CN110436629A - A sewage total nitrogen removal device and method - Google Patents
A sewage total nitrogen removal device and method Download PDFInfo
- Publication number
- CN110436629A CN110436629A CN201910812877.3A CN201910812877A CN110436629A CN 110436629 A CN110436629 A CN 110436629A CN 201910812877 A CN201910812877 A CN 201910812877A CN 110436629 A CN110436629 A CN 110436629A
- Authority
- CN
- China
- Prior art keywords
- total nitrogen
- oxygen
- section
- mixing section
- sewage
- 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.)
- Pending
Links
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 title claims abstract description 57
- 239000010865 sewage Substances 0.000 title claims abstract description 36
- 229910052757 nitrogen Inorganic materials 0.000 title claims abstract description 28
- 238000000034 method Methods 0.000 title claims abstract description 14
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 31
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 31
- 239000001301 oxygen Substances 0.000 claims abstract description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 238000006243 chemical reaction Methods 0.000 claims description 35
- 229940123973 Oxygen scavenger Drugs 0.000 claims description 18
- 239000007788 liquid Substances 0.000 claims description 11
- 241000894006 Bacteria Species 0.000 claims description 8
- GEHJYWRUCIMESM-UHFFFAOYSA-L sodium sulfite Chemical compound [Na+].[Na+].[O-]S([O-])=O GEHJYWRUCIMESM-UHFFFAOYSA-L 0.000 claims description 8
- 235000010265 sodium sulphite Nutrition 0.000 claims description 4
- 239000002351 wastewater Substances 0.000 claims 3
- 230000008676 import Effects 0.000 claims 2
- OLBVUFHMDRJKTK-UHFFFAOYSA-N [N].[O] Chemical compound [N].[O] OLBVUFHMDRJKTK-UHFFFAOYSA-N 0.000 claims 1
- 238000006396 nitration reaction Methods 0.000 claims 1
- 238000006392 deoxygenation reaction Methods 0.000 abstract description 10
- 238000004062 sedimentation Methods 0.000 abstract description 7
- 239000003795 chemical substances by application Substances 0.000 abstract 1
- 238000010992 reflux Methods 0.000 description 8
- 230000000694 effects Effects 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 2
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 2
- 238000013019 agitation Methods 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 230000001546 nitrifying effect Effects 0.000 description 2
- 229910002651 NO3 Inorganic materials 0.000 description 1
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 description 1
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 230000001651 autotrophic effect Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
Classifications
-
- 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
- C02F3/30—Aerobic and anaerobic processes
-
- 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
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/16—Total nitrogen (tkN-N)
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
技术领域technical field
本发明涉及污水处理领域,尤其涉及一种污水总氮去除装置与方法。The invention relates to the field of sewage treatment, in particular to a sewage total nitrogen removal device and method.
背景技术Background technique
硝化、反硝化反应是去除污水中总氮最方便、节能的处理方法。硝化反应由好氧自养型微生物完成,在有氧状态下,利用无机碳为碳源将NH4 +化成NO2 -,然后再氧化成NO3 -的过程。硝化过程可以分成两个阶段。第一阶段是由亚硝化菌将氨氮转化为亚硝酸盐(NO2 -),第二阶段由硝化菌将亚硝酸盐转化为硝酸盐(NO3 -)。反硝化反应是在缺氧状态下,反硝化菌将亚硝酸盐氮、硝酸盐氮还原成气态氮(N2)的过程。反硝化菌为异养型微生物,多属于兼性细菌,在缺氧状态时,利用硝酸盐中的氧作为电子受体,以有机物(污水中的BOD成分)作为电子供体,提供能量并被氧化稳定。但是,厌氧池中溶解氧浓度对反硝化反应的影响非常大,快速去除厌氧池进水中的溶解氧,有利于反硝化反应的进行,大大提高污水总氮的去除。Nitrification and denitrification are the most convenient and energy-saving treatment methods for removing total nitrogen in sewage. The nitrification reaction is completed by aerobic autotrophic microorganisms. In an aerobic state, inorganic carbon is used as a carbon source to convert NH 4 + into NO 2 - , and then oxidized into NO 3 - . The nitrification process can be divided into two stages. In the first stage, the ammonia nitrogen is converted into nitrite (NO 2 - ) by the nitrifying bacteria, and in the second stage, the nitrite is converted into nitrate (NO 3 - ) by the nitrifying bacteria. Denitrification reaction is a process in which denitrifying bacteria reduce nitrite nitrogen and nitrate nitrogen to gaseous nitrogen (N 2 ) under anoxic conditions. Denitrifying bacteria are heterotrophic microorganisms, most of which belong to facultative bacteria. In anoxic state, they use oxygen in nitrate as electron acceptor and organic matter (BOD components in sewage) as electron donor to provide energy and be Oxidation stable. However, the dissolved oxygen concentration in the anaerobic tank has a great influence on the denitrification reaction, and the rapid removal of dissolved oxygen in the influent water of the anaerobic tank is conducive to the denitrification reaction and greatly improves the removal of total nitrogen in sewage.
发明内容Contents of the invention
本发明提供一种污水总氮去除的装置与方法,通过在厌氧池前端增加除氧反应器,利用除氧剂与厌氧池进水和二沉池回流水中的溶解氧反应,降低厌氧池和缺氧池的溶解氧浓度,提高厌氧池的反硝化能力,从而提高污水中总氮的去除。The invention provides a device and method for removing total nitrogen in sewage. By adding a deoxygenation reactor at the front end of the anaerobic tank, the oxygen scavenger reacts with the dissolved oxygen in the influent water of the anaerobic tank and the return water of the secondary sedimentation tank to reduce the anaerobic concentration. The concentration of dissolved oxygen in the anaerobic pool and the anoxic pool can be improved, and the denitrification capacity of the anaerobic pool can be improved, thereby improving the removal of total nitrogen in the sewage.
本发明采用的技术方案是:The technical scheme adopted in the present invention is:
一种污水总氮去除装置,包括厌氧池、缺氧池、好氧池、二沉池,还包括除氧反应器,所述除氧反应器位于缺氧池前端,具有混合段、反应段和缓冲段,配有污水进口、回流液进口、除氧剂加药口和出水口。A sewage total nitrogen removal device, including anaerobic tank, anoxic tank, aerobic tank, secondary sedimentation tank, also includes a deoxygenation reactor, the deoxygenation reactor is located at the front end of the anoxic tank, has a mixing section, a reaction section And buffer section, equipped with sewage inlet, reflux liquid inlet, oxygen scavenger dosing port and water outlet.
优选的,所述除氧反应器为上部为圆柱形、下部为倒圆台形的中空密闭反应器。Preferably, the oxygen removal reactor is a hollow closed reactor with a cylindrical upper part and an inverted frustum-shaped lower part.
优选的,所述混合段位于所述除氧反应器的内部上端,其上部截面大、下部截面小。Preferably, the mixing section is located at the upper end of the oxygen removal reactor, and its upper section has a large section and its lower section has a small section.
优选的,所述污水进口、和所述回流液进口与所述混合段的顶部相连通,所述除氧剂加药口与混合段的下部相连通。Preferably, the sewage inlet and the reflux inlet are connected to the top of the mixing section, and the oxygen scavenger dosing port is connected to the lower part of the mixing section.
优选的,所述反应段的顶部与所述混合段的底部相连通,所述反应段的底部与所述缓冲段的下部相连通。Preferably, the top of the reaction section communicates with the bottom of the mixing section, and the bottom of the reaction section communicates with the lower part of the buffer section.
优选的,所述缓冲段为所述除氧反应器的剩余空间,所述出水口位于所述缓冲段的上部侧面。Preferably, the buffer section is the remaining space of the oxygen removal reactor, and the water outlet is located on the upper side of the buffer section.
一种污水总氮去除方法,污水进水与二沉池回流液在所述混合段混合均匀,在所述混合段下部与除氧剂接触反应,在所述反应段中充分反应后,液体从所述反应段出口出来受到所述缓冲段底部的冲击,形成水力搅拌,最终溶液通过所述缓冲段上部的所述出水口出来,完成厌氧池进水的除氧过程,厌氧池中溶解氧浓度为0 mg/L ~0.2mg/L,厌氧池中的反硝化细菌在低溶解氧的条件下进行硝化反应去除总氮。A method for removing total nitrogen in sewage. The sewage influent and the reflux liquid of the secondary sedimentation tank are uniformly mixed in the mixing section, and the lower part of the mixing section contacts and reacts with an oxygen scavenger. After fully reacting in the reaction section, the liquid is released from the The outlet of the reaction section is impacted by the bottom of the buffer section to form hydraulic agitation, and finally the solution comes out through the water outlet on the upper part of the buffer section to complete the deoxygenation process of the influent in the anaerobic pool, and dissolve in the anaerobic pool The oxygen concentration is 0 mg/L ~0.2mg/L, and the denitrifying bacteria in the anaerobic tank perform nitrification reaction to remove total nitrogen under the condition of low dissolved oxygen.
优选的,所述除氧剂为亚硫酸钠溶液。Preferably, the oxygen scavenger is sodium sulfite solution.
优选的,所述混合段(2)的停留时间为1 s ~10s,所述反应段(3)的停留时间为0.2s ~2s,所述缓冲段(4)的停留时间为10 s ~60s。Preferably, the residence time of the mixing section (2) is 1 s ~ 10s, the residence time of the reaction section (3) is 0.2s ~ 2s, and the residence time of the buffer section (4) is 10 s ~ 60s .
本发明的有益效果为:The beneficial effects of the present invention are:
1、有研究表明,厌氧池溶解氧在0mg/L~0.2mg/L时反硝化效果最好,但是由于污水厂进水及二沉池回水中溶解氧浓度较高,一般高于1mg/L,严重影响厌氧池的反硝化效果。由于厌氧池的搅拌强度小,若将除氧剂直接投入厌氧池中,则会混合不均匀、反应不充分,本发明通过在进水处安装除氧反应器,可直接使厌氧池进水的溶解氧浓度降低0mg/L~0.2mg/L,提高厌氧池的反硝化效果。1. Some studies have shown that the denitrification effect is the best when the dissolved oxygen in the anaerobic tank is 0mg/L~0.2mg/L. L, seriously affecting the denitrification effect of the anaerobic tank. Due to the low stirring intensity of the anaerobic tank, if the oxygen scavenger is directly put into the anaerobic tank, the mixing will be uneven and the reaction will be insufficient. The present invention can directly make the anaerobic tank The dissolved oxygen concentration of the influent is reduced by 0mg/L~0.2mg/L, which improves the denitrification effect of the anaerobic tank.
2、本发明的除氧反应器分为三段,混合段使污水进水与二沉池回流液均匀混合,并且混合后与除氧剂接触,混合段进口宽、出口窄,除氧剂的加药点接近出口处,水流直接带动除氧剂进入反应段,反应段出口处通过遮挡形成回流,进一步促进除氧剂与水中溶解氧的反应,使反应充分。本发明整个反应流程通过水力完成,不需要外加动力,设计紧凑、小巧、安装使用方便。2. The oxygen removal reactor of the present invention is divided into three sections. The mixing section makes the sewage influent and the return liquid of the secondary sedimentation tank evenly mixed, and after mixing, it contacts with the oxygen scavenger. The inlet of the mixing section is wide and the outlet is narrow. The dosing point is close to the outlet, and the water flow directly drives the oxygen scavenger into the reaction section, and the outlet of the reaction section is blocked to form a backflow, which further promotes the reaction between the oxygen scavenger and the dissolved oxygen in the water, so that the reaction is sufficient. The entire reaction process of the present invention is completed by hydraulic power without external power, compact and small in design, and convenient to install and use.
附图说明Description of drawings
为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动性的前提下,还可以根据这些附图获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. For those skilled in the art, other drawings can also be obtained according to these drawings without any creative effort.
图1为本发明一种污水总氮去除装置与方法的流程图。Fig. 1 is a flowchart of a sewage total nitrogen removal device and method of the present invention.
图2为本发明一种污水总氮去除装置的截面图。Fig. 2 is a cross-sectional view of a sewage total nitrogen removal device according to the present invention.
图3为本发明一种污水总氮去除装置的主视图。Fig. 3 is a front view of a sewage total nitrogen removal device according to the present invention.
图4为本发明一种污水总氮去除装置的左视图。Fig. 4 is a left view of a sewage total nitrogen removal device according to the present invention.
图中:1-除氧反应器;2-混合段;3-反应段;4-缓冲段;5-污水进口;6-回流液进口;7-除氧剂加药口;8-出水口。In the figure: 1-deoxygenation reactor; 2-mixing section; 3-reaction section; 4-buffer section; 5-sewage inlet; 6-reflux liquid inlet;
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有作出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only some, not all, embodiments of the present invention. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without creative efforts fall within the protection scope of the present invention.
本发明采用的技术方案是:The technical scheme adopted in the present invention is:
一种污水总氮去除装置,包括厌氧池、缺氧池、好氧池、二沉池,还包括除氧反应器1,所述除氧反应器1位于缺氧池前端,具有混合段2、反应段3和缓冲段4,配有污水进口5、回流液进口6、除氧剂加药口7和出水口8。A sewage total nitrogen removal device, including anaerobic tank, anoxic tank, aerobic tank, secondary sedimentation tank, and also includes a deoxygenation reactor 1, the deoxygenation reactor 1 is located at the front end of the anoxic tank, and has a mixing section 2 , The reaction section 3 and the buffer section 4 are equipped with a sewage inlet 5, a reflux liquid inlet 6, an oxygen scavenger dosing port 7 and a water outlet 8.
优选的,所述除氧反应器1为上部为圆柱形、下部为倒圆台形的中空密闭反应器。Preferably, the oxygen removal reactor 1 is a hollow closed reactor with a cylindrical upper part and a frustoconical lower part.
优选的,所述混合段2位于所述除氧反应器1的内部上端,其上部截面大、下部截面小。Preferably, the mixing section 2 is located at the inner upper end of the oxygen removal reactor 1, and its upper part has a large cross-section and its lower part has a small cross-section.
优选的,所述污水进口5、和所述回流液进口与所述混合段2的顶部相连通,所述除氧剂加药口7与混合段的下部相连通。Preferably, the sewage inlet 5 and the reflux inlet are connected to the top of the mixing section 2, and the oxygen scavenger dosing port 7 is connected to the lower part of the mixing section.
优选的,所述反应段3的顶部与所述混合段2的底部相连通,所述反应段3的底部与所述缓冲段4的下部相连通。Preferably, the top of the reaction section 3 communicates with the bottom of the mixing section 2 , and the bottom of the reaction section 3 communicates with the lower part of the buffer section 4 .
优选的,所述缓冲段4为所述除氧反应器1的剩余空间,所述出水口8位于所述缓冲段4的上部侧面。Preferably, the buffer section 4 is the remaining space of the deaeration reactor 1 , and the water outlet 8 is located on the upper side of the buffer section 4 .
一种污水总氮去除方法,污水进水与二沉池回流液在所述混合段2混合均匀,在所述混合段2下部与除氧剂接触反应,在所述反应段3中充分反应后,液体从所述反应段3出口出来受到所述缓冲段4底部的冲击,形成水力搅拌,最终溶液通过所述缓冲段4上部的所述出水口8出来,完成厌氧池进水的除氧过程,厌氧池中溶解氧浓度为0 mg/L ~0.2mg/L,厌氧池中的反硝化细菌在低溶解氧的条件下进行硝化反应去除总氮。A method for removing total nitrogen in sewage. The sewage influent and the reflux liquid of the secondary sedimentation tank are uniformly mixed in the mixing section 2, and the lower part of the mixing section 2 is contacted and reacted with an oxygen scavenger. After fully reacting in the reaction section 3 , the liquid comes out from the outlet of the reaction section 3 and is impacted by the bottom of the buffer section 4 to form hydraulic agitation, and finally the solution comes out through the water outlet 8 on the upper part of the buffer section 4 to complete the deoxygenation of the influent of the anaerobic tank In the process, the dissolved oxygen concentration in the anaerobic tank is 0 mg/L ~0.2mg/L, and the denitrifying bacteria in the anaerobic tank perform nitrification reaction to remove total nitrogen under the condition of low dissolved oxygen.
优选的,所述除氧剂为亚硫酸钠溶液。Preferably, the oxygen scavenger is sodium sulfite solution.
优选的,所述混合段(2)的停留时间为1 s ~10s,所述反应段(3)的停留时间为0.2s ~2s,所述缓冲段(4)的停留时间为10s ~60s。Preferably, the residence time of the mixing section (2) is 1 s to 10s, the residence time of the reaction section (3) is 0.2s to 2s, and the residence time of the buffer section (4) is 10s to 60s.
实施例Example
污水总氮去除装置,上部为圆柱形、下部为倒圆台形的中空密闭反应器,反应器顶部截面内径为50cm,混合段底部截面内径为10cm、高20cm;反应段为圆柱形,高35cm;反应段底部距离反应器底部15cm,反应器其余空间为缓冲段。进水流量为50m3/d,溶解氧浓度为1.5mg/L,回流液流量为100 m3/d,溶解氧浓度为1.8mg/L,除氧剂为30%的亚硫酸钠溶液,流量为270ml/h,混合段停留时间为7.5s,反应段停留时间为1.6s,缓冲段停留时间为55s,出水溶解氧浓度小于0.2 mg/L。Sewage total nitrogen removal device, the upper part is cylindrical and the lower part is a hollow closed reactor with inverted round table shape. The inner diameter of the top section of the reactor is 50cm, the inner diameter of the bottom section of the mixing section is 10cm, and the height is 20cm; the reaction section is cylindrical and the height is 35cm; The bottom of the reaction section is 15cm away from the bottom of the reactor, and the remaining space in the reactor is a buffer section. The influent flow rate is 50m 3 /d, the dissolved oxygen concentration is 1.5mg/L, the reflux liquid flow rate is 100 m 3 /d, the dissolved oxygen concentration is 1.8mg/L, the oxygen scavenger is 30% sodium sulfite solution, and the flow rate is 270ml /h, the residence time in the mixing section is 7.5s, the residence time in the reaction section is 1.6s, the residence time in the buffer section is 55s, and the dissolved oxygen concentration in the effluent is less than 0.2 mg/L.
Claims (9)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910812877.3A CN110436629A (en) | 2019-08-30 | 2019-08-30 | A sewage total nitrogen removal device and method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910812877.3A CN110436629A (en) | 2019-08-30 | 2019-08-30 | A sewage total nitrogen removal device and method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN110436629A true CN110436629A (en) | 2019-11-12 |
Family
ID=68438459
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910812877.3A Pending CN110436629A (en) | 2019-08-30 | 2019-08-30 | A sewage total nitrogen removal device and method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110436629A (en) |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5120442A (en) * | 1987-02-07 | 1992-06-09 | Dr. Karl Thomae Gmbh | Process for the simultaneous chemical and biological elimination of solid and liquid organic waste |
CN2759585Y (en) * | 2004-10-29 | 2006-02-22 | 中国石油化工股份有限公司 | Gases blending apparatus between reactor sections |
CN101353189A (en) * | 2008-09-19 | 2009-01-28 | 新疆时代石油工程有限公司 | Single cyclone coagulation reactor and oil-contaminated water processing method |
CN103769007A (en) * | 2012-10-19 | 2014-05-07 | 中国石油化工股份有限公司 | Fluidized bed reactor |
CN106219904A (en) * | 2016-09-14 | 2016-12-14 | 清华大学 | A kind of denitrification dephosphorization system for the treatment of of Power Industrial Recirculating Cooling Water |
CN207792814U (en) * | 2018-01-18 | 2018-08-31 | 尚川(北京)水务有限公司 | A kind of denitrification dephosphorization system |
CN210764575U (en) * | 2019-08-30 | 2020-06-16 | 天津壹新环保工程有限公司 | Sewage total nitrogen removing device |
-
2019
- 2019-08-30 CN CN201910812877.3A patent/CN110436629A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5120442A (en) * | 1987-02-07 | 1992-06-09 | Dr. Karl Thomae Gmbh | Process for the simultaneous chemical and biological elimination of solid and liquid organic waste |
CN2759585Y (en) * | 2004-10-29 | 2006-02-22 | 中国石油化工股份有限公司 | Gases blending apparatus between reactor sections |
CN101353189A (en) * | 2008-09-19 | 2009-01-28 | 新疆时代石油工程有限公司 | Single cyclone coagulation reactor and oil-contaminated water processing method |
CN103769007A (en) * | 2012-10-19 | 2014-05-07 | 中国石油化工股份有限公司 | Fluidized bed reactor |
CN106219904A (en) * | 2016-09-14 | 2016-12-14 | 清华大学 | A kind of denitrification dephosphorization system for the treatment of of Power Industrial Recirculating Cooling Water |
CN207792814U (en) * | 2018-01-18 | 2018-08-31 | 尚川(北京)水务有限公司 | A kind of denitrification dephosphorization system |
CN210764575U (en) * | 2019-08-30 | 2020-06-16 | 天津壹新环保工程有限公司 | Sewage total nitrogen removing device |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106830324B (en) | A device and method for enhancing biological denitrification and phosphorus removal by staged influent A2/O process | |
CN100395196C (en) | Improved MUCT process and device | |
CN112456643A (en) | System and method for realizing partial anaerobic ammonia oxidation deep nitrogen and phosphorus removal by circulating and alternately utilizing main flow and side flow zone biomembrane of urban sewage treatment plant | |
CN101357806B (en) | Nitrosation-ANAMMOX treatment method and equipment for livestock breeding wastewater | |
CN100395197C (en) | Improved UCT process and device | |
CN113200600B (en) | Device and method for treating high-ammonia-nitrogen organic matter wastewater by semi-shortcut nitrification anaerobic ammonia oxidation and serial shortcut denitrification anaerobic ammonia oxidation | |
CN103588299B (en) | A kind of integrated short-cut nitrification and denitrification biological denitrification reactor | |
CN101062807A (en) | Intensified anti-nitrated phosphorous-removal sequencing batch membrane bioreactor technique | |
JP2020524076A (en) | Method to upgrade and expand capacity of activated sludge process by biological treatment process of sewage based on functional floating carrier | |
CN113024032B (en) | A short-range nitrification and denitrification coupled with anammox-MBR-sulfur autotrophic denitrification and denitrification process and system | |
CN105461174A (en) | Method for removing high ammonia nitrogen from pig farm dry manure cleaning livestock wastewater | |
CN104071949B (en) | Integrated hybrid biomembrane-activated sludge reaction system and application method thereof | |
CN106277326A (en) | A kind of aerobic-anaerobic integration granular sludge reactor and the method processing waste water thereof | |
CN111960532A (en) | Method and reaction device for biological denitrification of sewage based on sulfur autotrophic short-range denitrification | |
CN103979750A (en) | Reactor for sewage treatment and phosphorus recovery and method for recovering phosphorus by using same | |
CN103214150A (en) | Complete self-backflow well type anabroeic-anoxic-oxic (AAO) sewage treatment method | |
CN202729946U (en) | Two-stage anoxic/oxic (A/O)-membrane biological reactor (MBR) nitrogen and phosphorus removal device | |
CN106673193A (en) | Method of Anaerobic Fermentation Coupling A2/O-Biological Contact Oxidation to Treat Low C/N Sewage | |
CN215855353U (en) | Biological carbon and nitrogen removal integrated reactor for treating organic nitrogen wastewater | |
CN200940110Y (en) | Device for short-cut nitrification by improving MUCT process | |
CN113697954B (en) | Device and method for realizing short-range denitrification phosphorus removal coupled with anaerobic ammonium oxidation deep nitrogen removal through side stream reactor | |
CN211664789U (en) | Advanced treatment device for town sewage based on improved denitrification filter column | |
JP3656426B2 (en) | Biological treatment of ammoniacal nitrogen | |
CN107129037A (en) | It is quick to start the method that Anammox coupling denitrification cooperates with denitrification reactor | |
CN106145337A (en) | An improved DEAMOX continuous flow process device and method for treating high-concentration NO3‑‑N wastewater and urban sewage |
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 | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20191112 |