CN104609558B - A kind of short-cut nitrification and denitrification integrated A BR reactor - Google Patents
A kind of short-cut nitrification and denitrification integrated A BR reactor Download PDFInfo
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- 238000006243 chemical reaction Methods 0.000 claims abstract description 103
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 87
- 238000005273 aeration Methods 0.000 claims abstract description 21
- 239000000945 filler Substances 0.000 claims abstract description 18
- 238000009423 ventilation Methods 0.000 claims abstract description 9
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 claims abstract description 7
- 238000011144 upstream manufacturing Methods 0.000 claims abstract description 7
- 239000002351 wastewater Substances 0.000 claims description 9
- 239000001301 oxygen Substances 0.000 claims description 6
- 229910052760 oxygen Inorganic materials 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 5
- 229920005570 flexible polymer Polymers 0.000 claims description 4
- 238000005192 partition Methods 0.000 claims description 4
- 238000012856 packing Methods 0.000 claims description 2
- 210000003437 trachea Anatomy 0.000 claims description 2
- 239000010802 sludge Substances 0.000 abstract description 11
- 239000010865 sewage Substances 0.000 abstract description 4
- 238000000034 method Methods 0.000 description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 5
- 229910052799 carbon Inorganic materials 0.000 description 5
- 230000008569 process Effects 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 4
- 210000004027 cell Anatomy 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 2
- 210000005056 cell body Anatomy 0.000 description 2
- 230000007812 deficiency Effects 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000010992 reflux Methods 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000002253 acid Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000002779 inactivation Effects 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
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- 238000011160 research Methods 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/302—Nitrification and denitrification treatment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/301—Aerobic and anaerobic treatment in the same reactor
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
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Abstract
本发明公开了一种短程硝化反硝化一体化ABR反应器,包括池体(1)、主进水管(2)、第一分进水管(3)、第二分进水管(5)、沼气集气管(8)、微孔曝气管(9)、通气管(10)、回流管(11)和出水管(14),所述池体(1)内部从第一分进水管(3)向出水管(14)方向依次为一级厌氧区、微曝短程硝化区和二级厌氧区,所述微曝短程硝化区的反应室底部均设有微孔曝气管(9),每个所述反应室的上流区均设有填料(17)。本发明既可高效反硝化脱氮,又能去除COD,且可有效解决污泥流失的问题,特别适合于处理高负荷高氨氮污水。
The invention discloses an integrated ABR reactor for short-range nitrification and denitrification, which comprises a tank body (1), a main water inlet pipe (2), a first sub-water inlet pipe (3), a second sub-water inlet pipe (5), a biogas collecting Air pipe (8), microporous aeration pipe (9), ventilation pipe (10), return pipe (11) and water outlet pipe (14), described pool body (1) inside is from the first sub-inlet pipe (3) to The direction of the water outlet pipe (14) is successively the primary anaerobic zone, the micro-exposure short-range nitrification zone and the secondary anaerobic zone. The bottom of the reaction chamber of the micro-exposure short-range nitrification zone is equipped with microporous aeration pipes (9), each The upstream regions of each of the reaction chambers are provided with fillers (17). The invention can not only efficiently denitrify and denitrify, but also remove COD, and can effectively solve the problem of sludge loss, and is especially suitable for treating sewage with high load and high ammonia nitrogen.
Description
技术领域technical field
本发明涉及一种短程硝化反硝化一体化ABR反应器,属于污水处理技术领域。The invention relates to a short-range nitrification and denitrification integrated ABR reactor, which belongs to the technical field of sewage treatment.
背景技术Background technique
传统的脱氮工艺是先在硝化过程,将NH4 +氧化成NO2 -,再氧化成NO3 -,然后经过反硝化过程,先将NO3 -反硝化为NO2 -,再反硝化为N2。短程硝化反硝化技术,则是将硝化过程控制在NO2 -阶段,阻止NO2 -进一步氧化为NO3 -,即先将NH4 +氧化成NO2 -,然后直接由NO2 -反硝化为N2。短程硝化反硝化技术与传统脱氮工艺相比,具有降低能耗、节省碳源、污泥产量少、占地面积少等特点,对于含氮较高和碳源不足的废水具有很大的应用价值。The traditional denitrification process is to oxidize NH 4 + into NO 2 - , then into NO 3 - in the nitrification process, and then through the denitrification process, denitrify NO 3 - into NO 2 - , and then denitrify into NO 2 - N 2 . The short-range nitrification and denitrification technology is to control the nitrification process in the NO 2 - stage and prevent the further oxidation of NO 2 - to NO 3 - , that is, to oxidize NH 4 + to NO 2 - first, and then directly denitrify from NO 2 - to N 2 . Compared with the traditional denitrification process, the short-cut nitrification and denitrification technology has the characteristics of reducing energy consumption, saving carbon sources, less sludge production, and less land occupation. It has great applications for wastewater with high nitrogen content and insufficient carbon sources. value.
当前的短程硝化反硝化反应器,大多集中在SBR反应器的研究中。由于SBR反应器是序批式反应器,具备好氧、厌氧、缺氧阶段的时间分隔阶段,空间上又具备完全混合阶段,因此比较适合短程硝化反硝化技术。但SBR的序批式特点,也造成了处理装置空置率高、投资高、自动化要求程度高等不足。另有一些反应器通过CSTR(完全混合搅拌式反应器)作为单独的短程硝化反应器,与后置的A/O或其他厌氧反应器连接,也有很好的效果。但是在污水COD浓度较高时,需要设置前置的厌氧反应器先行处理COD,该类技术仍有装置复杂、水力参数不易匹配控制等不足。Most of the current short-range nitrification and denitrification reactors focus on the research of SBR reactors. Since the SBR reactor is a sequencing batch reactor, it has a time-separated stage of aerobic, anaerobic, and anoxic stages, and a complete mixing stage in space, so it is more suitable for short-range nitrification and denitrification technology. However, the batch-type characteristics of SBR have also caused the shortcomings of high vacancy rate of processing equipment, high investment, and high degree of automation requirements. Some other reactors use CSTR (Completely Mixed Stirring Reactor) as a separate short-path nitrification reactor, which is connected to the rear A/O or other anaerobic reactors, which also has good results. However, when the concentration of COD in sewage is high, it is necessary to set up a pre-anaerobic reactor to treat COD first. This type of technology still has shortcomings such as complex equipment and difficult matching and control of hydraulic parameters.
ABR反应器(Anaerobic Baffled Reactor,厌氧折流板反应器)是上世纪80年代由P.LMcCarty提出的一种新型高效厌氧反应器,被称为第三代厌氧反应器。其特点是在反应器内部设置一系列垂直放置的折流板,将反应器分隔为多个串联在一起的反应室,每一个反应室都可以看作是一个独立的UASB(上流式厌氧污泥床)。由于在每个反应室内设置了折流板,使得在水流方向上形成了依次独立的格室,这样就实现了不同的微生物种群生长在不同格室内这一目的,从而实现了产酸相和产甲烷相的分离,使反应器具有较高的处理效率和较强的抗冲击能力。同时,由于ABR具有格室单独分开、不易受影响、各格室水力停留时间可自行设定、整体结构简单等优点,若将其中某些格室设置为微氧短程硝化室,不会对其余厌氧格室造成影响,亚硝化后的出水流至厌氧格室,即可进行有效的反硝化脱氮。因此,ABR反应器具备短程硝化反硝化所需的技术结构要求。ABR reactor (Anaerobic Baffled Reactor, anaerobic baffled reactor) is a new type of high-efficiency anaerobic reactor proposed by P.LMcCarty in the 1980s, known as the third-generation anaerobic reactor. Its characteristic is that a series of vertically placed baffles are set inside the reactor to divide the reactor into multiple reaction chambers connected in series, and each reaction chamber can be regarded as an independent UASB (upflow anaerobic sewage mud bed). Since the baffles are set in each reaction chamber, independent compartments are formed sequentially in the direction of water flow, so that the purpose of different microbial populations growing in different compartments is realized, thereby realizing the acid-producing phase and the production phase. The separation of the methane phase enables the reactor to have higher processing efficiency and stronger impact resistance. At the same time, because ABR has the advantages of separate compartments, not easily affected, the hydraulic retention time of each compartment can be set independently, and the overall structure is simple, if some of the compartments are set as micro-oxygen short-range nitrification chambers, it will not affect the rest The anaerobic cell is affected, and the effluent after nitrification flows to the anaerobic cell to carry out effective denitrification and denitrification. Therefore, the ABR reactor has the technical structure requirements required for short-cut nitrification and denitrification.
但是,传统的ABR反应器也存在着一些不足,比如在流速较快时,由于水流和产气两个同一方向上的力存在于上流室中,易造成格室内的污泥流失,而污泥流失会破坏各格室本应固定的菌群和环境,造成反应器处理效率的降低,严重时甚至会造成反应器内部菌群失活。而如果流速较慢,则污泥流失会得到一定的遏制,但是会使反应器下层的污泥搅动变得困难,从而死区加大,反应器的处理效率会受到影响。同时,如果进水的COD浓度较高(约高于10000mg/L)时,产生的沼气扰动剧烈,也容易使污泥流失。因此,需要提供一种既可有效实现短程硝化反硝化,又可有效减少污泥流失的一体化ABR反应器。However, the traditional ABR reactor also has some deficiencies. For example, when the flow rate is fast, because the force of the water flow and the gas production in the same direction exist in the upper chamber, it is easy to cause the sludge in the cell to be lost, and the sludge The loss will destroy the bacteria and environment that should be fixed in each compartment, resulting in a reduction in the treatment efficiency of the reactor, and even inactivation of the bacteria in the reactor in severe cases. And if the flow rate is slow, the sludge loss will be contained to a certain extent, but it will make it difficult to stir the sludge in the lower layer of the reactor, so that the dead zone will increase, and the treatment efficiency of the reactor will be affected. At the same time, if the COD concentration of the influent is high (about 10,000 mg/L), the generated biogas will be violently disturbed, and the sludge will be easily lost. Therefore, it is necessary to provide an integrated ABR reactor that can effectively realize short-cut nitrification and denitrification and effectively reduce sludge loss.
发明内容Contents of the invention
本发明的目的是弥补现有技术的不足,提供一种短程硝化反硝化一体化ABR反应器,本发明既能有效实现短程硝化反硝化,又可有效减少污泥流失。The purpose of the present invention is to make up for the deficiencies of the prior art and provide an integrated ABR reactor for short-range nitrification and denitrification. The invention can not only effectively realize short-range nitrification and denitrification, but also effectively reduce sludge loss.
本发明解决上述技术问题的技术方案如下:一种短程硝化反硝化一体化ABR反应器,包括池体、主进水管、第一分进水管、第二分进水管、沼气集气管、微孔曝气管、通气管、回流管和出水管,所述主进水管与废水进水口连接,所述第一分进水管和第二分进水管均与主进水管相连,所述池体内部相间设有多个垂直于池体底部的隔板,将所述池体内部分隔为多个串联且相互独立的反应室,所述每个反应室内部均有一从上至下的折流板将其分隔为下流区和上流区,所述池体的第一反应室的上部设有进水槽,并与第一分进水管相连,最后一个反应室的上部设有出水槽,并与出水管相连,其特征在于,所述池体内部从第一分进水管向出水管方向依次为一级厌氧区、微曝短程硝化区和二级厌氧区,所述一级厌氧区包括≥3个的反应室,所述微曝短程硝化区包括1~2个的反应室,所述二级厌氧区包括≥2个的反应室,所述微曝短程硝化区的反应室底部均设有微孔曝气管,所述微曝短程硝化区的反应室的上部和一级厌氧区的反应室的下部之间设有回流管,每个所述反应室的上流区均设有填料,每个所述一级厌氧区和所述二级厌氧区的反应室的顶部均设有沼气集气管,每个所述微曝短程硝化区的反应室的顶部均设有通气管,所述第二分进水管的出水口设在所述二级厌氧区的第一个反应室的折流板的下方。The technical scheme of the present invention to solve the above-mentioned technical problems is as follows: a short-range nitrification and denitrification integrated ABR reactor, including a tank body, a main water inlet pipe, a first sub-water inlet pipe, a second sub-water inlet pipe, a biogas collecting pipe, a microporous aeration Trachea, ventilation pipe, return pipe and water outlet pipe, the main water inlet pipe is connected to the waste water inlet, the first sub-water inlet pipe and the second sub-water inlet pipe are connected to the main water inlet pipe, and the interior of the pool body is arranged alternately There are a plurality of partitions perpendicular to the bottom of the cell body, which divide the interior of the cell body into a plurality of series and independent reaction chambers, and each reaction chamber has a baffle plate from top to bottom to separate it It is a downflow area and an upflow area. The upper part of the first reaction chamber of the pool body is provided with a water inlet tank, which is connected with the first water inlet pipe, and the upper part of the last reaction chamber is provided with a water outlet tank, which is connected with the water outlet pipe. It is characterized in that, from the first water inlet pipe to the water outlet pipe inside the pool body, there are first-level anaerobic zone, micro-exposure short-range nitrification zone and second-level anaerobic zone, and the first-level anaerobic zone includes ≥ 3 Reaction chamber, the micro-exposure short-range nitrification zone includes 1 to 2 reaction chambers, the secondary anaerobic zone includes ≥ 2 reaction chambers, and the bottom of the reaction chamber in the micro-exposure short-range nitrification zone is equipped with micropores An aeration pipe, a return pipe is provided between the upper part of the reaction chamber of the micro-exposure short-range nitrification zone and the lower part of the reaction chamber of the first-stage anaerobic zone, and the upstream area of each of the reaction chambers is provided with fillers, each The tops of the reaction chambers of the primary anaerobic zone and the secondary anaerobic zone are provided with biogas headers, and the tops of the reaction chambers of each micro-exposure short-path nitrification zone are provided with ventilation pipes. The water outlet of the two-point water inlet pipe is arranged below the baffle plate of the first reaction chamber of the secondary anaerobic zone.
在上述技术方案的基础上,本发明还可以做如下改进。On the basis of the above technical solutions, the present invention can also be improved as follows.
进一步,所述池体为长方体。Further, the pool body is a cuboid.
进一步,所述折流板的折角为45°。Further, the folding angle of the baffle is 45°.
进一步,当进水COD为2000~5000mg/L,氨氮为50~200mg/L时,所述一级厌氧区包括3个反应室,所述微曝短程硝化区包括1个反应室,所述二级厌氧区包括为2个反应室。Further, when the influent COD is 2000-5000 mg/L and ammonia nitrogen is 50-200 mg/L, the primary anaerobic zone includes 3 reaction chambers, the micro-exposure short-range nitrification zone includes 1 reaction chamber, and the The secondary anaerobic zone consists of 2 reaction chambers.
进一步,当进水COD为5000~10000mg/L,氨氮为200~800mg/L时,所述一级厌氧区包括4个反应室,所述微曝短程硝化区包括2个反应室,所述二级厌氧区包括2个反应室。Further, when the influent COD is 5000-10000 mg/L and ammonia nitrogen is 200-800 mg/L, the primary anaerobic zone includes 4 reaction chambers, and the micro-exposure short-path nitrification zone includes 2 reaction chambers, the The secondary anaerobic zone includes 2 reaction chambers.
进一步,所述填料底部距所述折流板底部≥20cm,所述填料顶部距水面≤30cm。Further, the distance between the bottom of the filler and the bottom of the baffle is ≥ 20 cm, and the distance between the top of the filler and the water surface is ≤ 30 cm.
进一步,所述填料为悬挂式柔性高分子填料。Further, the filler is a suspended flexible polymer filler.
进一步,所述填料是为了微生物附着生长。Further, the filler is for the attachment and growth of microorganisms.
进一步,所述微孔曝气管的内径为6~12mm,所述微孔曝气管距池体底部的距离≤10cm,≥5cm。Further, the inner diameter of the microporous aeration tube is 6-12 mm, and the distance between the microporous aeration tube and the bottom of the pool body is ≤10 cm, ≥5 cm.
进一步,所述微孔曝气管与鼓风机连接。Further, the microporous aeration pipe is connected with a blower.
进一步,每个所述微曝短程硝化区的反应室内溶解氧的浓度为0.5~1.0mg/L。Further, the concentration of dissolved oxygen in the reaction chamber of each micro-exposure short-range nitrification zone is 0.5-1.0 mg/L.
进一步,当所述微曝短程硝化区的反应室为1个时,所述回流管设有一根,设置在微曝短程硝化区的第一个反应室的上部和一级厌氧区的第二个反应室的下部之间。Further, when there is one reaction chamber in the micro-exposure short-range nitrification zone, the return pipe is provided with one, which is arranged on the upper part of the first reaction chamber of the micro-exposure short-range nitrification zone and the second one of the primary anaerobic zone. between the lower parts of the reaction chambers.
进一步,当所述微曝短程硝化区的反应室为2个时,所述回流管设有两根,其中一根设置在微曝短程硝化区的第一个反应室的上部和一级厌氧区的第二个反应室的下部之间,另一根设置在微曝短程硝化区的第二个反应室的上部和一级厌氧区的第一个反应室的下部之间。Further, when there are two reaction chambers in the micro-exposure short-range nitrification zone, two return pipes are provided, one of which is arranged on the upper part of the first reaction chamber in the micro-exposure short-range nitrification zone and the first-stage anaerobic Between the lower part of the second reaction chamber of the micro-exposure short-path nitrification zone and the lower part of the first reaction chamber of the primary anaerobic zone.
进一步,所述回流管的进水口设置在所述微曝短程硝化区的反应室的上部。Further, the water inlet of the return pipe is arranged at the upper part of the reaction chamber of the micro-exposure short-path nitrification zone.
进一步,所述回流管的出水口设置在所述一级厌氧区的反应室的下部。Further, the water outlet of the return pipe is set at the lower part of the reaction chamber of the primary anaerobic zone.
进一步,所述回流管上设有回流泵,所述回流泵用于为进入回流管的回流水提供动力。Further, a return pump is provided on the return pipe, and the return pump is used to provide power for the return water entering the return pipe.
进一步,所述回流管上设有回流阀,所述回流阀用于调节从微曝短程硝化区回流到第一厌氧区的回流水的回流比例。Further, the return pipe is provided with a return valve, and the return valve is used to adjust the return ratio of return water flowing back from the micro-exposure short-path nitrification area to the first anaerobic area.
进一步,所述回流比例为20~50%。Further, the reflux ratio is 20-50%.
进一步,所述通气管是为了排放鼓风曝气时所产生的气体。Further, the ventilation pipe is used to discharge the gas generated during blast aeration.
进一步,所述第二分进水管上设有分流阀,所述分流阀用于调节从主进水管分流到第二分进水管的废水分流比例。Further, a diverter valve is provided on the second water inlet pipe, and the diverter valve is used to adjust the ratio of the waste water diverted from the main water inlet pipe to the second water inlet pipe.
进一步,所述分流比例为≤主进水管进水总量的20%。Further, the diversion ratio is ≤20% of the total water intake of the main water inlet pipe.
进一步,当进水COD<3000mg/L,则开启所述分流阀,可以提高二级厌氧区的COD,增加碳源,以提高后续反硝化的效果。Further, when the influent COD<3000mg/L, the diverter valve is opened, which can increase the COD in the secondary anaerobic zone, increase the carbon source, and improve the effect of subsequent denitrification.
本发明的有益效果是:The beneficial effects of the present invention are:
1、本发明将传统的ABR反应器中段的1~2个反应室作为微曝短程硝化室,产生的高浓度NO2 -出水,一部分流入二级厌氧区进行反硝化,一部分回流至一级厌氧区,可以稳定进水水质,达到既可高效反硝化脱氮,又能去除COD的目的。1. In the present invention, one to two reaction chambers in the middle section of the traditional ABR reactor are used as micro-exposure short-range nitrification chambers, and part of the high-concentration NO 2 - effluent flows into the secondary anaerobic zone for denitrification, and part of it flows back to the primary stage The anaerobic zone can stabilize the quality of influent water, achieve the purpose of efficient denitrification and denitrification, and COD removal.
2、本发明的各反应室的上流区均设有悬挂式柔性高分子填料,可减少反应室死区,有效解决污泥流失的问题,可增加污泥含量,增加ABR反应器的有机负荷。2. The upstream area of each reaction chamber of the present invention is equipped with suspended flexible polymer fillers, which can reduce the dead area of the reaction chamber, effectively solve the problem of sludge loss, increase the sludge content, and increase the organic load of the ABR reactor.
3、本发明在进水COD<3000mg/L时,开启分流阀,让一部分废水直接进入到二级厌氧区,这样可以提高二级厌氧区的COD,增加碳源,以提高后续反硝化的效果。3. In the present invention, when the influent COD is less than 3000mg/L, the diverter valve is opened to let a part of the wastewater directly enter the secondary anaerobic zone, which can increase the COD of the secondary anaerobic zone, increase the carbon source, and improve subsequent denitrification Effect.
4、本发明结构简单,投资成本低,可有效实现高COD、高氨氮废水的COD降解和脱氮处理,特别适合于处理高负荷高氨氮污水。4. The invention has simple structure and low investment cost, can effectively realize COD degradation and denitrification treatment of high-COD and high-ammonia-nitrogen wastewater, and is especially suitable for treating high-load and high-ammonia-nitrogen wastewater.
附图说明Description of drawings
图1为本发明的立面图。Fig. 1 is the elevation view of the present invention.
图2为本发明的平面图。Figure 2 is a plan view of the present invention.
附图中,各标号所代表的部件列表如下:In the accompanying drawings, the list of parts represented by each label is as follows:
1、池体,2、主进水管,3、第一分进水管,4、进水槽,5、第二分进水管,6、隔板,7、折流板,8、沼气集气管,9、微孔曝气管,10、通气管,11、回流管,12、回流管进水口,13、回流管出水口,14、出水管,15、出水槽,16、第二分进水管出水口,17、填料,18、回流泵,19、回流阀,20、分流阀。1. Tank body, 2. Main water inlet pipe, 3. First water inlet pipe, 4. Water inlet tank, 5. Second water inlet pipe, 6. Partition plate, 7. Baffle plate, 8. Biogas collecting pipe, 9 , microporous aeration pipe, 10, ventilation pipe, 11, return pipe, 12, water inlet of return pipe, 13, water outlet of return pipe, 14, water outlet pipe, 15, water outlet tank, 16, water outlet of second water inlet pipe , 17, packing, 18, return pump, 19, return valve, 20, diverter valve.
具体实施方式detailed description
以下结合附图对本发明的原理和特征进行描述,所举实例只用于解释本发明,并非用于限定本发明的范围。The principles and features of the present invention are described below in conjunction with the accompanying drawings, and the examples given are only used to explain the present invention, and are not intended to limit the scope of the present invention.
如图1和图2所示,一种短程硝化反硝化一体化ABR反应器,包括池体1、主进水管2、第一分进水管3、第二分进水管5、沼气集气管8、微孔曝气管9、通气管10、回流管11和出水管14,所述主进水管2与废水进水口连接,所述第一分进水管3和第二分进水管5均与主进水管2相连,所述池体1内部相间设有多个垂直于池体1底部的隔板6,将所述池体1内部分隔为多个串联且相互独立的反应室,所述每个反应室内部均有一从上至下的折流板7将其分隔为下流区和上流区,所述池体1的第一反应室的上部设有进水槽4,并与第一分进水管3相连,最后一个反应室的上部设有出水槽15,并与出水管14相连,其特征在于,所述池体1内部从第一分进水管3向出水管14方向依次为一级厌氧区、微曝短程硝化区和二级厌氧区,所述一级厌氧区包括≥3个的反应室,所述微曝短程硝化区包括1~2个的反应室,所述二级厌氧区包括≥2个的反应室,所述微曝短程硝化区的反应室底部均设有微孔曝气管9,所述微曝短程硝化区的反应室的上部和一级厌氧区的反应室的下部之间设有回流管11,每个所述反应室的上流区均设有填料17,每个所述一级厌氧区和所述二级厌氧区的反应室的顶部均设有沼气集气管8,每个所述微曝短程硝化区的反应室的顶部均设有通气管10,所述第二分进水管5的出水口16设在所述二级厌氧区的第一个反应室的折流板7的下方。As shown in Figure 1 and Figure 2, a short-range nitrification and denitrification integrated ABR reactor includes a tank body 1, a main water inlet pipe 2, a first water inlet pipe 3, a second water inlet pipe 5, a biogas collecting pipe 8, Microporous aeration pipe 9, ventilation pipe 10, return pipe 11 and water outlet pipe 14, the main water inlet pipe 2 is connected with the waste water inlet, and the first water inlet pipe 3 and the second water inlet pipe 5 are connected with the main water inlet pipe. The water pipes 2 are connected, and the interior of the pool body 1 is provided with a plurality of partitions 6 perpendicular to the bottom of the pool body 1, which divides the interior of the pool body 1 into a plurality of reaction chambers connected in series and independent of each other. There is a baffle plate 7 from top to bottom inside the chamber to divide it into a downstream area and an upstream area. The upper part of the first reaction chamber of the pool body 1 is provided with a water inlet tank 4, which is connected to the first water inlet pipe 3 , the upper part of the last reaction chamber is provided with a water outlet tank 15, and is connected with the water outlet pipe 14, it is characterized in that, the inside of the pool body 1 is an anaerobic zone, an anaerobic zone, The micro-exposure short-range nitrification zone and the secondary anaerobic zone, the primary anaerobic zone includes ≥ 3 reaction chambers, the micro-exposure short-range nitrification zone includes 1 to 2 reaction chambers, and the secondary anaerobic zone Including ≥ 2 reaction chambers, the bottom of the reaction chamber of the micro-exposure short-range nitrification zone is equipped with a microporous aeration pipe 9, the upper part of the reaction chamber of the micro-exposure short-range nitrification zone and the reaction chamber of the primary anaerobic zone A return pipe 11 is provided between the lower part of each of the reaction chambers, and fillers 17 are provided in the upstream region of each of the reaction chambers. Biogas collecting pipe 8, the top of the reaction chamber of each said micro-exposure short-range nitrification zone is provided with aeration pipe 10, and the water outlet 16 of said second sub-water inlet pipe 5 is located at the first of said secondary anaerobic zone. Below the baffle plate 7 of the first reaction chamber.
所述池体1为长方体。The pool body 1 is a cuboid.
所述折流板7的折角为45°。The folding angle of the baffle 7 is 45°.
当进水COD为2000~5000mg/L,氨氮为50~200mg/L时,所述一级厌氧区包括3个反应室,所述微曝短程硝化区包括1个反应室,所述二级厌氧区包括为2个反应室。When the influent COD is 2000-5000 mg/L and ammonia nitrogen is 50-200 mg/L, the primary anaerobic zone includes 3 reaction chambers, the micro-exposure short-range nitrification zone includes 1 reaction chamber, and the secondary The anaerobic zone consists of 2 reaction chambers.
当进水COD为5000~10000mg/L,氨氮为200~800mg/L时,所述一级厌氧区包括4个反应室,所述微曝短程硝化区包括2个反应室,所述二级厌氧区包括2个反应室。When the influent COD is 5000-10000 mg/L and ammonia nitrogen is 200-800 mg/L, the primary anaerobic zone includes 4 reaction chambers, the micro-exposure short-range nitrification zone includes 2 reaction chambers, and the secondary The anaerobic zone consists of 2 reaction chambers.
所述填料17底部距所述折流板7底部≥20cm,所述填料17顶部距水面≤30cm。The distance between the bottom of the filler 17 and the bottom of the baffle 7 is ≥20 cm, and the distance between the top of the filler 17 and the water surface is ≤30 cm.
所述填料17为悬挂式柔性高分子填料。The filler 17 is a suspended flexible polymer filler.
所述填料17是为了微生物附着生长。The filler 17 is for the attachment and growth of microorganisms.
所述微孔曝气管9的内径为6~12mm,所述微孔曝气管9距池体1底部的距离≤10cm,≥5cm。The inner diameter of the microporous aeration pipe 9 is 6-12 mm, and the distance between the microporous aeration pipe 9 and the bottom of the pool body 1 is ≤10 cm, ≥5 cm.
所述微孔曝气管9与鼓风机连接。The microporous aeration pipe 9 is connected with a blower.
每个所述微曝短程硝化区的反应室内溶解氧的浓度为0.5~1.0mg/L。The concentration of dissolved oxygen in the reaction chamber of each micro-exposure short-range nitrification zone is 0.5-1.0 mg/L.
当所述微曝短程硝化区的反应室为1个时,所述回流管11设有一根,设置在微曝短程硝化区的第一个反应室的上部和一级厌氧区的第二个反应室的下部之间,即回流管11的进水口12设置在微曝短程硝化区的第一个反应室的上部,回流管11的出水口13设置在一级厌氧区的第二个反应室的下部。When there is one reaction chamber in the micro-exposure short-range nitrification zone, one return pipe 11 is arranged on the upper part of the first reaction chamber of the micro-exposure short-range nitrification zone and the second one of the first-stage anaerobic zone. Between the lower part of the reaction chamber, that is, the water inlet 12 of the return pipe 11 is set on the upper part of the first reaction chamber in the micro-exposure short-range nitrification zone, and the water outlet 13 of the return pipe 11 is set in the second reaction chamber of the primary anaerobic zone. lower part of the chamber.
当所述微曝短程硝化区的反应室为2个时,所述回流管11设有两根,其中一根设置在微曝短程硝化区的第一个反应室的上部和一级厌氧区的第二个反应室的下部之间,即回流管11的进水口12设置在微曝短程硝化区的第一个反应室的上部,回流管11的出水口13设置在一级厌氧区的第二个反应室的下部;另一根设置在微曝短程硝化区的第二个反应室的下部和一级厌氧区的第一个反应室的上部之间,即另一根回流管11的进水口12设置在微曝短程硝化区的第二个反应室的上部,另一根回流管11的出水口13设置在一级厌氧区的第一个反应室的下部。When there are 2 reaction chambers in the micro-exposure short-range nitrification zone, two return pipes 11 are provided, one of which is arranged on the upper part of the first reaction chamber of the micro-exposure short-range nitrification zone and the primary anaerobic zone Between the lower part of the second reaction chamber, that is, the water inlet 12 of the return pipe 11 is arranged on the upper part of the first reaction chamber of the micro-exposure short-range nitrification zone, and the water outlet 13 of the return pipe 11 is arranged at the first stage of the anaerobic zone. The bottom of the second reaction chamber; the other is arranged between the bottom of the second reaction chamber of the micro-exposure short-path nitrification zone and the top of the first reaction chamber of the primary anaerobic zone, that is, another return pipe 11 The water inlet 12 is set on the upper part of the second reaction chamber of the micro-exposure short-range nitrification zone, and the water outlet 13 of the other return pipe 11 is set on the lower part of the first reaction chamber of the primary anaerobic zone.
所述回流管11上设有回流泵18,所述回流泵18用于为进入回流管11的回流水提供动力。A return pump 18 is provided on the return pipe 11 , and the return pump 18 is used to provide power for the return water entering the return pipe 11 .
所述回流管11上设有回流阀19,所述回流阀19用于调节从微曝短程硝化区回流到第一厌氧区的回流水的回流比例。The return pipe 11 is provided with a return valve 19, and the return valve 19 is used to adjust the return flow ratio of return water flowing back from the micro-exposure short-path nitrification area to the first anaerobic area.
所述回流比例为20~50%。The reflux ratio is 20-50%.
所述通气管10是为了排放鼓风曝气时所产生的气体。The ventilation pipe 10 is used to discharge the gas generated during blast aeration.
所述第二分进水管5上设有分流阀20,所述分流阀20用于调节从主进水管1分流到第二分进水管5的废水分流比例。The second sub-inlet pipe 5 is provided with a diverter valve 20 , and the diverter valve 20 is used to adjust the proportion of waste water diverted from the main water inlet pipe 1 to the second sub-inlet pipe 5 .
所述分流比例为≤主进水管1进水总量的20%。The diversion ratio is ≤ 20% of the total water intake of the main water inlet pipe 1 .
当进水COD<3000mg/L,则开启所述分流阀20,可以提高二级厌氧区的COD,增加碳源,以提高后续反硝化的效果。When the influent COD<3000mg/L, the diverter valve 20 is opened, which can increase the COD in the secondary anaerobic zone, increase the carbon source, and improve the subsequent denitrification effect.
以上所述仅为本发明的较佳实施例,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included in the protection of the present invention. within range.
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