CN101066805A - A high-efficiency anaerobic ammonium oxidation reactor - Google Patents
A high-efficiency anaerobic ammonium oxidation reactor Download PDFInfo
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- CN101066805A CN101066805A CNA2007100691809A CN200710069180A CN101066805A CN 101066805 A CN101066805 A CN 101066805A CN A2007100691809 A CNA2007100691809 A CN A2007100691809A CN 200710069180 A CN200710069180 A CN 200710069180A CN 101066805 A CN101066805 A CN 101066805A
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- 230000003647 oxidation Effects 0.000 title claims description 8
- 238000007254 oxidation reaction Methods 0.000 title claims description 8
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 title claims description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 45
- 239000010802 sludge Substances 0.000 claims abstract description 39
- 239000007788 liquid Substances 0.000 claims abstract description 35
- 239000002893 slag Substances 0.000 claims abstract description 8
- 238000006243 chemical reaction Methods 0.000 claims description 26
- 239000000945 filler Substances 0.000 claims description 8
- 238000009423 ventilation Methods 0.000 claims description 6
- 238000005070 sampling Methods 0.000 claims description 4
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- 241000894006 Bacteria Species 0.000 abstract description 2
- 238000007789 sealing Methods 0.000 abstract 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 10
- 239000007789 gas Substances 0.000 description 9
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 7
- 229910021529 ammonia Inorganic materials 0.000 description 5
- 238000004062 sedimentation Methods 0.000 description 5
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- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
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- QDHHCQZDFGDHMP-UHFFFAOYSA-N Chloramine Chemical compound ClN QDHHCQZDFGDHMP-UHFFFAOYSA-N 0.000 description 1
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
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- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
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Abstract
Description
技术领域technical field
本发明涉及一种高效厌氧氨氧化反应器。The invention relates to a high-efficiency anaerobic ammonia oxidation reactor.
背景技术Background technique
随着工农业生产的发展和人民生活水平的提高,含氮有机物的排放量急剧增加。二级生物处理的陆续上马,虽然对有机物污染起到了很好的遏制作用,但是出水含氮量较高,依然是一个严重的环境污染源。氮素污染的危害极大,氨进入水体,不但能诱发“富营养化”,造成水生生态系统的紊乱,而且还能消耗溶解氧,造成水体缺氧,影响鱼锶的氧传递,使鱼类致死;与氯气作用生成氯胺,影响氯化消毒处理。因此经济有效地控制氮素污染已势在必行。With the development of industrial and agricultural production and the improvement of people's living standards, the discharge of nitrogenous organic matter has increased dramatically. Secondary biological treatment has been launched one after another. Although it has played a good role in curbing organic pollution, the high nitrogen content in the effluent is still a serious source of environmental pollution. Nitrogen pollution is extremely harmful. Ammonia entering the water body can not only induce "eutrophication" and cause the disorder of the aquatic ecosystem, but also consume dissolved oxygen, resulting in hypoxia in the water body, affecting the oxygen transfer of strontium in fish, making fish Lethal; react with chlorine gas to form chloramine, which affects chlorination disinfection treatment. Therefore, it is imperative to control nitrogen pollution economically and effectively.
废水脱氮的方法较多,有物理法、化学法和生物法等。由于种种原因,物理、化学法的应用受到很大限制,目前国内外主要采用生物脱氮技术。厌氧氨氧化反应可将氨和亚硝酸盐转化为氮气,消除氨对环境的影响。因此,研究和开发厌氧氨氧化反应器具有重要的现实意义。There are many methods for denitrification of wastewater, including physical, chemical and biological methods. Due to various reasons, the application of physical and chemical methods is greatly restricted. At present, biological denitrification technology is mainly used at home and abroad. Anammox reaction can convert ammonia and nitrite into nitrogen gas, eliminating the impact of ammonia on the environment. Therefore, the research and development of anammox reactor has important practical significance.
现有的厌氧氨氧化反应器主要由厌氧反应器演变而来。为了保证装置中有足够数量的微生物(活性污泥)进行厌氧氨氧化作用,一般在厌氧反应器后建造二次沉淀池,用以分离活性污泥,一方面满足厌氧反应器所需的活性污泥,另一方面满足出水水质要求。以二沉池分离活性污泥,并通过回流泵送回厌氧反应器,不仅增加设备,消耗动力,而且会破坏活性污泥结构,不利于形成沉淀性能优良的颗粒污泥和实现泥水分离。The existing anammox reactors are mainly evolved from anaerobic reactors. In order to ensure that there is a sufficient amount of microorganisms (activated sludge) in the device for anaerobic ammonium oxidation, a secondary sedimentation tank is generally built after the anaerobic reactor to separate the activated sludge, on the one hand to meet the needs of the anaerobic reactor Activated sludge, on the other hand, meets the requirements of effluent water quality. Separating the activated sludge with the secondary settling tank and sending it back to the anaerobic reactor through the reflux pump not only increases the equipment and consumes power, but also destroys the structure of the activated sludge, which is not conducive to the formation of granular sludge with excellent sedimentation performance and the separation of sludge and water.
针对厌氧反应器的上述缺陷,本设计试图通过设置独特的布水器,以保证进水均匀;在升流式反应室内设置填料,以持留高活性厌氧氨氧化污泥;在反应器上部设置三相分离器,以回收污泥、提高污泥浓度;通过出水回流,以稳定出水水质,并强化传质。试验证明,据此开发的新型高效厌氧氨氧化反应器具有很好的厌氧氨氧化性能。In view of the above defects of the anaerobic reactor, this design tries to ensure uniform water inflow by setting a unique water distributor; set packing in the upflow reaction chamber to retain high-activity anaerobic ammonium oxidation sludge; A three-phase separator is installed to recycle sludge and increase sludge concentration; to stabilize the quality of the effluent and enhance mass transfer through effluent backflow. Tests have proved that the new high-efficiency anammox reactor developed accordingly has good anammox performance.
发明内容Contents of the invention
本发明的目的是提供一种高效厌氧氨氧化反应器。The purpose of the present invention is to provide a high-efficiency anaerobic ammonium oxidation reactor.
高效厌氧氨氧化反应器具有反应器本体、支脚,反应器本体从上到下依次设有污泥沉淀室、渐扩室、升流式反应室,反应器本体底部内侧设有旋流布水器,反应器本体底部外侧设有进水管、排泥管、外循环管进口组成的四通管,升流式反应室上、下设有十字形网格,上、下十字形网格之间设有填料,渐扩室上部设有过流锥形挡板,污泥沉淀室内设有三相分离器,污泥沉淀室上部侧壁设有溢流堰、溢流堰出水管、液封槽,液封槽内设有液封水位控制管,液封槽底部设有液封槽排渣管,反应器本体顶部设有外循环管出口,三相分离器由集气罩与喉管构成,喉管上开通气孔,反应器本体侧壁设有多个取样口。The high-efficiency anaerobic ammonium oxidation reactor has a reactor body and legs. The reactor body is equipped with a sludge settling chamber, a gradual expansion chamber, and an upflow reaction chamber in sequence from top to bottom. A swirl water distributor is installed inside the bottom of the reactor body. , the outside of the bottom of the reactor body is provided with a four-way pipe consisting of a water inlet pipe, a mud discharge pipe, and the inlet of an external circulation pipe. There are cross-shaped grids on the upper and lower sides of the upflow reaction chamber, and a cross-shaped grid between the upper and lower cross-shaped grids. There is packing, the upper part of the gradual expansion chamber is equipped with an overflow conical baffle, the sludge settling chamber is equipped with a three-phase separator, and the upper side wall of the sludge settling chamber is equipped with an overflow weir, an outlet pipe of the overflow weir, a liquid seal tank, and a liquid seal tank. There is a liquid seal water level control pipe in the seal tank, a liquid seal tank slag discharge pipe is installed at the bottom of the liquid seal tank, and an external circulation pipe outlet is provided on the top of the reactor body. The three-phase separator is composed of a gas collecting hood and a throat pipe. Ventilation holes are opened on the top, and multiple sampling ports are provided on the side wall of the reactor body.
所述的反应器本体高径比H/D为2.5~4.0,升流式反应室横截面积S1与污泥沉淀室横截面积S2之比为1∶2.0~3.0,升流式反应室横截面积S1与三相分离器下端集气罩最大横截面积S3之比为1∶1.2~2.0,升流式反应室横截面积S1与三相分离器上端喉管横截面积S4之比为1∶0.12~0.16。The height-to-diameter ratio of the reactor body H/D is 2.5-4.0, and the ratio of the cross-sectional area S1 of the upflow reaction chamber to the cross-sectional area S2 of the sludge settling chamber is 1:2.0-3.0. The ratio of the cross-sectional area S1 of the chamber to the maximum cross-sectional area S3 of the gas collecting hood at the lower end of the three-phase separator is 1:1.2-2.0, and the cross-sectional area S1 of the upflow reaction chamber is compared with the cross-sectional area of the throat pipe at the upper end of the three-phase separator. The ratio of the area S4 is 1:0.12-0.16.
旋流布水器呈伞形,由6~12片旋转式梯形板组合而成,旋流布水器(18)母线与水平面夹角α为15~30°,相邻旋转式梯形板之间的投影重合γ为10~50mm,相邻旋转式梯形板之间的缝隙宽度a为5~20mm,旋转式梯形板上端固定在直径为100~500mm的圆形平台上,旋转式梯形板下端固定在反应器内周平台上。The swirling water distributor is umbrella-shaped and is composed of 6 to 12 rotating trapezoidal plates. The angle α between the busbar of the swirling water distributor (18) and the horizontal plane is 15 to 30°, and the projection between adjacent rotating trapezoidal plates The coincidence γ is 10-50mm, the gap width a between adjacent rotary trapezoidal plates is 5-20mm, the upper end of the rotary trapezoidal plate is fixed on a circular platform with a diameter of 100-500mm, and the lower end of the rotary trapezoidal plate is fixed on the reaction on the inner peripheral platform of the device.
十字形网格相距1000~2000mm,网格尺寸为100~200mm×100~200mm,十字形网格之间设置的填料为串状填料。十字形网格上下两个为一组,在升流式反应室内设有一组或数组十字形网格。The distance between the cross-shaped grids is 1000-2000mm, the grid size is 100-200mm×100-200mm, and the fillers arranged between the cross-shaped grids are string-shaped fillers. The upper and lower cross-shaped grids form a group, and a set or array of cross-shaped grids is arranged in the upflow reaction chamber.
过流锥形挡板设置于渐扩室内壁,位于三相分离器下部,其截面为一直角三角形,直角边长为50~200mm,三相分离器下沿至过流锥形挡板之间的污泥回流缝截面积S5与污泥沉淀室截面积S2之比为1∶2.5~4。The overflow conical baffle is set on the inner wall of the gradually expanding chamber and located at the lower part of the three-phase separator. The ratio of the cross-sectional area S5 of the sludge return slot to the cross-sectional area S2 of the sludge settling chamber is 1:2.5-4.
三相分离器集气罩截面积为梯形,下底面积与上底面积之比为8~12∶1,喉管高500~1000mm,喉管上沿高于出水液面300~500mm,并在出水液面上方100~300mm处的喉管上开4~6个通气孔,通气孔直径30~50mm。The cross-sectional area of the gas collecting hood of the three-phase separator is trapezoidal, the ratio of the area of the lower bottom to the area of the upper bottom is 8-12:1, the height of the throat is 500-1000mm, and the upper edge of the throat is 300-500mm higher than the water outlet surface, and in the 4 to 6 ventilation holes are opened on the throat at 100 to 300 mm above the water outlet surface, and the diameter of the ventilation holes is 30 to 50 mm.
外循环管出口从三相分离器喉管内伸至集气罩,外循环管出口底部管头至喉管下沿的距离为100~200mm,底部管头设成弯头,旋转角度为90°。The outlet of the external circulation pipe extends from the throat of the three-phase separator to the gas collecting hood. The distance from the bottom head of the outlet of the external circulation pipe to the lower edge of the throat is 100-200 mm. The bottom pipe head is set as an elbow with a rotation angle of 90°.
溢流堰出水管设置成弯管,出水口低于溢流堰出水管水平段中心线250~500mm,液封槽水位控制管管头与溢流堰出水管水平段中心线等高,液封槽排渣管位于液封槽底部。The outlet pipe of the overflow weir is set as an elbow, the water outlet is 250-500mm lower than the center line of the horizontal section of the outlet pipe of the overflow weir, the water level control pipe head of the liquid seal tank is at the same height as the center line of the horizontal section of the outlet pipe of the overflow weir, and the liquid seal The tank slag discharge pipe is located at the bottom of the liquid seal tank.
本发明具有的有益效果:1)能够高效持留厌氧氨氧化菌体,厌氧氨氧化反应潜力大,抗冲击能力强;2)设置出水回流,能够强化传质过程与基质转化,并缓解基质抑制;3)设置旋流式布水器,布水均匀,能够提高反应器有效容积,保证反应效能;4)设置液封槽,能够有效阻止空气向反应器内泄漏,保证反应器处于厌氧状态;5)沉淀室设置于三相分离器外围,结构紧凑,省去了二次沉淀池和污泥回流设施,避免了回流泵对颗粒污泥的破坏;6)该反应器能承受高进水氨和亚硝酸盐浓度,具有高容积转化效率,运行性能稳定。The present invention has beneficial effects: 1) it can efficiently retain the anammox bacteria, the anammox reaction potential is great, and the impact resistance is strong; 2) setting the effluent backflow can strengthen the mass transfer process and matrix transformation, and relieve the matrix Inhibition; 3) Set up a swirling water distributor to distribute water evenly, which can increase the effective volume of the reactor and ensure the reaction efficiency; 4) Set up a liquid seal tank, which can effectively prevent air from leaking into the reactor and ensure that the reactor is anaerobic 5) The settling chamber is set on the periphery of the three-phase separator with a compact structure, eliminating the secondary settling tank and sludge return facilities, and avoiding the damage of the return pump to the granular sludge; 6) The reactor can withstand high influent ammonia and nitrite concentration, with high volume conversion efficiency and stable operation performance.
附图说明Description of drawings
图1是厌氧氨氧化反应器结构示意图;图中:支脚1、法兰2、升流式反应室3、填料4、十字形网格5、渐阔室6、过流锥形挡板7、沉淀室8、溢流堰9、外循环管出口10、三相分离器11、通气孔12、溢流堰出水管13、液封水位控制管14、液封槽15、液封槽排渣管16、取样口17、旋流布水器18、进水管19、排泥管20、外循环管进口21;Figure 1 is a schematic diagram of the structure of an anammox reactor; in the figure:
图2是本发明的旋流布水器结构示意图。Fig. 2 is a structural schematic diagram of the swirl water distributor of the present invention.
具体实施方式Detailed ways
如附图所示,高效厌氧氨氧化反应器具有反应器本体、支脚1,反应器本体从上到下依次设有污泥沉淀室8、渐扩室6、升流式反应室3,反应器本体底部内侧设有旋流布水器18,反应器本体底部外侧设有进水管19、排泥管20、外循环管进口2)组成的四通管,升流式反应室3上、下设有十字形网格5,上、下十字形网格5之间设有填料4,渐扩室6上部设有过流锥形挡板7,污泥沉淀室8内设有三相分离器11,污泥沉淀室8上部侧壁设有溢流堰9、溢流堰出水管13、液封槽15,液封槽15内设有液封水位控制管14,液封槽15底部设有液封槽排渣管16,反应器本体顶部设有外循环管出口10,三相分离器11由集气罩与喉管构成,喉管上开通气孔12,反应器本体侧壁设有多个取样口17。As shown in the drawings, the high-efficiency anaerobic ammonium oxidation reactor has a reactor body and a
所述的反应器本体高径比H/D为2.5~4.0,升流式反应室3横截面积S1与污泥沉淀室8横截面积S2之比为1∶2.0~3.0,升流式反应室3横截面积S1与三相分离器11下端集气罩最大横截面积S3之比为1∶1.2~2.0,升流式反应室3横截面积S1与三相分离器11上端喉管横截面积S4之比为1∶0.12~0.16。The height-to-diameter ratio of the reactor body H/D is 2.5-4.0, the ratio of the cross-sectional area S1 of the upflow reaction chamber 3 to the cross-sectional area S2 of the sludge settling chamber 8 is 1:2.0-3.0, and the upflow The ratio of the cross-sectional area S1 of the type reaction chamber 3 to the maximum cross-sectional area S3 of the gas collecting hood at the lower end of the three-
旋流布水器18呈伞形,根据反应器容积大小,由6~12片旋转式梯形板组合而成,旋流布水器18母线与水平面夹角α为15~30°,相邻旋转式梯形板之间的投影重合γ为10~50mm,相邻旋转式梯形板之间的缝隙宽度a为5~20mm,旋转式梯形板上端固定在直径为100~500mm的圆形平台上,旋转式梯形板下端固定在反应器内周平台上。The
十字形网格5相距1000~2000mm,网格尺寸为100~200mm×100~200mm,十字形网格5之间设置的填料4为串状填料。十字形网格5上下两个为一组,在升流式反应室3内设有一组或数组十字形网格。The distance between the
过流锥形挡板7设置于渐扩室6内壁,位于三相分离器下部,其截面为一直角三角形,直角边长为50~200mm,三相分离器11下沿至过流锥形挡板7之间的污泥回流缝截面积S5与污泥沉淀室8截面积S2之比为1∶2.5~4。三相分离器11集气罩截面积为梯形,下底面积与上底面积之比为8~12∶1,喉管高500~1000mm,喉管上沿高于出水液面300~500mm,并在出水液面上方100~300mm处的喉管上开4~6个通气孔12,通气孔直径30~50mm。外循环管出口10从三相分离器11喉管内伸至集气罩,外循环管出口10底部管头至喉管下沿的距离为100~200mm,底部管头设成弯头,旋转角度为90°。The overflow
溢流堰出水管13设置成弯管,出水口低于溢流堰出水管13水平段中心线250~500mm,液封槽水位控制管14管头与溢流堰出水管13水平段中心线等高,液封槽排渣管16位于液封槽底部。The outlet pipe 13 of the overflow weir is set as an elbow, the water outlet is 250-500mm lower than the center line of the horizontal section of the outlet pipe 13 of the overflow weir, the head of the water
高效厌氧氨氧化反应器由钢板构建。接种污泥投加至升流式反应室。污水通过进水管导入反应室底部,经过旋流布水器均匀分布,污泥与废水充分接触,高活性的厌氧氨氧化污泥或附着生长在填料表面,或阻截于填料内,所产生的气体(N2)上逸,由三相分离器收集后通过通气孔和液封槽排出反应器,随气体带上的污泥经过过流锥形挡板的阻挡作用,大部分被截留在升流式反应室内,少量流入至污泥沉淀室,沉淀分离后,依靠污泥重力由污泥回流缝返回至升流式反应室。反应器出水经过污泥沉淀室溢流至液封槽内,由液封槽水位控制管出水。部分出水通过外循环管回流至反应器底部,用于强化传质与基质降解。剩余活性污泥由排泥管排出反应器外。The high-efficiency anammox reactor is constructed of steel plates. Inoculation sludge was added to the upflow reaction chamber. The sewage is introduced into the bottom of the reaction chamber through the water inlet pipe, and is evenly distributed through the swirling water distributor. The sludge and the wastewater are fully contacted. (N 2 ) escapes upwards, is collected by the three-phase separator and discharged out of the reactor through the vent hole and the liquid seal tank, and the sludge on the gas belt passes through the blocking effect of the overflow conical baffle, and most of it is trapped in the upflow A small amount flows into the sludge settling chamber, and after sedimentation and separation, it returns to the upflow reaction chamber from the sludge return slot by relying on the gravity of the sludge. The effluent from the reactor overflows into the liquid seal tank through the sludge settling chamber, and the water is discharged from the water level control pipe of the liquid seal tank. Part of the effluent is returned to the bottom of the reactor through the external circulation pipe to enhance mass transfer and matrix degradation. The remaining activated sludge is discharged out of the reactor through the sludge discharge pipe.
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CN102010113A (en) * | 2010-10-27 | 2011-04-13 | 山东建筑大学 | Anaerobic solid reactor |
CN102145940A (en) * | 2011-02-23 | 2011-08-10 | 大连理工大学 | Fast breeding device and method of anammox bacteria |
CN102153194A (en) * | 2011-02-28 | 2011-08-17 | 杭州师范大学 | Upflow subregion anammox bioreactor |
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CN103755020B (en) * | 2013-12-26 | 2015-12-09 | 中南大学 | A rapid start-up device for anaerobic ammonium oxidation based on acid-base regulation |
CN105152324A (en) * | 2015-09-22 | 2015-12-16 | 浙江大学 | Anaerobic ammonia oxidation reactor capable of classifying sludge through cyclone |
CN107487843A (en) * | 2017-10-10 | 2017-12-19 | 重庆大学 | A kind of vacuous solar energy heat collecting type open air upflow anaerobic sludge blanket reactor |
CN107935183A (en) * | 2017-12-27 | 2018-04-20 | 山东太平洋环保股份有限公司 | A kind of high-efficiency biological denitrification reactor and process for treating high ammonia nitrogen waste water |
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CN114804527A (en) * | 2022-04-30 | 2022-07-29 | 齐鲁工业大学 | Movable upflow MBBR integrated sewage treatment equipment and system |
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