Figure 1 are used to treat the wastewater of a non-fermented bean product processing factory in Shenyang. During the treatment process: the designed mesh size of the fine mesh screen is 10 mm; Settling adjustment pool, the design residence time of the reaction zone in the air flotation area is 5min, the design flow velocity of the contact chamber in the air flotation area is 0.05m/s, the design residence time of the contact chamber is 2min, and the surface load of the separation chamber in the air flotation area is 8m 3 /(m 2 h); oil separation area, design 2-stage oil separation lower baffle, 1st-stage oil separation upper baffle, 1 float oil skimmer, the float oil skimmer is set in front of the oil separation upper baffle; sedimentation area, including sediment 4 buckets, 1 set of slag discharge system; the design residence time of the regulating pool is 24h;
厌氧流化床反应器设计负荷为8kgCOD/(m3·d),设计最大上升流速为10m/h;厌氧连续搅拌反应器设计停留时间20d;生物接触氧化反应器设计BOD负荷为1.5kg/(m3·d);缺氧-好氧曝气生物滤池反应器,缺氧区设计停留时间为3h,硝化液回流比为200%,设计BOD负荷为2.0kgBOD/(m3·d);The design load of the anaerobic fluidized bed reactor is 8kgCOD/(m 3 d), and the design maximum rising velocity is 10m/h; the design residence time of the anaerobic continuous stirring reactor is 20d; the design BOD load of the biological contact oxidation reactor is 1.5kg /(m 3 ·d); anoxic-aerobic biological aerated filter reactor, the design residence time in the anoxic zone is 3h, the reflux ratio of nitrifying liquid is 200%, and the design BOD load is 2.0kgBOD/(m 3 ·d );
微砂沉淀池设计表面负荷为14m3/(m2·h);活性砂滤池设计平均滤速为6m/h;动态膜过滤系统,设计滤速为15m/h;采用尼龙筛网、涤纶无纺布和硅藻土作为成膜物质,尼龙筛网尺寸为1cm╳1cm,设计网眼尺寸为10目,涤纶无纺布尺寸为1cm╳1cm,单位面积质量为300g/m2,硅藻土设计渗透率为0.25Darcy,尼龙筛网、涤纶无纺布和硅藻土的质量比为10:1:5。The design surface load of the micro-sand sedimentation tank is 14m 3 /(m 2 h); the design average filtration rate of the active sand filter is 6m/h; the design filtration rate of the dynamic membrane filtration system is 15m/h; nylon screen, polyester Non-woven fabric and diatomaceous earth are used as film-forming materials, the size of nylon mesh is 1cm╳1cm, the design mesh size is 10 mesh, the size of polyester non-woven fabric is 1cm╳1cm, the mass per unit area is 300g/m 2 , diatomite The design permeability is 0.25Darcy, and the mass ratio of nylon mesh, polyester non-woven fabric and diatomaceous earth is 10:1:5.
经过本实施例的集成工艺系统及方法处理后的废水的水质检测结果如表3所示。Table 3 shows the water quality testing results of the wastewater treated by the integrated process system and method of this embodiment.
表3table 3
尽管上面已经示出和描述了本发明的实施例,可以理解的是,上述实施例是示例性的,不能理解为对本发明的限制,本领域的普通技术人员在本发明的范围内可以对上述实施例进行变化、修改、替换和变型。Although the embodiments of the present invention have been shown and described above, it can be understood that the above embodiments are exemplary and should not be construed as limiting the present invention, and those skilled in the art can make the above-mentioned The embodiments are subject to changes, modifications, substitutions and variations.
Claims (6)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201711444827.1A CN108083579B (en) | 2017-12-27 | 2017-12-27 | Modular integrated system and process for treating non-fermented soybean product production wastewater |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201711444827.1A CN108083579B (en) | 2017-12-27 | 2017-12-27 | Modular integrated system and process for treating non-fermented soybean product production wastewater |
Publications (2)
Publication Number | Publication Date |
---|---|
CN108083579A true CN108083579A (en) | 2018-05-29 |
CN108083579B CN108083579B (en) | 2021-02-26 |
Family
ID=62179701
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201711444827.1A Active CN108083579B (en) | 2017-12-27 | 2017-12-27 | Modular integrated system and process for treating non-fermented soybean product production wastewater |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN108083579B (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108751584A (en) * | 2018-06-04 | 2018-11-06 | 东华大学 | A kind of novel bean product production wastewater treatment and recycling system |
CN110862179A (en) * | 2019-12-19 | 2020-03-06 | 锦科绿色科技(苏州)有限公司 | Water treatment system and control workstation |
CN111252990A (en) * | 2020-03-23 | 2020-06-09 | 导洁(北京)环境科技有限公司 | Low-cost and easy-to-operate desulfurization wastewater zero-discharge method |
CN113788577A (en) * | 2021-09-13 | 2021-12-14 | 昆明理工大学 | Integrated treatment device for underground water |
CN116768427A (en) * | 2023-08-15 | 2023-09-19 | 北京百灵天地环保科技股份有限公司 | Advanced treatment process for industrial wastewater |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20140042086A1 (en) * | 2012-08-07 | 2014-02-13 | Dan Weber | Method for improving a wastewater purification process |
CN104961292A (en) * | 2015-06-04 | 2015-10-07 | 沈阳建筑大学 | Modularized integrated system and method applicable to treatment of low-temperature livestock and poultry slaughtering waste water in north |
CN106336083A (en) * | 2016-10-20 | 2017-01-18 | 沈阳建筑大学 | Integrated system and method for dairy product waste water treatment |
CN106830562A (en) * | 2017-03-23 | 2017-06-13 | 沈阳建筑大学 | A kind of petrochemical industry wastewater treatment integrated technique system and method |
CN106977042A (en) * | 2016-11-09 | 2017-07-25 | 沈阳建筑大学 | A kind of modularization integrated approach handled suitable for soy sauce brewing wastewater |
-
2017
- 2017-12-27 CN CN201711444827.1A patent/CN108083579B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20140042086A1 (en) * | 2012-08-07 | 2014-02-13 | Dan Weber | Method for improving a wastewater purification process |
CN104961292A (en) * | 2015-06-04 | 2015-10-07 | 沈阳建筑大学 | Modularized integrated system and method applicable to treatment of low-temperature livestock and poultry slaughtering waste water in north |
CN106336083A (en) * | 2016-10-20 | 2017-01-18 | 沈阳建筑大学 | Integrated system and method for dairy product waste water treatment |
CN106977042A (en) * | 2016-11-09 | 2017-07-25 | 沈阳建筑大学 | A kind of modularization integrated approach handled suitable for soy sauce brewing wastewater |
CN106830562A (en) * | 2017-03-23 | 2017-06-13 | 沈阳建筑大学 | A kind of petrochemical industry wastewater treatment integrated technique system and method |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108751584A (en) * | 2018-06-04 | 2018-11-06 | 东华大学 | A kind of novel bean product production wastewater treatment and recycling system |
CN110862179A (en) * | 2019-12-19 | 2020-03-06 | 锦科绿色科技(苏州)有限公司 | Water treatment system and control workstation |
CN111252990A (en) * | 2020-03-23 | 2020-06-09 | 导洁(北京)环境科技有限公司 | Low-cost and easy-to-operate desulfurization wastewater zero-discharge method |
CN113788577A (en) * | 2021-09-13 | 2021-12-14 | 昆明理工大学 | Integrated treatment device for underground water |
CN116768427A (en) * | 2023-08-15 | 2023-09-19 | 北京百灵天地环保科技股份有限公司 | Advanced treatment process for industrial wastewater |
Also Published As
Publication number | Publication date |
---|---|
CN108083579B (en) | 2021-02-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN108083579A (en) | Handle the modularization integrated system and technique of non-fermented class bean product production waste water | |
CN201033757Y (en) | A sewage treatment system for fruit juice wastewater | |
Ji et al. | Integrated ABR and UASB system for dairy wastewater treatment: Engineering design and practice | |
CN110668633A (en) | Kitchen waste sorting wastewater treatment system and process | |
CN102107989A (en) | Treatment method of potato type non-grain starch fuel ethanol distiller solution | |
CN201932982U (en) | Combined system using micro-electrolysis-MBR (membrane bio-reactor) combined technology to treat printing and dyeing wastewater | |
CN114685014A (en) | Livestock and poultry breeding wastewater treatment circulating system | |
CN201400630Y (en) | Chemical fiber wastewater treatment system | |
CN105819568B (en) | A kind of aerobic granular sludge sewage treatment method and special equipment with denitrification effect | |
CN108996831A (en) | A kind of method of the circulating processing beer brewery water of self energizing | |
CN102557324B (en) | Method for treating garbage leachate | |
CN101781055A (en) | Treatment method of waste papermaking water | |
CN212687862U (en) | Cassava starch production sewage treatment system | |
CN114426375A (en) | Food production wastewater treatment method | |
CN111252994A (en) | Domestic fungus wastewater treatment method | |
CN109292980A (en) | A multi-stage AO-MBBR process sewage treatment device and method with adjustable stages | |
JP5873736B2 (en) | Organic wastewater treatment method and treatment apparatus | |
CN202063797U (en) | High-concentration printing and dyeing wastewater treatment system | |
CN205328795U (en) | Wet spinning acrylic fibres production polymerization effluent disposal system | |
CN103626291A (en) | Inner circulation membrane bioreactor | |
CN108675567A (en) | Garbage percolation liquid treating system | |
CN205473253U (en) | Pharmacy sewage treatment plant | |
CN108751584A (en) | A kind of novel bean product production wastewater treatment and recycling system | |
CN211141836U (en) | Waste paper regeneration papermaking wastewater treatment device | |
CN209456252U (en) | A kind of waste water treatment system in acrylic acid production |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
TA01 | Transfer of patent application right | ||
TA01 | Transfer of patent application right |
Effective date of registration: 20210129 Address after: Room 403, building D, wisdom cloud Valley, No.1, Sanhe Road, Gaofeng community, Dalang street, Longhua District, Shenzhen, Guangdong 518000 Applicant after: Shenzhen Tianran Intellectual Property Operations Co.,Ltd. Address before: 110168 No. 9 Hunnan East Road, Hunnan District, Shenyang City, Liaoning Province Applicant before: SHENYANG JIANZHU University Effective date of registration: 20210129 Address after: 311100 211b, building 2, No.1 cangxing Road, Cangqian street, Yuhang District, Hangzhou City, Zhejiang Province Applicant after: Plant meat (Hangzhou) Health Technology Co.,Ltd. Address before: Room 403, building D, wisdom cloud Valley, No.1, Sanhe Road, Gaofeng community, Dalang street, Longhua District, Shenzhen, Guangdong 518000 Applicant before: Shenzhen Tianran Intellectual Property Operations Co.,Ltd. |
|
GR01 | Patent grant | ||
GR01 | Patent grant | ||
PE01 | Entry into force of the registration of the contract for pledge of patent right | ||
PE01 | Entry into force of the registration of the contract for pledge of patent right |
Denomination of invention: Modular integrated system and process for treating non fermented soy product production wastewater Granted publication date: 20210226 Pledgee: Bank of Jiangsu Limited by Share Ltd. Hangzhou branch Pledgor: Plant meat (Hangzhou) Health Technology Co.,Ltd. Registration number: Y2024980044992 |