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Treatment and reuse of textile wastewater by overland flow

机译:陆流处理和回用纺织废水

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This paper presents the findings of a laboratory scale study utilizing land treatment of textile wastewater after pretreatment by physico-chemical and biological processes. The textile industry is a growing industry in Malaysia. It contributes about 22% of the total volume of industrial wastewater generated in the country. The wastewater contains various types of pollutants from desizing, scouring, bleaching and dyeing processes. A single treatment process was found to be unsatisfactory for treating the wastewater. For example, the wastewater cannot be treated effectively by biological processes such as the activated sludge process because dyes may contain heavy metals such as chromium and lead that are toxic to microbes. Some are also refractory in nature. A combination of physico-chemical, biological and land treatment processes was attempted in this study. The treatment regime proposed would allow water reuse. The treated wastewater also complied with the regulatory effluent discharge requirements. Alum was added at a rate of 416 mg/l of wastewater as flocculant and lime at 213 mg/l as precipitant. Settling of flocs was assisted by addition of polyelectrolyte at 11 mg/l. An activated sludge process comprising a 30 l aeration tank and a 20 cm ID conical settling tank was used in the study. Oxygen was supplied to the aeration tank via eight diffusers connected to air pumps. The process was maintained for 5 weeks to establish appropriate biological populations in the aeration tank. Sludge from a domestic wastewater treatment plant was used as the seeding material in the process. The biological system was operated with a loading rate of 0.9 kg COD/m~3 and maintained at a pH between 7.0-8.5. The sludge recycles rate was 20% and nutrient addition was maintained at optimum level of BOD:N:P of 100:5:1. The nutrient addition was found to be necessary for the operation of the activated sludge system. Overland flow was effected by using two units of artificial grass beds of 62x25x5 cm~3 each planted with Axonopus afflnis and Panicum maximum. The beds were positioned at a 10° angle and operated with alternate resting periods of about 5 h under direct sunlight before another application of pretreated wastewater was carried out. The rate of land application was 1.053 cm/d. Sample of effluent from the irrigation bed was taken over 12 h after the wastewater application. The raw wastewater has high BOD, COD, SS and pH. The average pH level was 10.9 with average BOD, COD and SS values of 324, 2009 and 95 mg/l, respectively. The combined pretreatment process could improve the quality of the wastewater, i.e., BOD, COD and SS reductions averaged at 48, 488 and 27 mg/l, respectively. The BOD level was lower than the discharge limit for Class B rivers (i.e., 50 mg/l) but the COD is higher than the regulatory limit of 100 mg/l. Further reductions of BOD and COD to average values of 12 and 89 mg/l, respectively, were achieved after the land treatment. The overall performance of the treatment system indicated that land irrigation is suitable for the treatment of textile wastewater. The treated effluent has a potential for reuse in agriculture and fisheries.
机译:本文介绍了一项实验室规模研究的结果,该研究利用了通过物理化学和生物过程进行预处理的纺织废水的土地处理。纺织业是马来西亚的一个新兴产业。它贡献了该国产生的工业废水总量的约22%。废水包含退浆,精练,漂白和染色过程中的各种污染物。发现单一处理工艺不能令人满意地处理废水。例如,由于染料可能包含对微生物有毒的重金属,例如铬和铅,因此不能通过生物过程(例如活性污泥法)有效地处理废水。有些在性质上也是难熔的。本研究尝试将物理化学,生物和土地处理过程相结合。建议的处理方案将允许水的再利用。处理后的废水还符合法规要求的废水排放要求。以416 mg / l的废水浓度作为絮凝剂添加明矾,以213 mg / l的石灰作为沉淀剂加入石灰中。絮凝物的沉淀通过添加11 mg / l的聚电解质来辅助。在研究中使用了由30升曝气池和20厘米ID锥形沉降池组成的活性污泥工艺。氧气通过连接到气泵的八个扩散器供应到曝气池。维持该过程5周,以在曝气池中建立合适的生物种群。来自家用废水处理厂的污泥在该过程中用作播种材料。该生物系统以0.9kg COD / m〜3的负载速率运行,并保持在7.0-8.5之间的pH。污泥的再循环率为20%,养分添加保持在BOD:N:P的最佳水平为100:5:1。发现营养物的添加对于活性污泥系统的运行是必要的。通过使用两块62x25x5 cm〜3的人工草床(每棵种植了Axonopus afflnis和Panicum)来实现地表径流。将床以10°角放置,并在阳光直射下交替休息约5小时,然后再进行预处理废水的处理。土地施用率为1.053 cm / d。废水施用后12小时内,从灌溉床中抽取废水样品。原废水的BOD,COD,SS和pH值很高。平均pH值为10.9,BOD,COD和SS的平均值分别为324、2009和95 mg / l。组合的预处理过程可以提高废水的质量,即BOD,COD和SS的平均减少量分别为48、488和27 mg / l。 BOD水平低于B级河流的排放限值(即50 mg / l),但COD高于监管限值100 mg / l。土地处理后,BOD和COD分别进一步降低至平均值12和89 mg / l。处理系统的整体性能表明,土地灌溉适合处理纺织废水。经过处理的废水具有在农业和渔业中再利用的潜力。

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