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温暖气候下的 WWTP 设计——使用质量平衡对全规模活性污泥厂进行指南比较和参数调整。

WWTP design in warm climates - guideline comparison and parameter adaptation for a full-scale activated sludge plant using mass balancing.

机构信息

VA TECH WABAG GmbH, Dresdner Str. 87-91, 1200 Vienna, Austria.

出版信息

Water Sci Technol. 2013;67(1):224-31. doi: 10.2166/wst.2012.559.

Abstract

The ATV-A-131 guideline and the design approach published in 'Wastewater Engineering, Treatment and Reuse (WE)' are widely used for the design of activated sludge plants. They are both based on simplified steady-state assumptions tailored to the boundary conditions of temperate climates. Using design guidelines beyond the designated temperature range may lead to inappropriate results. The objectives of this paper are (1) to summarise temperature relevant differences between ATV-A-131 and WE; (2) to show the related design components; and (3) to demonstrate a procedure for design parameter adaptation for a full-scale activated sludge plant located in a warm climate region. To gain steady-state data required for wastewater treatment plant (WWTP) design according to ATV-A-131 and WE, full-scale plant data were acquired for a period of 6 months as a basis for analyses and adaptation. Mass balances were calculated for the verification of the measurements and for analysing excess sludge production. The two approaches showed relevant temperature related differences. WE default application resulted in lower deviation in the mass balance results for excess sludge production. However, with the adaptation of the heterotrophic decay rates for both approaches and the inert organic and mineral solids fraction additionally for ATV-A-131, a good fit to the observed excess sludge production could be achieved.

摘要

ATV-A-131 指南和在《废水工程、处理和再利用(WE)》中发表的设计方法广泛用于活性污泥厂的设计。它们都基于简化的稳态假设,针对温带气候的边界条件进行了调整。超出指定温度范围使用设计指南可能会导致结果不合适。本文的目的是:(1) 总结 ATV-A-131 和 WE 之间与温度相关的差异;(2) 展示相关的设计组件;(3) 展示为位于温暖气候地区的全规模活性污泥厂设计参数调整的程序。为了根据 ATV-A-131 和 WE 获得用于废水处理厂 (WWTP) 设计的稳态数据,在 6 个月的时间内获取了全规模工厂数据,作为分析和调整的基础。为了验证测量值并分析剩余污泥产量,计算了质量平衡。这两种方法显示出了与温度相关的显著差异。WE 默认应用导致剩余污泥产量的质量平衡结果偏差较小。然而,通过对两种方法的异养衰减率以及 ATV-A-131 中惰性有机和矿物质固体部分进行调整,可以很好地拟合观察到的剩余污泥产量。

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