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Effect of Activated Sludge Composition on its Dewaterability and Sticky Phase

机译:活性污泥组成对其脱水性和黏相的影响

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摘要

This research is aimed at solving two major operational issues the wastewater treatment plant of Monsanto in Antwerp was coping with at the end of 2004. At first, inexplicable periodic deteriorations of the activated sludge settling resulted frequently in sludge losses from the final clarifier. And secondly, the Centridry® installation, used to reduce the waste sludge volume by the combination of mechanical dewatering and thermal drying, was performing significantly below its designed capacity. The latter was more specifically caused by two bottlenecks, that is (i) the high vibrations of the decanter centrifuge and (ii) the unexplainable phenomenon of dryer fouling by build-up of drying solids on the dryer wall, inducing substantial operational downtime. Moreover, the investigation of this peculiar fouling phenomenon is seriously impeded by the design of the Centridry® - the design which makes it, at the same time, also a unique technology. By combining both unit operations, dewatering and drying of the sludge, in one enclosed machine, the Centridry® inherently rules out sampling and, hence, analysis of the dewatered cake leaving the centrifuge and thus entering the drying stage. The lack of information on this intermediate product forms a serious drawback from a research and optimization point of view. A 3-year study of the varying Ca++ and Na+ concentrations in the wastewater has been conducted, in relation to the changing sludge settling characteristics. Two mechanisms are demonstrated to exist by which Ca++ ions influence the bioflocculation and so the sludge settleability: (i) in accordance with the Divalent Cation Bridging Theory (DCBT), the divalent Ca++ ions exchange the monovalent Na+ ions from the sludge flocs, bridging the individual flocs into larger and stronger flocs that settle better; (ii) the low soluble CaCO3, formed in the biodegradation basin, precipitates from the water, and is enmeshed within the floc structure, making the flocs heavier and so settling better. Hence, in the case of a Ca++ depletion from the wastewater (when the only Ca++ supplying plant on site goes in shutdown), the sludge settleability starts to worsen over time as a result of (i) the floc disintegration, and (ii) the continuous wasting of the (old) heavy (CaCO3) flocs, being replaced by new grown sludge flocs without the heavy solids incorporated in the floc structure. The first objective of this research, avoiding the sludge settling to deteriorate to such an extent that solids losses manifest in the clarifier overflow, is being accomplished by adding CaCl2 to the wastewater in order to avoid the complete floc disintegration to happen when the influent is for a longer period deficient in Ca++. Conclusively, Ca++ ions are of upmost importance for the bioflocculation, and, hence, for the sludge settleability.In the second part of this research, two lab tests are introduced to (i) simulate the sludge dewatering in the decanter centrifuge (that is, to simulate the important intermediate product of the Centridry®) and (ii) to map the sticky behavior of drying sludge (that is, to make the fouling issue in the Centridry® tangible). A 4-year follow-up of the centrifugal dewaterability of the Centridry® sludge feed has been conducted at lab scale. It is emphatically demonstrated that the dryness of the dewatered sludge cake is mainly governed by the sludge CaCO3 fraction, with a high sludge inorganic fraction yielding a higher cake dryness. Up to a sludge inorganic fraction of 55%, the cake can be made ‘wet’ again by reducing the amount of inorganic clay conditioner to the Centridry® feed. Furthermore, the lab protocol to map the stickiness of the sludge provides information of equal importance to better understand the fouling issue in the dryer. The drying of sludge is, worldwide, cumbersome because of its sticky phase. When partially dried it behaves as a sticky, gluey substance that likes to cling on a dryer wall. An explanation for this physical consistency is proposed to be found in the 3-dimensional structure of extracellular polymeric substances (EPS) surrounding the micro-organisms, which achieves its strongest (plastic, pasty) configuration when the sludge is partially dried. The sticky phase, i.e., the range of dryness wherein it behaves most sticky, depends on the sludge inorganic fraction as well, with a high sludge inorganic fraction (and thus a low EPS content) resulting in a higher sludge dryness ‘needed’ to come in the sticky phase. Further, it is shown that the intrinsic stickiness of sludge can be reduced by adding pure polyaluminiumchloride (PACl) to waste sludge. It is postulated that this salient feature of PACl conditioning is due to the large Al13-clusters and their associated hydrated water. When present on the exterior of the drying flocs, these (artificially added) clusters of bound water (water shields) act as some kind of lubricant for the intrinsically sticky solids. This stickiness mitigating effect of pure PACl addition to waste sludge is a totally new application of PACl. In addition to both lab tests, a statistical model is obtained for the fouling propensity, based on a 5-year data base with operational experience. This empirical model clearly demonstrates that the sludge characteristics, resulting from the cations in the incoming wastewater, govern the fouling probability, with sludge characterized by a high inorganic fraction (excellent dewaterability) corresponding with a higher chance of dryer fouling. The second objective of this research, increasing the Centridry® capacity, is then accomplished as follows. The vibrational bottleneck is eliminated by substantially reducing the centrifuge speed of rotation, from 3165 rpm to 2500 rpm. Next, the fouling of the sludge dryer is managed by a two-fold control strategy: (i) for sludge with an inorganic fraction below a threshold of approximately 55%, a wet cake after the centrifuge is aimed for, by lowering the inorganic clay addition to the sludge feed (making ‘wet cake’); (ii) for sludge that dewaters to such a high extent that making ‘wet cake’ is not an option anymore, pure PACl is added to the sludge feed. The latter strategy is dealing with reducing the sludge’s intrinsic stickiness, whereas the former is ‘post-poning’ the sludge’s sticky phase to occur only after the drying solids have passed the most sensitive places at the entrance of the dryer before behaving most sticky. By doing so, the Centridry® capacity could be increased with 107%.In conclusion, this PhD study made the optimization of the industrial-scale Centridry® installation possible by unraveling the relation between the micro-scale activated sludge floc structure and the changing cation concentrations in the wastewater.
机译:这项研究旨在解决2004年底安特卫普孟山都废水处理厂要应对的两个主要操作问题。首先,活性污泥沉降的莫名其妙的定期恶化经常导致最终澄清池中污泥的流失。其次,用于机械脱水和热干燥相结合减少废物污泥量的Centridry®设备的性能明显低于其设计能力。后者更具体地是由两个瓶颈引起的,即(i)cent析器离心机的高振动,以及(ii)由于干燥固体在干燥器壁上堆积而造成的干燥器结垢的无法解释的现象,从而导致大量的停机时间。此外,Centridry®的设计严重阻碍了对这种特殊结垢现象的研究,而Centridry®的设计使其同时也是一项独特的技术。通过在一台封闭的机器中结合污泥的脱水和干燥这两个单元操作,Centridry®固有地排除了采样,因此排除了脱水饼离开离心机并进入干燥阶段的分析。从研究和优化的角度来看,有关该中间产品的信息的缺乏形成了严重的缺陷。与污泥沉降特性的变化有关,已对废水中Ca ++和Na +浓度变化进行了为期3年的研究。已证明存在两种机制,其中Ca ++离子影响生物絮凝,从而影响污泥的沉降性:(i)根据二价阳离子桥联理论(DCBT),二价Ca ++离子交换污泥絮凝物中的一价Na +离子,从而将污泥絮凝。将各个絮凝物分为更大,更强的絮凝物,使其沉降更好(ii)在生物降解池中形成的低溶解度CaCO3从水中沉淀出来,并渗入絮凝物结构,使絮凝物较重,沉降效果更好。因此,如果废水中的Ca ++耗尽(当现场唯一的Ca ++供应工厂关闭时),由于(i)絮凝物分解和(ii) (旧)重质(CaCO3)絮凝物的连续浪费,被新生长的污泥絮凝物取代,絮凝物结构中未包含重质固体。这项研究的第一个目标是避免污泥沉降恶化到澄清器溢流中出现固体损失的程度,这是通过向废水中添加CaCl2来实现的,从而避免了当进水进入水中时絮凝物完全分解。长期缺乏Ca ++。最终,Ca ++离子对于生物絮凝至关重要,因此对于污泥的沉降能力也至关重要。在本研究的第二部分中,引入了两个实验室测试以(i)模拟simulate析器离心机中的污泥脱水(即,模拟Centridry®的重要中间产品,以及(ii)绘制干燥污泥的粘性行为(也就是说,使Centridry®的结垢问题变得明显)。在实验室规模下对Centridry®污泥进料的离心脱水能力进行了为期4年的跟踪。有力地证明,脱水污泥饼的干燥度主要受污泥CaCO3馏分的控制,污泥中无机物含量越高,滤饼的干燥度越高。污泥中无机物含量最高为55%时,可通过减少Centridry®进料中的无机粘土调理剂的量来再次使饼变“湿”。此外,绘制污泥粘性图的实验室协议可提供同等重要的信息,以更好地了解干燥机中的结垢问题。在世界范围内,污泥的干燥由于其粘性阶段而麻烦。当部分干燥时,其表现为粘性的胶状物质,喜欢粘附在干燥机的墙壁上。提议在微生物周围的细胞外聚合物质(EPS)的3维结构中找到这种物理一致性的解释,当污泥部分干燥时,该结构可实现其最强的(塑料,糊状)构型。粘性阶段,即表现出最大粘性的干燥范围,也取决于污泥无机部分,污泥无机部分含量高(因此EPS含量低),因此需要更高的污泥干燥度在粘性阶段。此外,显示出可以通过向废污泥中添加纯聚氯化铝(PACl)来降低污泥的固有粘性。据推测,PAC1调理的显着特征是由于较大的Al13团簇及其相关的水。当存在于干燥絮状物的外部时,这些(人工添加的)束缚水簇(挡水板)充当了固有粘性固体的某种润滑剂。纯PACl添加到废泥中的这种减轻粘性的作用是PACl的全新应用。除了这两个实验室测试之外,还基于5年的操作经验数据库,获得了结垢倾向的统计模型。该经验模型清楚地表明,来自进水废水中阳离子的污泥特性决定了结垢的可能性,污泥的特点是无机物含量高(优异的脱水性),且干燥机结垢的可能性更高。这项研究的第二个目标是提高Centridry®的生产能力,如下所述。通过将离心机的旋转速度从3165 rpm降低到2500 rpm,可以消除振动瓶颈。接下来,污泥干燥器的结垢通过双重控制策略进行管理:(i)对于无机物含量低于大约55%阈值的污泥,通过降低无机黏土来达到离心后的湿饼目的。除污泥饲料外(制作“湿蛋糕”); (ii)对于高度脱水以至于不再制造“湿饼”的污泥,应在污泥进料中添加纯的PACl。后者的策略是减少污泥的固有粘性,而前者是“延迟”污泥的粘性阶段,只有在干燥的固体经过行为之后才在干燥机的入口经过最敏感的地方之后才发生最粘。这样,Centridry®的产能可以提高107%。总之,这项博士研究通过揭示微观规模的活性污泥絮体结构与阳离子变化之间的关系,使工业规模的Centridry®装置的优化成为可能。废水中的浓度。

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    Peeters Bart;

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