首页> 外文会议>Water Environment Federation 75th annual technical exhibition amp; conference (WEFTEC 2002) >METHODS FOR MEASURING NITRIFIER MAXIMUM SPECIFIC GROWTH RATE: CRUCIAL FOR PLANT CAPACITY RATING
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METHODS FOR MEASURING NITRIFIER MAXIMUM SPECIFIC GROWTH RATE: CRUCIAL FOR PLANT CAPACITY RATING

机译:测定硝化剂最大比生长速率的方法:对植物容量额定值的影响

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Nitrification kinetics is one of the most important parameters in activated sludge process designrnand determines the necessary solids retention time (SRT) and aeration tank volume to meet anrneffluent ammonia-nitrogen (NH4-N) concentration goal. The necessary SRT is directly related tornthe maximum specific growth rate of the nitrifying bacteria (μmax), a key term in the Monodrngrowth kinetics equation. Reported values for μmax vary by a factor of five. In view of thernuncertainty about nitrification kinetics, methods are needed to provide site-specific assessmentsrnof nitrification kinetics for use in plant capacity evaluation and optimization. The purpose of thernwork reported here was to evaluate three different bench-scale methods for μmax determinations.rnThe three test methods are the Low F/M SBR, High F/M, and Washout test methods. The LowrnF/M method requires operating a sequencing batch reactor (SBR) for a time period equal to atrnleast three SRTs, followed by a series of batch nitrification rate tests using the SBR mixed liquor.rnIn the High F/M test, a small seed is placed in a reactor with a wastewater sample spiked withrnNH4-N and alkalinity, and exponential increase in nitrate and nitrite (NOx-N) concentrations isrnfollowed over about a 5-7 day period. For the Washout test, a nitrifying mixed liquor is placed inrna reactor fed with wastewater spiked with NH4-N and alkalinity and the reactor NH4-N andrnNOx-N concentrations are monitored with time over about a 5-7 day period. The feed rate to thernreactor is selected so that a low enough SRT exist and the nitrifying bacteria are washout out ofrnthe reactor over time. Tests were done with all these methods using wastewater from the Renton,rnWA. and Puyallup, WA. wastewater treatment plants. The model fitting methods to obtain maxrnfrom the data obtained for each method are presented, and the results of experiments to assessrnsome key operating variables for the Low F/M and High F/M methods are presented.rnAll three methods provide reliable μmax values from test data, and advantages and disadvantagesrnof using a particular method is presented. To obtain μmax values a value for the endogenousrndecay coefficient for nitrifying bacteria is critical. Tests at temperatures ranging from 12 to 220Crnfound a 200C specific endogenous decay coefficient of 0.17 g/g-d, with a temperature correctionrnfactor of 1.03. A temperature correction factor of 1.072 was obtained for μmax. Reports onrnnitrification kinetics must include both μmax and decay coefficient values.
机译:硝化动力学是活性污泥工艺设计中最重要的参数之一,它确定必要的固体保留时间(SRT)和曝气池容积,以满足氨氮(NH4-N)浓度的目标。必要的SRT与硝化细菌的最大比生长速率(μmax)直接相关,这是Monodrngrowth动力学方程式中的一个关键术语。报告的μmax值相差五倍。鉴于硝化动力学的不确定性,需要一些方法来提供针对特定地点的评估硝化动力学,以用于工厂产能评估和优化。此处报告的工作目的是评估三种不同的台式测量方法以用于μmax测定。三种测试方法是Low F / M SBR,High F / M和Washout测试方法。 LowrnF / M方法要求运行顺序分批反应器(SBR)的时间至少等于三个SRT,然后使用SBR混合液进行一系列分批硝化率测试.rn在High F / M测试中,一粒小种子将其放置在反应器中,废水样品中掺有NH4-N和碱度,并且在大约5-7天的时间内,硝酸盐和亚硝酸盐(NOx-N)浓度呈指数增加。对于冲洗测试,将硝化混合液置于反应器中,并向其中注入了NH4-N和碱度的废水,并在约5-7天的时间内随时间监测反应器中NH4-N和rnNOx-N的浓度。选择反应器的进料速率,以使存在足够低的SRT,并且随着时间的流逝,硝化细菌会从反应器中冲出。使用伦顿(Renton,rnWA)的废水,用所有这些方法进行了测试。和华盛顿州的普亚洛普。废水处理厂。给出了从每种方法获得的数据中获得最大值的模型拟合方法,并给出了评估低F / M和高F / M方法的一些关键操作变量的实验结果。所有这三种方法均提供了可靠的μmax值数据,并介绍了使用特定方法的优缺点。为了获得μmax值,硝化细菌的内源性衰变系数值至关重要。在12至220°C的温度范围内进行测试,发现200°C的内生衰减系数为0.17 g / g-d,温度校正系数为1.03。对于μmax,获得的温度校正因子为1.072。关于硝化动力学的报告必须同时包括μmax和衰减系数值。

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