CN102531162A - First-grid upflow ABR (Anaerobic Baffled Reactor) reactor improved device and method - Google Patents
First-grid upflow ABR (Anaerobic Baffled Reactor) reactor improved device and method Download PDFInfo
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Abstract
Description
技术领域 technical field
本发明涉及一种污废水厌氧处理装置及方法,属于反应器范畴,主要用于城镇生活污水、化工、印染等工业废水的前处理,中小规模生活污水收集后可直接进入本反应器,工业废水经预处理后进入本反应器。The invention relates to a device and method for anaerobic treatment of sewage and wastewater, which belongs to the category of reactors and is mainly used for the pretreatment of urban domestic sewage, chemical industry, printing and dyeing and other industrial wastewater. Small and medium-scale domestic sewage can directly enter the reactor after being collected. Wastewater enters the reactor after pretreatment.
背景技术 Background technique
厌氧处理反应器主要有上流式厌氧污泥床(UASB)、膨胀颗粒污泥床反应器(EGSB)、厌氧内循环反应器(IC)、厌氧折板反应器(ABR)等。UASB反应器由于同时具备厌氧过滤及厌氧活性污泥法的双重特点,在形成颗粒污泥的基础上,通过三相分离器有效分离泥水和沼气,因而耐冲击负荷;缺点是三相分离器结构复杂。ABR反应器的特点是在反应器内沿水流方向设置多个折流挡板,将反应器分隔成若干个串联的反应区,每个反应区又分隔成上流室和降流室,由于折流板的阻挡和污泥的自身沉降性能,污泥多被截留在各自的反应区内,形成相对独立的微生物反应区。缺点是:首格反应区要承受的负荷远大于平均负荷,造成局部负荷过载;容积较大、上升流速较小的升流室易形成沟流和死角,大大减小了反应器容积负荷。Anaerobic treatment reactors mainly include upflow anaerobic sludge bed reactor (UASB), expanded granular sludge bed reactor (EGSB), anaerobic internal circulation reactor (IC), anaerobic folded plate reactor (ABR), etc. UASB reactor has the dual characteristics of anaerobic filtration and anaerobic activated sludge method at the same time. On the basis of forming granular sludge, muddy water and biogas are effectively separated through a three-phase separator, so it is resistant to impact loads; the disadvantage is three-phase separation The device structure is complex. The characteristic of the ABR reactor is that multiple baffles are set in the reactor along the water flow direction to divide the reactor into several series reaction zones, and each reaction zone is divided into an upflow chamber and a downflow chamber. Due to the baffle Due to the blocking of the plate and the self-settling performance of the sludge, the sludge is mostly trapped in its own reaction zone, forming a relatively independent microbial reaction zone. The disadvantages are: the load to be borne by the Shouge reaction zone is much greater than the average load, resulting in partial load overload; the upflow chamber with a large volume and a small ascending flow rate is prone to channeling and dead angles, which greatly reduces the volume load of the reactor.
发明内容 Contents of the invention
1、发明目的1. Purpose of the invention
本发明目的是将首格升流式ABR反应器改进装置分为首格升流式反应区、折流反应室串联反应区。借鉴UASB反应器的设计原理,充分利用首格进水泵进行动力布水,在ABR反应器的首格反应区设置三相分离器,采用上流式进水方式,将首格反应区分割成反应区、泥水分离区、排气区,有效提高ABR反应器应对高负荷污废水冲击的能力。在上向流反应室设置导流板和挡板,并采用周边堰溢流出水方式,有效提高上流室污水混合紊流程度;在上流室设置填料区,提高厌氧微生物富集效果并可有效截流上升污泥以防进入下一反应区,营造相对独立的厌氧微生物增殖环境。The object of the present invention is to divide the improved device of the first up-flow ABR reactor into the first up-flow type reaction zone and the series reaction zone of the baffled reaction chamber. Drawing lessons from the design principle of the UASB reactor, making full use of the Shouge water inlet pump for dynamic water distribution, setting a three-phase separator in the Shouge reaction area of the ABR reactor, and adopting an upflow water inlet method to divide the Shouge reaction area into reaction areas , mud-water separation area, and exhaust area, effectively improving the ability of the ABR reactor to cope with the impact of high-load sewage and wastewater. Set deflectors and baffles in the upward flow reaction chamber, and use the overflow method of peripheral weirs to effectively improve the mixing and turbulent degree of sewage in the upper flow chamber; set a packing area in the upper flow chamber to improve the enrichment effect of anaerobic microorganisms and effectively The rising sludge is intercepted to prevent it from entering the next reaction zone, creating a relatively independent anaerobic microbial proliferation environment.
2、技术方案2. Technical solution
本发明的技术方案:一种污废水厌氧处理装置,首格反应室采用UASB反应器设计结构,在上部设置折流挡板,中部设置反射锥,将首格反应区分为反应区、排气区、泥水分离区,可有效减少因为产气和水流上升引起的厌氧污泥流失;首格反应区之后为多个下向流反应室和上向流反应室的串联,下向流与上向流反应室通过导流板和斜板分隔开,上向流反应室宽度大于下向流反应室,上流室设置填料,从而形成污泥沉降区、填料区、上流室泥水分离区三个区;污废水在上下流反应室折流过程中除了导流板的导流作用外,还有上流室挡板阻挡所起到的均匀布水作用,结合周边堰出水方式,污废水在上流室紊流混合,克服了传统ABR反应器上流室沟流和死角多的缺点。The technical solution of the present invention: an anaerobic treatment device for sewage and wastewater. The first reaction chamber adopts the UASB reactor design structure, and a baffle baffle is arranged on the upper part, and a reflection cone is arranged on the middle part, and the first reaction zone is divided into a reaction area, an exhaust zone and mud-water separation zone, which can effectively reduce the loss of anaerobic sludge caused by gas production and rising water flow; after the Shouge reaction zone, there are multiple downflow reaction chambers and upflow reaction chambers in series, and the downflow and upflow reaction chambers are connected in series. The upward flow reaction chamber is separated by deflectors and inclined plates, the width of the upward flow reaction chamber is larger than that of the downward flow reaction chamber, and the upper flow chamber is equipped with fillers, thus forming three sludge settlement areas, packing areas, and upper flow chamber mud-water separation areas. area; during the reflux process of sewage and wastewater in the upstream and downstream reaction chambers, in addition to the diversion effect of the deflector, there is also the function of uniform water distribution played by the baffle in the upper chamber. Turbulent mixing overcomes the shortcomings of channel flow and many dead ends in the upper chamber of the traditional ABR reactor.
一种污废水厌氧处理方法,其步骤为:A method for anaerobic treatment of sewage and wastewater, the steps of which are:
一、污废水从底部进入反应器首格反应区,在反应区A形成颗粒污泥,发酵产生气体混合污泥在上升过程中碰撞反射锥(2)和折流挡板(1),引起泥气分离,分离后气体从排气区(B)排出并通过排气口(9)回收利用,脱气后的泥水混合液进入泥水分离区(C)进行泥水分离,分离上清液溢流进入下一个反应区,沉淀后的污泥滑落到主体反应区(A)参与污染物分解作用。1. Sewage and waste water enter the reaction zone of the reactor from the bottom, and granular sludge is formed in the reaction zone A, and the gas mixed with the sludge generated by fermentation collides with the reflector cone (2) and the baffle plate (1) during the rising process, causing sludge Gas separation, the separated gas is discharged from the exhaust area (B) and recycled through the exhaust port (9), the degassed mud-water mixture enters the mud-water separation area (C) for mud-water separation, and the separated supernatant overflows into the In the next reaction zone, the settled sludge slides down to the main reaction zone (A) to participate in the decomposition of pollutants.
二、ABR反应器各反应区通过隔板或隔墙(3)隔开,下向流反应室和上向流反应室通过导流板(4)和斜板(5)分隔开,首格反应区出水进入ABR反应器下向流反应室(D1),在导流板(4)及斜板(5)导流作用下进入上流室,挡板(6)起到均匀进水的作用,上流室宽度大于下流室,因而进入上流室的流速会显著降低,促进污泥在上流室底部形成污泥沉降区(E1),上流室中部为填料区(F1),设置组合填料或悬浮填料球等,富集厌氧微生物,通过微生物分解有效净化污水,形成的泥水混合物在G1区泥水分离后,上清液通过周边堰(8)溢流收集进入下一个反应区,多次净化后溢流排出。上下流反应室串联数量因进水水质而异。2. Each reaction area of the ABR reactor is separated by a partition or a partition wall (3), and the downflow reaction chamber and the upflow reaction chamber are separated by a deflector (4) and an inclined plate (5). The effluent from the reaction zone enters the downflow reaction chamber (D1) of the ABR reactor, and enters the upflow chamber under the diversion action of the deflector (4) and the inclined plate (5), and the baffle (6) plays the role of uniform water inflow. The width of the upflow chamber is larger than that of the downflow chamber, so the flow rate into the upflow chamber will be significantly reduced, promoting the sludge to form a sludge settlement zone (E1) at the bottom of the upflow chamber, and the middle part of the upflow chamber is a filler zone (F1), where combined fillers or suspended filler balls are set etc., enrich anaerobic microorganisms, and effectively purify sewage through microbial decomposition. After the mud-water mixture is separated in the G1 area, the supernatant is collected by the overflow of the surrounding weir (8) and enters the next reaction area. After multiple purifications, the overflow discharge. The number of series connection of up and down flow reaction chambers varies with the quality of influent water.
三、斜板(5)导流结合挡板(6)均匀进水、周边堰(8)溢流出水,有效起到了上流室污水的紊流混合作用。每个ABR反应区底部设有倾斜坡度(7),沉降的污泥滑落到反应区一角,定期清除。3. The slant plate (5) diversion combined with the baffle plate (6) evenly enters the water, and the peripheral weir (8) overflows the water, effectively playing the role of turbulent mixing of the sewage in the upper chamber. The bottom of each ABR reaction zone is provided with an inclined slope (7), and the settled sludge slides to a corner of the reaction zone and is regularly removed.
3、有益效果:3. Beneficial effects:
1)由于首格反应区采用类似UASB的上流式进水,具备可形成颗粒污泥的条件,容积负荷高,耐冲击负荷能力强,有效提高了整个ABR反应器抗冲击负荷的能力,解决了传统ABR反应器首格反应区承受负荷大,局部负荷过载的问题;三相分离器的设置,可有效减少因为产气和水流引起的厌氧污泥流失问题。1) Since the Shouge reaction zone adopts an upflow water inlet similar to UASB, it has the conditions to form granular sludge, high volume load, and strong impact load resistance, which effectively improves the impact load resistance of the entire ABR reactor and solves the problem of The Shouge reaction zone of the traditional ABR reactor bears a large load and the local load is overloaded; the setting of the three-phase separator can effectively reduce the loss of anaerobic sludge caused by gas production and water flow.
2)污废水在上下流反应室折留过程中除了有导流板的导流作用外,还有挡板阻挡起到的均匀布水作用,结合周边堰出水方式,污废水在上流室充分混合,克服了传统ABR反应器上流室沟流和死角多的缺点。2) In the retention process of the sewage and wastewater in the upper and lower reaction chambers, in addition to the diversion effect of the deflector, there is also a uniform water distribution function played by the baffle barrier. Combined with the water outlet method of the surrounding weir, the sewage and wastewater are fully mixed in the upper flow chamber , Overcoming the shortcomings of channeling and many dead ends in the upper chamber of the traditional ABR reactor.
3)上流室设置填料区,提高厌氧微生物富集效果的同时,可阻隔厌氧污泥的上升,上清液从泥水分离区顶部周边堰溢流出水,沉降污泥集中在各自反应区的一角,定期清除,不对其他反应区造成影响,各反应区营造了相对独立的厌氧微生物增殖环境,厌氧微生物种类繁多,厌氧过程也复杂多过程,分区的方式可提高厌氧处理的效率。3) The upflow chamber is equipped with a packing area to improve the enrichment effect of anaerobic microorganisms and at the same time block the rise of anaerobic sludge. The supernatant overflows from the weir around the top of the mud-water separation area, and the settled sludge is concentrated in the respective reaction areas. One corner, cleared regularly, does not affect other reaction areas. Each reaction area creates a relatively independent anaerobic microbial proliferation environment. There are many types of anaerobic microorganisms, and the anaerobic process is also complex and multi-process. The method of partitioning can improve the efficiency of anaerobic treatment. .
附图说明 Description of drawings
图1是首格升流式ABR反应器改进装置示意图。Figure 1 is a schematic diagram of the improvement device of Shouge upflow ABR reactor.
其中1为折流挡板,2为反射锥,3为隔板或隔墙,4为导流板,5为导流板斜板,6为挡板,7为斜坡,8为周边出水堰,9为排气口;A为反应区,B为排气区,C为泥水分离区,D1、D2、D3为下向流反应室,E1、E2、E3为污泥沉降区,F1、F2、F3为填料区,G1、G2、G3上流室泥水分离区。Among them, 1 is baffle, 2 is reflection cone, 3 is partition or partition wall, 4 is deflector, 5 is inclined plate of deflector, 6 is baffle, 7 is slope, 8 is peripheral weir, 9 is the exhaust port; A is the reaction area, B is the exhaust area, C is the mud-water separation area, D1, D2, D3 are the downward flow reaction chambers, E1, E2, E3 are the sludge settlement areas, F1, F2, F3 is the filling area, G1, G2, and G3 are the mud-water separation areas in the upper chambers.
图2是周边堰溢流出水示意图。Figure 2 is a schematic diagram of the overflow of the peripheral weir.
具体实施方式 Detailed ways
下面结合附图1、2进一步对本发明作进一步说明。The present invention will be further described below in conjunction with accompanying
实施例Example
对照图1、2,首格升流式ABR反应器改进装置主体结构可以是砖混结构或钢结构,整个反应器分为四个反应区,分别为首格升流式反应区、三个上下流反应室串联反应区,各反应区通过隔板或隔墙(3)隔开。污废水经收集后从底部进入反应器首格反应区,进水管开口向下以防沉淀污泥堵塞进水管。污水升流过程中接触反应区A内形成的颗粒污泥,厌氧微生物分解、同化吸收污水中有机物及氮磷等营养物质,有机物分解产生的甲烷、氢气等气体物质混合部分污泥上升,碰撞反射锥(2)和折流挡板(1),反射锥和折流挡板为钢结构或硬质塑料结构,反射锥为三角形状,折流挡板折角120°~145°,反射锥和折流挡板在一侧方向上重叠有余,气体反射阻挡后从排气区(B)排出并通过排气口(9)回收利用,气体分离后的泥水混合液通过反射锥和折流挡板之间的缺口进入泥水分离区(C),在泥水分离区没有了产气的扰动,污泥在重力作用下沉降,遇反射锥滑落到反应区继续参与污染物净化作用,上清液则溢流进入第二格反应区的下流室(D1)。第二格反应区上下流室通过导流板(4)和斜板(5)分隔开,导流板、斜板可以为钢制或硬质塑料,导流板与斜板夹角在120°~145°,上下流反应室体积2∶1~3∶1,污水在导流板和斜板的导流下进入上流室,由于体积增大,上流室污水上升流速较下流室下降流速显著降低,挡板(6)阻挡促进布水均匀的同时促使污水中悬浮物质在污泥沉降区(E1)沉降,第二反应区底部斜坡坡度为5%,沉降的污泥滑落到反应区一角,定期清除。上流室中部填料区(F1)占上流室体积1/3~1/2,填料采用组合填料或悬浮填料球(悬浮填料球需固定住)等富集厌氧微生物,填料上富集的微生物是污水净化的主要参与者,脱落的微生物部分沉降进入污泥沉降区,部分随同上流污水进入上流室泥水分离区(G1),在重力作用下逐渐沉淀,上清液则通过周边堰(8)溢流进入第三格反应区的下流室(D2),周边堰可以为平口堰或锯齿堰。第三格反应区上下流室通过导流板(4)和斜板(5)分隔开,导流板、斜板可以为钢制或硬质塑料,导流板与斜板夹角在120°~145°,上下流反应室体积2∶1~3∶1,污水在导流板和斜板的导流下进入上流室,由于体积增大,上流室污水上升流速较下流室下降流速显著降低,挡板(6)阻挡促进布水均匀的同时促使污水中悬浮物质在污泥沉降区(E2)沉降,第三反应区底部斜坡坡度为5%,沉降的污泥滑落到反应区一角,定期清除。上流室中部填料区(F2)占上流室体积1/3~1/2,填料采用组合填料或悬浮填料球(悬浮填料球需固定住)等富集厌氧微生物,填料上富集的微生物是污水净化的主要参与者,脱落的微生物部分沉降进入污泥沉降区,部分随同上流污水进入上流室泥水分离区(G2),在重力作用下逐渐沉淀,上清液则通过周边堰(8)溢流进入第四格反应区的下流室(D3),周边堰可以为平口堰或锯齿堰。第四格反应区上下流室通过导流板(4)和斜板(5)分隔开,导流板、斜板可以为钢制或硬质塑料,导流板与斜板夹角在120°~145°,上下流反应室体积2∶1~3∶1,污水在导流板和斜板的导流下进入上流室,由于体积增大,上流室污水上升流速较下流室下降流速显著降低,挡板(6)阻挡促进布水均匀的同时促使污水中悬浮物质在污泥沉降区(E3)沉降,第四反应区底部斜坡坡度为5%,沉降的污泥滑落到反应区一角,定期清除。上流室中部填料区(F3)占上流室体积1/3~1/2,填料采用组合填料或悬浮填料球(悬浮填料球需固定住)等富集厌氧微生物,填料上富集的微生物是污水净化的主要参与者,脱落的微生物部分沉降进入污泥沉降区,部分随同上流污水进入上流室泥水分离区(G3),在重力作用下逐渐沉淀,上清液则溢流排出。Comparing with Figures 1 and 2, the main structure of the Shouge upflow ABR reactor improvement device can be a brick-concrete structure or a steel structure. The reaction chamber is connected in series with reaction areas, and each reaction area is separated by a partition or a partition wall (3). After the sewage water is collected, it enters the Shouge reaction zone of the reactor from the bottom, and the opening of the water inlet pipe is downward to prevent the sedimentation sludge from blocking the water inlet pipe. During the upflow process of sewage, it contacts the granular sludge formed in the reaction zone A, anaerobic microorganisms decompose, assimilate and absorb organic matter and nutrients such as nitrogen and phosphorus in the sewage, and the gas substances such as methane and hydrogen generated by the decomposition of organic matter are mixed with part of the sludge. The reflection cone (2) and the baffle plate (1), the reflection cone and the baffle plate are steel structure or hard plastic structure, the reflection cone is triangular shape, the deflection baffle angle is 120°~145°, the reflection cone and The deflection baffle overlaps more than one side. After the gas is reflected and blocked, it is discharged from the exhaust area (B) and recycled through the exhaust port (9). The mud-water mixture after gas separation passes through the reflection cone and the deflection baffle. The gap between them enters the mud-water separation zone (C), where there is no disturbance of gas production, the sludge settles under the action of gravity, meets the reflection cone and slides down to the reaction zone to continue to participate in the purification of pollutants, and the supernatant overflows The flow enters the downflow chamber (D1) of the second compartment reaction zone. The upper and lower flow chambers of the second grid reaction zone are separated by a deflector (4) and an inclined plate (5). The deflector and the inclined plate can be made of steel or hard plastic, and the angle between the deflector and the inclined plate is 120. ° ~ 145°, the volume of the upstream and downstream reaction chambers is 2:1 ~ 3:1, the sewage enters the upstream chamber under the diversion of the deflector and the inclined plate, due to the increase in volume, the upward flow rate of the sewage in the upstream chamber is significantly higher than the downward flow rate in the downstream chamber lower, the baffle (6) stops and promotes uniform water distribution, and at the same time promotes the settlement of suspended matter in the sewage in the sludge settlement zone (E1). The slope at the bottom of the second reaction zone is 5%, and the settled sludge slides to a corner of the reaction zone. Remove regularly. The filling area (F1) in the middle of the upflow chamber accounts for 1/3 to 1/2 of the volume of the upflow chamber. As the filler, combined fillers or suspended filler balls (the suspended filler balls need to be fixed) are used to enrich anaerobic microorganisms. The microorganisms enriched on the filler are The main participant in sewage purification, part of the shed microorganisms settles into the sludge settlement area, and part enters the mud-water separation area (G1) of the upper chamber with the upstream sewage, and gradually settles under the action of gravity, and the supernatant overflows through the surrounding weir (8) The flow enters the downflow chamber (D2) of the third grid reaction zone, and the peripheral weir can be a flat weir or a sawtooth weir. The upper and lower flow chambers of the third grid reaction area are separated by the deflector (4) and the inclined plate (5). The deflector and the inclined plate can be made of steel or hard plastic, and the angle between the deflector and the inclined plate is 120. ° ~ 145°, the volume of the upstream and downstream reaction chambers is 2:1 ~ 3:1, the sewage enters the upstream chamber under the diversion of the deflector and the inclined plate, due to the increase in volume, the upward flow rate of the sewage in the upstream chamber is significantly higher than the downward flow rate in the downstream chamber lower, the baffle (6) stops and promotes uniform water distribution, and at the same time promotes the settlement of suspended matter in the sewage in the sludge settlement zone (E2). The slope at the bottom of the third reaction zone is 5%, and the settled sludge slides to a corner of the reaction zone. Remove regularly. The filling area (F2) in the middle of the upflow chamber accounts for 1/3 to 1/2 of the volume of the upflow chamber. As the filler, combined fillers or suspended filler balls (the suspended filler balls need to be fixed) are used to enrich anaerobic microorganisms. The microorganisms enriched on the filler are The main participant in sewage purification, part of the shed microorganisms settles into the sludge settlement area, and part enters the mud-water separation area (G2) of the upper chamber with the upstream sewage, and gradually settles under the action of gravity, and the supernatant overflows through the surrounding weir (8) The flow enters the downflow chamber (D3) of the fourth grid reaction zone, and the peripheral weir can be a flat weir or a sawtooth weir. The upper and lower flow chambers in the reaction zone of the fourth grid are separated by a deflector (4) and an inclined plate (5). The deflector and the inclined plate can be made of steel or hard plastic, and the angle between the deflector and the inclined plate is 120° °~145°, the volume of the upstream and downstream reaction chambers is 2:1~3:1, the sewage enters the upstream chamber under the diversion of the guide plate and the inclined plate, due to the increase in volume, the upward flow rate of the sewage in the upstream chamber is significantly higher than the downward flow rate in the downstream chamber lower, the baffle plate (6) blocks and promotes uniform water distribution, and at the same time promotes the settlement of suspended matter in the sewage in the sludge settlement zone (E3). The slope at the bottom of the fourth reaction zone is 5%, and the settled sludge slides to a corner of the reaction zone. Remove regularly. The filling area (F3) in the middle of the upflow chamber accounts for 1/3 to 1/2 of the volume of the upflow chamber. As the filler, combined fillers or suspended filler balls (the suspended filler balls need to be fixed) are used to enrich anaerobic microorganisms. The microorganisms enriched on the filler are The main participants in sewage purification, part of the shed microorganisms settles into the sludge settlement area, and part enters the mud-water separation area (G3) of the upper chamber with the upstream sewage, and gradually settles under the action of gravity, and the supernatant is overflowed and discharged.
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Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20050028985A (en) * | 2003-09-19 | 2005-03-24 | 안대희 | A wastewater treatment apparatus combined a membrane soaked biological reactor and an anaerobic granule sludge packed reactor |
CN1803668A (en) * | 2006-01-12 | 2006-07-19 | 林长青 | Multiphase Internal Circulation Anaerobic Reactor |
CN1899980A (en) * | 2006-07-20 | 2007-01-24 | 清华大学 | Method and device for improving three phase separating efficiency of baffle type anaerobic biological reactor |
CN101113054A (en) * | 2006-07-25 | 2008-01-30 | 陈晓华 | Microbiological anaerobic diversion reaction apparatus based on EMO organic carrier |
CN201458823U (en) * | 2009-04-21 | 2010-05-12 | 龙吉海 | Biological filtration tank of up/reverse-flow anaerobic baffle plate |
-
2011
- 2011-12-21 CN CN2011104311006A patent/CN102531162A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20050028985A (en) * | 2003-09-19 | 2005-03-24 | 안대희 | A wastewater treatment apparatus combined a membrane soaked biological reactor and an anaerobic granule sludge packed reactor |
CN1803668A (en) * | 2006-01-12 | 2006-07-19 | 林长青 | Multiphase Internal Circulation Anaerobic Reactor |
CN1899980A (en) * | 2006-07-20 | 2007-01-24 | 清华大学 | Method and device for improving three phase separating efficiency of baffle type anaerobic biological reactor |
CN101113054A (en) * | 2006-07-25 | 2008-01-30 | 陈晓华 | Microbiological anaerobic diversion reaction apparatus based on EMO organic carrier |
CN201458823U (en) * | 2009-04-21 | 2010-05-12 | 龙吉海 | Biological filtration tank of up/reverse-flow anaerobic baffle plate |
Non-Patent Citations (1)
Title |
---|
童健等: "ABR反应器的设计", 《江苏环境科技》 * |
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