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Effect of activated sludge characteristics on the fouling frequency of a single stage mechanical dewatering and thermal drying process

机译:活性污泥特性对单级机械脱水和热干燥过程的污垢频率的影响

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On the wastewater treatment plant of the Monsanto Europe site in Antwerp, Belgium, two dewatering devices are used to dewater the excess wastewater sludge: (1) filter presses yielding a final cake dryness of typically 35-40% DS, and (2) a single stage process combining mechanical dewatering and thermal drying in a single compact machine yielding a significant higher final product dryness of 85-95 %DS. It is obvious that a higher capacity of the latter results in less volume of waste generated. Over the years, the operational team has been facing here two main bottlenecks, namely (1) high vibrations of the solid bowl decanter centrifuge and (2) periods of frequently fouling around the centrifuge cake outlet or somewhat further in the flash drier. The vibrations of the centrifuge were reduced (and so the first bottleneck eliminated) by simply reducing the centrifuge bowl speed in steps of 100 rpm from historical 3165 rpm to 2880 rpm. It was shown that the final reduction step from 2980 rpm to 2880 rpm resulted n a significant and spectacular reduction of the vibrations baseline. Besides this huge positive improvement, the lower G-force (83% for 2880 rpm compared to 3165 rpm) did not show any negative operational impact. After setting the centrifuge bowl speed at 2880 rpm, fouling of the system became the next bottleneck. This issue seems harder to be resolved. From time to time, frequently (daily) product build-up at the centrifuge cake outlet or further in the flash drier is experienced. In these periods, sludge feed towards the centrifuge has to be stopped frequently to remove product build-up by flushing. Through extensive research over the years, it was shown that the plugging frequency seems to be related with the type of activated sludge being made in the aerators of this WWTP. The nature of the activated sludge is mainly determined by the sludge settleability and the inorganic fraction of the sludge floes. This fraction varies significantly over time for this particular WWTP as a result of varying calcium concentrations in the wastewater: periods of 15% inorganic fractions are followed by periods with more than 30% inorganics on the sludge floes. Sludge settleability varies in accordance with these changes in inorganic fractions, with a higher inorganic fraction resulting in a heavier floe and so a better sludge settling ability. It was shown that sludge comprised of higher inorganic fractions results in a higher chance for product build up in the system. As a result of the hot gasstream (260 °C) surrounding the centrifuge cake outlet, it is impossible to take cake samples during operation. Still, cake analysis would be preferable to know how cake composition is changing in the field, and to possibly find relations with the product build-up. That's why the operational team started with regularly executing spin tube tests in the lab on centrifuge feed samples taken in the field. Those spin tube tests simulate the centrifugal dewatering by compaction in the field. Based on a one year follow up, this research shows that the inorganic fraction of the sludge fides has a significant impact on the cake dryness obtained by centrifugal compaction, with a higher inorganic fraction yielding a drier cake. Taking into account the fact that activated sludge goes through a sticky phase while being dried (somewhere in the range around 40-50%DS, depending on the literature source), this implies that the centrifuge cake dryness determines timing and place in the system where the sludge is going through the sticky phase. Hypothesis is that a "too dry" cake leaving the decanter centrifuge goes through the sticky phase at an earlier stage in the system where it seems to be more susceptible for product build up, for example at the point where the cake particles are leaving the centrifuge with high velocity and hit the centrifuge casing for the first time. In that case, in periods of sludge characterised by a higher inorganic fraction, centrif
机译:在比利时安特卫普蒙松罗欧洲现场的废水处理厂上,两种脱水装置用于脱水过量的废水污泥:(1)滤网压机,产生典型的35-40%DS的最终蛋糕干燥,(2)a单级工艺将机械脱水和热干燥在单一小型机器中,产生显着的最终产物干燥度为85-95%DS。显而易见的是,后者的高容量导致较少的废物产生。多年来,业务团队一直在这里面临两个主要的瓶颈,即(1)固体碗滗析器离心机的高振动和(2)在离心蛋糕出口周围的经常污染的时期或在闪蒸干燥器中进一步遇到。通过简单地将离心碗速度从历史3165rpm达到2880rpm的步骤降低离心碗速度,降低了离心机的振动(所以第一个瓶颈)。结果表明,从2980rpm至2880rpm的最终还原步骤导致振动基线的显着和壮观地减少。除了这种巨大的积极改善之外,较低的G力(83%为2880rpm,与3165 rpm相比)没有显示出任何负面运行影响。在将离心碗速度设定为2880 rpm后,系统的污垢成​​为下一个瓶颈。这个问题似乎难以解决。经常(每日)产品在离心蛋糕出口或进一步的闪存干燥器中积聚经常(每日)产品。在这些时期,必须经常停止向离心机馈送污泥以通过冲洗去除产品积聚。多年来通过广泛的研究,表明堵漏频率似乎与在该WWTP的曝气器中进行的活性污泥的类型有关。活性污泥的性质主要由污泥沉积性和污泥絮凝物的无机馏分决定。由于废水中的钙浓度不同,该级分随着该特定WWTP而随着时间的推移而变化:15%的无机级分,随后在污泥絮凝物上具有超过30%的无机无机级分的时间。污泥沉降性根据无机级分的这些变化而变化,具有较高的无机馏分,导致较重的剥落等更好的污泥沉降能力。结果表明,由更高的无机分数组成的污泥导致产品在系统中积聚的更高机会。由于离心机滤饼出口周围的热气流(260°C),在操作期间不可能在蛋糕样品中服用蛋糕样品。尽管如此,蛋糕分析是可以知道蛋糕组成在该领域如何变化,并且可能找到与产品积聚的关系。这就是为什么运营团队开始定期执行在该领域采集的离心机进料样品的实验室中的旋转管测试。这些旋转管试验通过在现场压实来模拟离心脱水。基于一年的跟进,该研究表明,污泥针的无机级分具有对离心压实获得的蛋糕干燥的显着影响,具有更高的无机馏分,产生干燥饼干。考虑到活性污泥在干燥时经过粘性阶段的事实(在40-50%DS的范围内的某处,根据文献来源),这意味着离心蛋糕干燥决定了系统中的时序和放置污泥正在经历粘性阶段。假设是,离开滗析器离心机的“太干”饼干通过较早阶段的粘性相位在系统中的早期阶段,似乎更容易受到产品的影响,例如在蛋糕颗粒离开离心机的点处具有高速度并首次击中离心机套管。在这种情况下,在污泥的时期,以较高的无机馏分,离心

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