首页> 外文会议>Annual conference exposition of Water Environment Federation >COMPARING BIOLOGICAL AERATED FILTER (BAF) AND ACTIVATED SLUDGE (AS) OPERATION ON FULL SCALE
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COMPARING BIOLOGICAL AERATED FILTER (BAF) AND ACTIVATED SLUDGE (AS) OPERATION ON FULL SCALE

机译:将生物充气过滤器(BAF)和活性污泥(AS)在满量程上进行比较

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To extend capacity for nitrogen removal at the Wastewater Treatment Plant in Frederikshavn (WWTP) in 1995, for an average daily flow of 4,5 MGD (16,500 m3/24 h), or a load of approx. 130,000 PE, the existing activated sludge plant (AS) was supplemented with a biological aerated filter (BAF) to upgrade treatment for the demands of the Danish Action Plan on the Aquatic Environment (8 mg/l TN, 1,5 mg TP/l). Running two full scale processes in parallel on the same wastewater and treatment objectives enabled a direct comparison in relation to operating performance, costs and experience. After screening, the wastewater is pumped a combined grit and grease chamber and 3 primary settlers. The max. hydraulic load on the pretreatment section as a whole is 10 MGD (1,530 m3/h) . During rain, some of the water can be directed through a stormwater bypass to the BAF. After final bio-treatment, the wastewater is conveyed through a 500 m sea outfall. Approx. 50% of the wastewater comes from the fish processing industry, the remaining being a mixture of other industrial and domestic wastewater. The BAF backwash sludge, generated once every 24 h in dry weather, is returned to the primary settlers, which results in a total load of approx. 1 MGD (3,000 m3/d). Sludge from primary settlers and the AS plant is finally treated in digestion tanks, in which methane gas is produced and used for generation of heat and power. The bio-treatment consists of an AS with recirculation and a BAF, to be operated in parallel in such a way that the AS was given priority over the BAF. This implies that the AS treated the total wastewater amount under a low hydraulic load whereas the BAF was on standby. The operation of the BAF can be combined in several ways, using nitrification/denitrification in all filters, or post-denitrification in 1 filter, or bottom aeration with full nitrification in all filters. Both bioreactors are equipped with multi-channel on-line meters for the parameters NO3, NO2, NH4 and PO4 as well as oxygen. The measurementss are used for control of the oxygen saturation in aeration and for addition of an external carbon source (methanol) to the anoxic tank. Approx. 60% of the sewer system in Frederikshavn is constructed as a combined sewer system with a total of 32 overflow structures, relieving the system of mixed stormwater and wastewater, which is then discharged direct into the receiving waters. To deal with these environmental nuisances in wet weather, the hydraulic capacity was increased by switching all six BAF to full nitrification by applying the bottom aeration, leading to a BAF surface load of 9.6 m3/m2/hour and a total hydraulic capacity of the WWTP during rain of 27 mgd ( 4,330 m3/hour) or 6 times average flow. To optimize the operation and expanding wet weather capacity, hydraulic capacity of the plant during rain, and control strategies for the plants were implemented for high and low flow situations. This paper discusses the experience gained from the plant operation as well as the modifications in control strategies to increase the total hydraulic capacity during rain.
机译:延长1995年Frederikshavn(WWTP)废水处理厂的氮去除能力,平均每日流量为4,5 MgD(16,500平方米/ 24小时),或约大约。 130,000 PE,现有的活性污泥厂(AS)辅以生物曝气过滤器(BAF),以升级治疗丹麦行动计划对水生环境的需求(8毫克/吨TN,1,5 Mg TP / L. )。在相同的废水和治疗目标上并行运行两个完全尺度过程,使得与运营性能,成本和经验有关的直接比较。筛选后,将废水泵送组合的砂砾和润滑脂室和3个主沉降器。最大。预处理部分的液压负载整体为10 MgD(1,530 m3 / h)。在雨中,一些水可以通过雨水旁路指向BAF。在最后生物处理后,废水通过500米的海上排出量输送。约。 50%的废水来自鱼类加工行业,剩下的是其他工业和国内废水的混合。在干燥天气中每24小时生成一次BAF反作觉污泥,返回主要定居者,这导致总负荷约为。 1 mgd(3,000 m3 / d)。来自初级定居者和植物的污泥最终在消化罐中处理,其中生产甲烷气体并用于产生热量和功率。生物处理包括与再循环和BAF一样,并以这样的方式运行,使得按照BAF优先考虑。这意味着在低液压负荷下的总废水量,而BAF在待机状态下。 BAF的操作可以在几种方式中,在所有过滤器中使用硝化/脱氮,或在1个过滤器中的脱硝,或在所有滤波器中具有完全硝化的底部通气。 BioReActors两种生物反应器配备了用于参数3,No2,NH4和PO4以及氧气的多通道在线仪表。测量用于控制通气中的氧饱和度,并加入缺氧罐的外部碳源(甲醇)。约。 Frederikshavn中的60%的下水道系统被构造为组合的下水道系统,总共32个溢流结构,减轻了混合雨水和废水系统,然后将其直接排放到接收水中。通过在潮湿的天气中处理这些环境滋扰,通过施加底部通气将所有六个BAF切换到全硝化,导致BAF表面载荷为9.6 m3 / m2 /小时,以及WWTP的总液压容量,液压容量增加在27 mgd(4,330 m3 /小时)或平均流量的雨中。为了优化运行和扩展潮湿的天气能力,雨水期间植物的液压能力,以及植物的控制策略,用于高流量情况。本文讨论了从工厂运行中获得的经验以及控制策略的修改,以提高雨中的总液压能力。

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