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Phosphate Removal from Domestic Wastewater Using Coal Bottom Ashes

机译:使用煤层灰烬从国内废水中磷酸盐去除

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A very large quantity of coal ash is produced annually in the world as a result of coal combustion. Only a small portion, less than 25% for example in Canada, however is utilized, mainly by cement industries and for road construction. The majority of it is disposed of in landfills and surface impoundments. Phosphorus (P) in natural waters is a critical nutrient and often controls the productivity of aquatic plant species. An oversupply of P can cause eutrophication in surface waters. In the effort to accelerate the utilization of coal ash and to reduce P input to surface water, coal bottom ashes have been examined as sorbent of dissolved phosphate in domestic wastewater using bench-scale lab experiments as well as full-scale field tests. It was found that bottom coal ash was in general very effective in removing P from domestic wastewater. In addition to P, the ash in packed beds removed other contaminants effectively, including total suspended solid (TSS), biological oxygen demand (BOD), ammonia nitrogen (NH3-N), total Kjeldahl nitrogen (TKN) and E. coli. The removal of E. coli was close 100% in all four cases. Batch lab experiments provide information only on intrinsic properties of a coal ash and on specific P retention mechanisms. P retention processes in a batch system were quite different from that in a flow through or a packed bed system, particularly in a field environment. The packed bed system was more complicated and involved not only physical/chemical but also biological processes. As most of these processes enhanced P retention under field conditions, batch sorption experiments conducted in lab underestimated the P retention capacity of a coal ash if it was used in a field filter bed system. In general, the P retention of a coal bottom ash in a filter bed system is affected by the physicochemical properties of the ash, the hydraulic properties of the packed bed system and the conditions f wastewaters treated.
机译:由于煤燃烧,世界上每年生产大量的煤灰。然而,在加拿大只有一小部分,小于25%,而且主要由水泥行业和道路建设使用。其中大多数是在垃圾填埋场和表面蓄水池中处置。天然水域中的磷(P)是一种关键营养素,通常控制水生植物物种的生产率。 P的供过于求可能导致表面水域中的富营养化。在加快粉煤灰的利用率,为P输入减少地表水的功夫,煤底灰已经用实验室规模的实验室试验以及全面的实地测试被检验溶解的磷酸盐吸附剂国内废水中结果发现,底部煤灰一般非常有效地从国内废水中去除P.除了P,在填充床中的灰分有效地去除其他污染物,包括总悬浮固体(TSS),生物需氧量(BOD),氨氮(NH3-N),总凯氏氮(TKN)和大肠杆菌。在所有四种情况下,除去大肠杆菌的含量接近100%。 Batch Lab实验仅提供煤灰的内在性质和特定的P保留机制。批量系统中的P保留过程与流过或填充床系统中的批量相比,特别是在现场环境中。包装的床系统更复杂,不仅涉及物理/化学,还涉及生物过程。由于大多数这些方法在现场条件下增强了P保留,但是在Lab中进行的分批吸附实验在野外过滤床系统中使用时低估了煤灰的P保留容量。通常,过滤床系统中的煤底灰的P保留受灰分的物理化学特性的影响,填充床系统的液压性能和处理的条件。

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