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Biological Nitrogen Removal from Nitrogen-Rich Wastewaters by Partial Nitrification and Anaerobic Ammonium Oxidation

机译:部分硝化和厌氧铵氧化法去除富氮废水中的生物氮

摘要

PURPOSE: A system for advanced biological wastewater treatment by partial nitrification (NH4-NNO2-N) and anaerobic ammonium oxidation is provided to effectively treat nitrogen-rich wastewater with no supply of external carbon source. CONSTITUTION: Wastewater is first introduced into a precipitation tank(1) before it is treated in an intermittent aeration SBR(2), because organics and phosphorus of raw wastewater inhibit anaerobic ammonia oxidation in the intermittent aeration SBR. In the precipitation tank phosphorus up to 90 % and organics up to 75 % are removed by chemical precipitation. The intermittent aeration SBR process consists of partial nitrification, denitrification and reaeration. The partial nitrification lasts until SCOD/NO2-N become 2, and represented as follows,(2NH4¬+)+(3O2)(2NO2¬-)+(4H¬+)+(H2O)(partial nitrification/aerobic). After partial nitrification the intermittent aeration SBR is alternated to anoxic condition for denitrification, by which organics are consumed. This reaction is represented as shown below,(2NO2¬-)+(CH3)OH+(CO2) (N2)+(2HCO¬-)3+(H2)(denitrification/anoxic). These alternative reactions are repeated until the ratio of NH4-N/NO2-N become 1:1.3. For the optimal operation, the temperature of wastewater is maintained with the range of 30 to 35 deg.C and sludge retention time (SRT) is controlled to be 1.0 to 3.0 days. After wastewater is treated in the intermittent aeration SBR process, it enters into a deaeration tank(3) where oxygen an inhibition factor of anaerobic ammonia oxidation is removed and settled sludge is withdrawn. Effluent from the deaeration tank is introduced into a continuous media reactor (SMR,4) for allowing wastewater to come into contact with fixed media when directed downward and fluidizing media when directed upward. The anaerobic ammonia oxidation process is represented as shown below, (NH4¬+)+(1.3NO2¬-)+(0.0425CO)2(1.045N)2+(0.22NO3¬-)3+1.87(H2O)+(0.09OH¬-)+(0.0425CH)2. For the optimal operation, the temperature of wastewater in the continuous media reactor is maintained with the range of 30 to 35 deg.C, hydraulic retention time (HRT) is controlled to be 1.5 to 2.0 days and pH 7 to 8.
机译:目的:提供一种通过部分硝化(NH4-NNO2-N)和厌氧铵氧化处理高级生物废水的系统,以有效地处理无需外部碳源的富氮废水。组成:废水首先被引入沉淀池(1),然后在间歇曝气SBR(2)中进行处理,因为原废水中的有机物和磷会抑制间歇曝气SBR中的厌氧氨氧化。在沉淀池中,通过化学沉淀去除了高达90%的磷和高达75%的有机物。间歇曝气SBR工艺包括部分硝化,反硝化和再反应。持续进行部分硝化直到SCOD / NO2-N变为2,并表示如下:(2NH4¬+)+(3O2)(2NO2¬-)+(4H¬+)+(H2O)(部分硝化/好氧)。部分硝化后,间歇曝气SBR交替进入缺氧条件进行反硝化,从而消耗有机物。该反应表示如下,(2NO 2--)+(CH 3)OH +(CO 2)(N 2)+(2HCO--)3 +(H 2)(脱氮/缺氧)。重复这些替代反应,直到NH4-N / NO2-N的比例变为1:1.3。为了实现最佳操作,废水的温度保持在30到35℃的范围内,污泥保留时间(SRT)控制为1.0到3.0天。废水经过间歇曝气SBR工艺处理后,进入除氧池(3),在其中除氧和厌氧氨氧化的抑制因子,并去除沉淀的污泥。将脱气罐的废水引入连续介质反应器(SMR,4)中,以使废水在向下引导时与固定介质接触,而在向上引导时与流化介质接触。厌氧氨氧化过程如下所示:(NH4¬+)+(1.3NO2¬-)+(0.0425CO)2(1.045N)2+(0.22NO3¬-)3 + 1.87(H2O)+(0.09 OH-)+(0.0425CH)2。为了实现最佳操作,连续介质反应器中废水的温度保持在30至35摄氏度的范围内,水力停留时间(HRT)控制为1.5至2.0天,pH值为7至8。

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