CN102159509A - Suction filtration/concentration method and suction filtration/concentration device - Google Patents
Suction filtration/concentration method and suction filtration/concentration device Download PDFInfo
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Abstract
Description
技术领域technical field
本发明涉及一种吸引过滤浓缩方法以及吸引过滤浓缩装置,更详细地说,涉及一种不使浓缩污泥再溶解,可以高效地向外部排出的吸引过滤浓缩方法以及吸引过滤浓缩装置。The present invention relates to a suction filtration concentration method and a suction filtration concentration device, and more specifically, to a suction filtration concentration method and a suction filtration concentration device capable of efficiently discharging concentrated sludge to the outside without redissolving the sludge.
背景技术Background technique
当前,在对上水进行过滤处理时所产生的污泥的浓缩步骤中,使用了利用虹吸原理及吸引泵的吸引过滤浓缩装置。该吸引过滤浓缩装置,由于在其内部具有形成过滤室的袋状的滤布,所以将所吸引的污泥(浓缩前的污泥)分离为水分和浓缩的污泥。即,污泥中包含的水分通过滤布的大量细孔,由此被引导至过滤室内,作为滤液而回收。另外,去除水分而浓缩的污泥附着在滤布的外表面,然后,进行剥离处理,向吸引过滤浓缩装置的外部排出(参照专利文献1)。Currently, a suction filtration thickening device using a siphon principle and a suction pump is used in a step of thickening sludge generated when upper water is filtered. Since the suction filtration concentration device has a bag-shaped filter cloth forming a filter chamber inside, the suctioned sludge (sludge before concentration) is separated into water and concentrated sludge. That is, the moisture contained in the sludge is guided into the filter chamber through a large number of pores of the filter cloth, and recovered as filtrate. In addition, the dehydrated and concentrated sludge adheres to the outer surface of the filter cloth, and then undergoes peeling treatment, and is discharged to the outside of the suction filtration concentration device (see Patent Document 1).
另外,在现有技术中,在将附着在这种滤布的外表面上的浓缩污泥从滤布剥离时,进行以下的(S1)~(S4)的处理。首先,将过滤浓缩槽内的未浓缩污泥向外部排出,暂时储存(S1)。这是为了不会由于将浓缩污泥溶入未浓缩污泥中而减小浓缩污泥的浓缩度。然后,通过过滤室将规定压力的空气(气体)从滤布的内部向外部输送(S2)。在滤布的外表面整体上附着浓缩污泥,将滤布的大量细孔堵塞。因此,通过输送空气,使滤布向外侧膨胀而变形,并且由于使空气通过大量细孔,由此可以将浓缩污泥向外侧强制地剥离。然后,将浓缩污泥向外部排出(S3)。利用上述(S2)而剥离的浓缩污泥会积存在过滤浓缩槽的底部。因此,必须将浓缩污泥从过滤浓缩槽去除。然后,使储存的未浓缩污泥返回至过滤浓缩槽内(S4)。Moreover, in the prior art, when peeling the concentrated sludge adhering to the outer surface of such a filter cloth from a filter cloth, the process of following (S1)-(S4) was performed. First, the non-concentrated sludge in the filter concentration tank is discharged to the outside and temporarily stored (S1). This is in order not to reduce the degree of thickening of the thickened sludge by dissolving the thickened sludge into the non-thickened sludge. Then, air (gas) at a predetermined pressure is sent from the inside of the filter cloth to the outside through the filter chamber (S2). Concentrated sludge adheres to the entire outer surface of the filter cloth, clogging a large number of fine pores of the filter cloth. Therefore, by sending air, the filter cloth is expanded and deformed outward, and the concentrated sludge can be forcibly peeled outward by allowing the air to pass through a large number of pores. Then, the concentrated sludge is discharged to the outside (S3). The concentrated sludge peeled off by said (S2) accumulates in the bottom of a filtration thickening tank. Therefore, the thickened sludge must be removed from the filter thickener. Then, the stored unconcentrated sludge is returned to the filter thickening tank (S4).
如上述所示,根据现有的吸引过滤浓缩装置,在大气中利用空气将浓缩污泥从滤布剥离。由此,不会减小污泥的浓缩度,可以将浓缩污泥从滤布剥离。此外,与浓缩污泥在滤布上的附着程度对应地,进行气压的调整。As described above, according to the conventional suction filtration concentration device, the concentrated sludge is peeled off from the filter cloth by air in the atmosphere. Thereby, the concentrated sludge can be peeled off from a filter cloth, without reducing the concentration degree of sludge. Moreover, the air pressure is adjusted according to the degree of adhesion of the concentrated sludge to the filter cloth.
但是,在这种浓缩污泥的剥离技术中,存在下述技术问题。However, there are technical problems described below in the stripping technique of such concentrated sludge.
第1,由于作为剥离用介质的空气的压缩性,所以难以达到对浓缩污泥的期望的剥离特性。例如,如果在滤布的外表面整体上附着浓缩污泥,则滤布的大量细孔也被浓缩污泥堵塞。因此,附着在外表面整体上的浓缩污泥的保形性不充分,如果在滤布和浓缩污泥之间的附着力也不均匀的状态下向滤布输送空气,则容易从滤布的一部分细孔泄漏空气。另外,如果从滤布的一部分细孔泄漏空气,则空气容易从该部分流出。即,由于空气难以从滤布的其他部分流出,所以难以将附着在其他部分上的浓缩污泥剥离。因此,在袋状的滤布的周方向上,引起剥离的不均匀性,从而在滤布上残留无法被剥离的浓缩污泥。如果浓缩污泥残留在滤布上,则必须采用例如用人手刮落残留浓缩污泥等其他方法,使浓缩污泥的处理效率降低。First, due to the compressibility of air as a medium for detachment, it is difficult to achieve desired detachment properties for concentrated sludge. For example, if concentrated sludge adheres to the entire outer surface of the filter cloth, many pores of the filter cloth will also be clogged with the concentrated sludge. Therefore, the shape retention of the thickened sludge adhering to the entire outer surface is insufficient, and if air is sent to the filter cloth in a state where the adhesion force between the filter cloth and the thickened sludge is not uniform, fine particles from a part of the filter cloth are easily The hole leaks air. In addition, if air leaks from a part of the pores of the filter cloth, the air will easily flow out from this part. That is, since air is difficult to flow out from other parts of the filter cloth, it is difficult to peel off the concentrated sludge adhering to other parts. Therefore, in the circumferential direction of the bag-shaped filter cloth, non-uniform peeling occurs, and concentrated sludge that cannot be peeled remains on the filter cloth. If the concentrated sludge remains on the filter cloth, other methods such as scraping off the remaining concentrated sludge by hand must be used to reduce the treatment efficiency of the concentrated sludge.
另外,如果不将未浓缩污泥从过滤浓缩槽排出,而在未浓缩污泥内将浓缩污泥剥离,则浓缩污泥会再溶解,因此无法将浓缩污泥高效地向外部排出。因此,如上述所示,在现有技术中,在大气中利用空气将浓缩污泥从滤布剥离。但是,在这种剥离处理中,在将浓缩污泥从滤布剥离时,产生很大噪音。因此,存在吸引式污泥浓缩装置的设置场所受到制约等问题。这是第2问题。此外,上述很大噪音的产生,其原因是例如在从滤布的内部压送空气时,伴随着空气从滤布的大量细孔喷出的喷出声。另外,剥离的浓缩污泥向过滤浓缩槽的底部落下时的碰撞声等也是原因。即,在用于将未浓缩污泥向外部排出的污泥浓缩槽内,浓缩污泥在大气中落下并与过滤浓缩槽的底部碰撞时产生该碰撞声。由于上述以过滤浓缩槽内为声源的喷出音及碰撞声,在过滤浓缩槽内回响,所以容易成为额外的噪音。In addition, if the concentrated sludge is peeled off in the non-concentrated sludge without discharging the non-concentrated sludge from the filter thickening tank, the concentrated sludge will be redissolved, so that the concentrated sludge cannot be efficiently discharged to the outside. Therefore, as mentioned above, conventionally, the concentrated sludge was peeled from the filter cloth by air in the atmosphere. However, in such peeling treatment, when the concentrated sludge is peeled off from the filter cloth, a lot of noise is generated. Therefore, there is a problem that the installation place of a suction type sludge thickening apparatus is restricted. This is the 2nd question. In addition, the generation of the above-mentioned loud noise is caused by, for example, the ejection sound of air ejected from a large number of pores of the filter cloth when the air is pressure-fed from the inside of the filter cloth. In addition, the collision sound when the stripped thickened sludge falls to the bottom of the filtration thickening tank, etc. are also causes. That is, the collision sound is generated when the concentrated sludge falls in the atmosphere and collides with the bottom of the filter concentration tank in the sludge thickening tank for discharging unconcentrated sludge to the outside. Since the above-mentioned ejection sound and collision sound, which use the filter concentration tank as the sound source, reverberate in the filter concentration tank, it is easy to become additional noise.
第3,积存在过滤浓缩槽底部的浓缩污泥成为没有保形性的形态,难以将浓缩污泥向外部排出。这是由在大气中利用空气将浓缩污泥从滤布剥离所引起的。即,浓缩污泥利用空气从滤布剥离,在阻力较小的空气中向过滤浓缩槽的底部落下并碰撞。由于该碰撞使得浓缩污泥的形状变形,作为没有保形性的沉淀物而积存在底部。在这里,所谓“保形性”,是指附着在滤布上的浓缩污泥以何种程度维持其附着时的板状形态(大小、厚度等)。例如,在剥离时的浓缩污泥作为较大的块(形状的最长部的尺寸大于或等于100mm,优选大于或等于150mm的块)而剥离,此后的步骤中其形状几乎不变形的情况下,可以判断为保形性良好。相反地,在剥离时成为较小的块,或剥离后的块分解而成为较小的块,或分解为极小的情况下,可以说保形性差。Third, the concentrated sludge accumulated at the bottom of the filter concentration tank has no shape retention, and it is difficult to discharge the concentrated sludge to the outside. This is caused by the use of air in the atmosphere to strip the thickened sludge from the filter cloth. That is, the thickened sludge is peeled from the filter cloth by air, falls to the bottom of the filter thickening tank in the air with low resistance, and collides. The shape of the thickened sludge is deformed by this collision, and it accumulates at the bottom as a sediment without shape retention. Here, "shape retention" means to what extent the concentrated sludge adhering to the filter cloth maintains the plate-like form (size, thickness, etc.) at the time of adhering. For example, when the thickened sludge at the time of peeling is peeled off as a large block (a block whose longest part of the shape is 100 mm or more, preferably 150 mm or more), and its shape is hardly deformed in the subsequent steps , it can be judged that the shape retention is good. Conversely, it can be said that the shape retention property is poor when it becomes a small block at the time of peeling, or when the peeled block is decomposed into a small block, or is decomposed into an extremely small size.
与上述技术问题相关联,在专利文献2中公开了上水污泥的浓缩方法及装置。在专利文献2所记载的方法及装置中,在污泥浓缩槽(相当于上述过滤浓缩槽)内配置平膜模块,通过利用吸引泵间歇性地吸引,从而对流入污泥浓缩槽内的上水污泥进行过滤浓缩。更详细地说,流入污泥浓缩槽内的上水污泥的水分,通过平膜模块的细孔而作为滤液被回收。另一方面,无法通过细孔的上水污泥附着在平膜模块的外表面,由此形成浓缩浓度25%左右的浓缩污泥。然后,利用鼓风机向平膜模块的内部间歇性地压送空气或水。利用该间歇性地压送的空气或水,在未浓缩的上水污泥中,使附着在平膜模块的外表面上的浓缩污泥剥离。剥离的浓缩污泥在未浓缩的上水污泥中沉降,积存在污泥浓缩槽的底部。然后,利用设置在污泥浓缩槽的底部的浓缩污泥分离过滤网,捕捉浓缩污泥,同时将未浓缩污泥向外部排出。如上述所示,在污泥浓缩槽内将浓缩污泥和未浓缩污泥分离。然后,使用螺旋输送机,将积存在污泥浓缩槽的底部的上水污泥向外部排出。In connection with the technical problem described above, Patent Document 2 discloses a method and an apparatus for concentrating sewage sludge. In the method and device described in Patent Document 2, a flat membrane module is arranged in a sludge thickening tank (equivalent to the above-mentioned filter thickening tank), and by intermittent suction by a suction pump, the upper surface of the sludge flowing into the sludge thickening tank is sucked. Water sludge is filtered and concentrated. More specifically, the moisture of the upper water sludge flowing into the sludge thickening tank passes through the pores of the flat membrane module and is collected as filtrate. On the other hand, the sewage sludge that cannot pass through the fine pores adheres to the outer surface of the flat membrane module, thereby forming concentrated sludge with a concentrated concentration of about 25%. Then, air or water is intermittently pressure-fed to the inside of the flat-membrane module by a blower. The concentrated sludge adhering to the outer surface of the flat membrane module is peeled off from the unconcentrated upper water sludge by the intermittently pressure-fed air or water. The stripped concentrated sludge settles in the unconcentrated upper water sludge and accumulates at the bottom of the sludge thickening tank. Then, the thickened sludge is captured by the thickened sludge separation filter installed at the bottom of the sludge thickening tank, and the unthickened sludge is discharged to the outside. As mentioned above, thickened sludge and non-thickened sludge are separated in the sludge thickening tank. Then, the upper water sludge accumulated in the bottom of the sludge thickening tank is discharged to the outside using a screw conveyor.
如上述所示,在专利文献2中,公开了在液体中(上水污泥)利用空气或水对浓缩污泥进行剥离的剥离技术,可以解决上述第1至第3技术问题。但是,在专利文献2的过滤浓缩装置中,即使附着在平膜模块的外表面上的浓缩污泥的结块(块或层)成为结块片(从滤布或膜的表面以较大的块形状剥离的浓缩污泥),可以以结块片的方式将浓缩污泥从平膜模块的外表面剥离,但剥离的浓缩污泥的结块片,容易受到从散气管喷出的气泡的搅拌(起泡)影响,成为层状而容易破碎。As mentioned above, Patent Document 2 discloses a stripping technique for stripping concentrated sludge using air or water in a liquid (upstream sludge), which can solve the above-mentioned first to third technical problems. However, in the filter concentration device of Patent Document 2, even if the agglomeration (block or layer) of the concentrated sludge attached to the outer surface of the flat membrane module becomes an agglomerate sheet (from the surface of the filter cloth or membrane in a larger Concentrated sludge peeled off in the shape of lumps), the concentrated sludge can be peeled off from the outer surface of the flat membrane module in the form of agglomerated sheets, but the agglomerated sheets of the peeled concentrated sludge are easily affected by the air bubbles ejected from the diffuser pipe. Affected by stirring (foaming), it becomes layered and easily broken.
即,专利文献2的装置停留在使用利用吸引泵的平膜模块对污泥进行过滤浓缩的技术阶段。换言之,在污泥附着于平膜模块的外表面上时,污泥的浓缩度较高而大于或等于20%。但是,相反地,为了使浓缩污泥的剥离容易,而“间歇性地”进行吸引泵的吸引。因此,必须使附着在平膜模块的外表面上的污泥产生疏密。即,在这种状态下附着在滤布上的浓缩污泥的结块(块或层),在剥离处理前具有不会再溶解的程度的保形性,但在剥离后,必定容易成为柔软且小的形状(小片)、或者不具有形状的状态。另外,根据专利文献2,为了使浓缩污泥的剥离容易,而“间歇性地”供给空气或水,使过滤膜反复膨胀收缩。与此同时,在平膜模块的外侧进行充气(即,上述的“起泡”)。并且,在未浓缩污泥排出时,在结块片的浓缩污泥之间流过未浓缩污泥。因此,剥离后积存于污泥浓缩槽的底部的柔软且较小疏密的结块片的浓缩污泥,较强地受到上述影响,使结块片破碎成层状。因此,在专利文献2的过滤浓缩装置中,在浓缩污泥排出前结块片再溶解,无法高效地取出浓缩污泥。That is, the device of Patent Document 2 is still at the technical stage of filtering and concentrating sludge using a flat membrane module using a suction pump. In other words, when the sludge is attached to the outer surface of the flat membrane module, the concentration of the sludge is as high as 20% or more. However, conversely, in order to facilitate the peeling of the concentrated sludge, the suction by the suction pump is performed "intermittently". Therefore, the sludge attached to the outer surface of the flat membrane module must be densified. That is, the agglomeration (agglomerate or layer) of the concentrated sludge adhering to the filter cloth in this state has shape retention to the extent that it will not redissolve before the peeling treatment, but it must easily become soft after peeling. And a small shape (small piece), or a state without a shape. In addition, according to Patent Document 2, in order to facilitate the peeling of the concentrated sludge, air or water is supplied "intermittently", and the filter membrane is repeatedly expanded and contracted. At the same time, aeration takes place on the outside of the flat-membrane module (ie, the above-mentioned "bubbling"). And, when the non-concentrated sludge is discharged, the non-concentrated sludge flows between the concentrated sludge of the agglomerated sheet. Therefore, the thickened sludge of soft and relatively small agglomerated pieces accumulated in the bottom of the sludge thickening tank after peeling is strongly affected by the above-mentioned influence, and the agglomerated pieces are broken into layers. Therefore, in the filtration concentration device of Patent Document 2, the agglomerated pieces are redissolved before the concentrated sludge is discharged, and the concentrated sludge cannot be efficiently taken out.
此外,难以使用专利文献1的虹吸式过滤浓缩装置,在未浓缩污泥中对浓缩污泥进行剥离处理。其原因是,如果在未浓缩污泥中对浓缩污泥进行剥离,则附着在滤布的外表面上的浓缩污泥会溶入未浓缩污泥中。另外,在结块化的状态(污泥附着在滤布上时的块或层的状态)下,无法剥离浓缩污泥。另外,在使积存于污泥浓缩槽的底部的浓缩污泥维持其保形性的状态下,无法将其向外部排出。In addition, it is difficult to use the siphon type filter concentration device of Patent Document 1 to perform peeling treatment of concentrated sludge in non-concentrated sludge. This is because the concentrated sludge adhering to the outer surface of the filter cloth dissolves in the non-concentrated sludge when the concentrated sludge is peeled off in the non-concentrated sludge. In addition, in the state of agglomeration (the state of lumps or layers when sludge adheres to the filter cloth), the concentrated sludge cannot be peeled off. In addition, the concentrated sludge accumulated in the bottom of the sludge thickening tank cannot be discharged to the outside while maintaining its shape retention.
即,专利文献1中公开的使用作为过滤系统的滤布的虹吸式过滤浓缩装置,与专利文献2所示的使用过滤膜的情况不同,捕捉原本粒径比滤布的孔小的固体部分。因此,在滤布的表面形成使固体部分凝结·密集的膜层,对比该滤布的孔小的固体部分进行过滤(所谓动态过滤)。在使用滤布的虹吸式过滤浓缩装置中,即使吸引力没那么强也可以过滤,因此,不会在膜表面上密集固体部分而阻碍过滤,另外,不需要用于排除该固体部分的间歇运转(即,由于反清洗引起的过滤浓缩运转中断)。另外,由于是低压吸引,所以附着的浓缩污泥的浓缩浓度较低,并且附着的固体部分之间的附着强度较弱。因此,在没有吸引力的情况下,无法维持固体部分之间的附着,在利用滤布以虹吸式对污泥进行浓缩过滤的情况下,如果在过滤浓缩槽内的未浓缩污泥中,将附着在滤布的外表面上的浓缩污泥利用压缩空气等进行剥离,则由于浓缩污泥(固体部分)之间的附着力较弱而分散,并溶入未浓缩污泥中,使浓缩度降低,上述预测是本技术领域中的技术常识。That is, the siphon filter concentrator disclosed in Patent Document 1 using a filter cloth as a filter system captures solids whose particle size is originally smaller than the pores of the filter cloth, unlike the case of using a filter membrane shown in Patent Document 2. Therefore, a film layer in which solid parts are condensed and densely formed is formed on the surface of the filter cloth, and solid parts smaller than the pores of the filter cloth are filtered (so-called dynamic filtration). In a siphon filter concentration device using a filter cloth, filtration is possible even if the suction force is not so strong, so solids do not accumulate on the surface of the membrane to impede filtration, and intermittent operation to remove the solids is not required (ie, interruption of the filter concentration operation due to backwashing). In addition, due to low-pressure suction, the concentrated concentration of the attached concentrated sludge is low, and the adhesion strength between the attached solid parts is weak. Therefore, in the absence of suction, the adhesion between solid parts cannot be maintained, and in the case of thickening and filtering sludge with a filter cloth in a siphon type, if the unconcentrated sludge in the filter thickening tank will The concentrated sludge attached to the outer surface of the filter cloth is peeled off by compressed air, etc., and the concentrated sludge (solid part) is dispersed due to the weak adhesion between the concentrated sludge and dissolves into the unconcentrated sludge to make the concentration The above prediction is common knowledge in this technical field.
专利文献1:日本特开2006-218455号公报Patent Document 1: Japanese Patent Laid-Open No. 2006-218455
专利文献2:日本特开2000-325998号公报Patent Document 2: Japanese Patent Laid-Open No. 2000-325998
发明内容Contents of the invention
因此,鉴于上述现有的技术问题,本发明的目的在于,提供一种吸引过滤浓缩方法以及吸引过滤浓缩装置,其不会使浓缩污泥再溶解,并可以高效地向外部排出。即,提供一种吸引过滤浓缩方法以及吸引过滤浓缩装置,其通过在规定吸引压力下连续吸引,使附着在滤布上的浓缩污泥的结块变硬变大,并在剥离时可以连续压送水,由此,可以在具有不会再溶解的硬度和大小以及保形性的状态下,将浓缩污泥剥离。特别地,其目的在于,提供一种吸引过滤浓缩方法以及吸引过滤浓缩装置,其即使在水中使浓缩污泥移动,也可以减少再溶解。Therefore, in view of the aforementioned conventional technical problems, an object of the present invention is to provide a suction filtration concentration method and a suction filtration concentration device that can efficiently discharge the concentrated sludge to the outside without redissolving the sludge. That is, to provide a suction filtration concentration method and a suction filtration concentration device, which can make the agglomeration of the concentrated sludge attached to the filter cloth hard and large by continuous suction under a predetermined suction pressure, and can be continuously pressed when peeling off. By sending water, the concentrated sludge can be peeled off in a state of hardness, size, and shape retention that cannot be redissolved. In particular, an object thereof is to provide a suction filtration concentration method and a suction filtration concentration device capable of reducing redissolution even when concentrated sludge is moved in water.
为了实现上述目的,根据本发明,提供一种如下所示的吸引过滤浓缩方法以及吸引过滤浓缩装置。In order to achieve the above object, according to the present invention, a suction filtration concentration method and a suction filtration concentration device as shown below are provided.
〔1〕一种吸引过滤浓缩方法,其使污泥在过滤浓缩槽内通过滤布而进行吸引过滤,从而使滤液通过滤布内部的过滤室而被回收,并且使污泥作为浓缩污泥而附着在滤布的外表面上,该方法具有下述步骤:污泥供给步骤,在该步骤中,向过滤浓缩槽内供给污泥;过滤浓缩步骤,在该步骤中,在过滤浓缩槽内对所供给的污泥进行过滤浓缩;浓缩污泥剥离步骤,在该步骤中,将过滤浓缩后的浓缩污泥从滤布的外表面剥离;以及浓缩污泥排出步骤,在该步骤中,将剥离的浓缩污泥向过滤浓缩槽的外部排出,所述过滤浓缩步骤具有下述步骤,即,利用即使在未浓缩污泥中使浓缩污泥剥离也可以维持保形性的程度的规定吸引压力,连续地进行吸引,从而使浓缩污泥附着在滤布的外表面上,所述浓缩污泥剥离步骤具有下述步骤,即,通过在所供给的未浓缩的污泥中,经由过滤室向滤布连续地以规定时间压送水,从而将附着在滤布的外表面上的浓缩污泥(滤渣)剥离。〔1〕A suction filtration concentration method, which makes the sludge pass through the filter cloth in the filter concentration tank to perform suction filtration, so that the filtrate is recovered through the filter chamber inside the filter cloth, and the sludge is collected as concentrated sludge. Attached to the outer surface of the filter cloth, the method has the following steps: a sludge supply step, in which the sludge is supplied to the filter concentration tank; a filter concentration step, in which the sludge is supplied to the filter concentration tank The supplied sludge is subjected to filtration and concentration; a concentrated sludge stripping step in which the filtered and concentrated concentrated sludge is stripped from the outer surface of the filter cloth; and a concentrated sludge discharge step in which the stripped The concentrated sludge is discharged to the outside of the filter concentration tank. The filter concentration step has a step of using a predetermined suction pressure to the extent that the shape retention can be maintained even if the concentrated sludge is peeled off from the unconcentrated sludge, The suction is continuously performed so that the concentrated sludge adheres to the outer surface of the filter cloth, and the concentrated sludge stripping step has the following steps: The cloth continuously presses water for a predetermined time to peel off the concentrated sludge (filter residue) adhering to the outer surface of the filter cloth.
〔2〕根据〔1〕所述的吸引过滤浓缩方法,其中,所述浓缩污泥排出步骤具有在未浓缩污泥中将积存于过滤浓缩槽的底部的结块状片的浓缩污泥捞出的步骤。[2] The suction filtration concentration method according to [1], wherein the step of discharging the concentrated sludge includes removing the concentrated sludge accumulated in the bottom of the filter concentration tank from the unconcentrated sludge. A step of.
〔3〕根据〔1〕或〔2〕所述的吸引过滤浓缩方法,其中,所述浓缩污泥排出步骤,在以规定次数反复实施由所述过滤浓缩步骤和所述浓缩污泥剥离步骤构成的循环后进行,在各循环中的所述过滤浓缩步骤前,具有利用所述污泥供给步骤向过滤浓缩槽内补给污泥的步骤。[3] The suction filtration concentration method according to [1] or [2], wherein the step of discharging the concentrated sludge consists of the step of concentration by filtration and the step of stripping the concentrated sludge after repeating a predetermined number of times. It is carried out after the cycle, and before the above-mentioned filtration concentration step in each cycle, there is a step of supplying sludge to the filter concentration tank by the above-mentioned sludge supply step.
〔4〕根据〔1〕或〔2〕所述的吸引过滤浓缩方法,其中,所述浓缩污泥排出步骤在所述过滤浓缩步骤中并行进行,并且,在所述过滤浓缩步骤前,具有利用所述污泥供给步骤向过滤浓缩槽内补给污泥的步骤。[4] The suction filtration concentration method according to [1] or [2], wherein the concentrated sludge discharge step is performed in parallel in the filtration concentration step, and prior to the filtration concentration step, there is a The sludge supply step is a step of supplying sludge into the filter thickening tank.
〔5〕根据〔1〕至〔4〕中任一项所述的吸引过滤浓缩方法,其中,在所述浓缩污泥剥离步骤中向所述过滤室内输送的水,利用被回收至所述过滤室内的滤液。[5] The suction filtration concentration method according to any one of [1] to [4], wherein the water sent to the filter chamber in the step of stripping the concentrated sludge is recycled to the filter Indoor filtrate.
〔6〕一种吸引过滤浓缩装置,其使污泥通过滤布而进行吸引过滤,从而使滤液通过滤布内部的过滤室而被回收,并且使污泥作为浓缩污泥而附着在滤布的外表面上,该吸引过滤浓缩装置具有:污泥供给单元,其向过滤浓缩槽内供给污泥;过滤浓缩单元,其在过滤浓缩槽内对所供给的污泥进行过滤浓缩;浓缩污泥剥离单元,其将过滤浓缩后的浓缩污泥从滤布的外表面剥离;以及浓缩污泥排出单元,其将剥离的浓缩污泥向过滤浓缩槽的外部排出,所述过滤浓缩单元具有下述单元,该单元利用即使在未浓缩污泥中使浓缩污泥剥离也可以维持保形性的程度的规定吸引压力,连续地进行吸引,从而使浓缩污泥附着在滤布的外表面上,所述浓缩污泥剥离单元具有下述单元,该单元通过在所供给的未浓缩的污泥中经由过滤室向滤布连续地以规定时间压送水,从而将附着在滤布的外表面上的浓缩污泥(滤渣)剥离。[6] A suction filtration concentration device that performs suction filtration by allowing sludge to pass through a filter cloth, whereby the filtrate is recovered through a filter chamber inside the filter cloth, and the sludge is attached to the bottom of the filter cloth as concentrated sludge On the outer surface, the suction filter concentration device has: a sludge supply unit that supplies sludge into the filter concentration tank; a filter concentration unit that filters and concentrates the supplied sludge in the filter concentration tank; A unit that peels the concentrated sludge after filtration and concentration from the outer surface of the filter cloth; and a concentrated sludge discharge unit that discharges the peeled concentrated sludge to the outside of the filter concentration tank, the filter concentration unit has the following units , this unit utilizes a predetermined suction pressure that can maintain shape retention even if the concentrated sludge is peeled off in the unconcentrated sludge, and continuously sucks the concentrated sludge to the outer surface of the filter cloth, said The concentrated sludge stripping unit has a unit for continuously pressure-feeding water to the filter cloth for a predetermined time through the filter chamber among the supplied unconcentrated sludge, thereby removing the concentrated sludge adhering to the outer surface of the filter cloth. Mud (filter residue) stripping.
〔7〕根据〔6〕所述的吸引过滤浓缩装置,其中,所述浓缩污泥排出单元具有在未浓缩污泥中将积存于过滤浓缩槽的底部的结块片的浓缩污泥捞出的单元。[7] The suction filtration concentration device according to [6], wherein the concentrated sludge discharge unit has a mechanism for removing agglomerated sludge accumulated at the bottom of the filter concentration tank from the unconcentrated sludge. unit.
〔8〕根据〔6〕所述的吸引过滤浓缩装置,其中,所述浓缩污泥排出单元是带把手的网眼状托盘,其配置在所述过滤浓缩槽的底部,该把手具有从所述过滤浓缩槽的上部开口向上方延伸的长度。[8] The suction filtration concentration device according to [6], wherein the concentrated sludge discharge unit is a mesh-shaped tray with a handle, which is arranged at the bottom of the filtration concentration tank, and the handle has The length that the upper opening of the concentration tank extends upwards.
〔9〕根据〔6〕所述的吸引过滤浓缩装置,其中,所述浓缩污泥排出单元是从所述过滤浓缩槽的底部通过所述过滤浓缩槽的上部开口向外部延伸的斗式输送机,使从所述过滤浓缩槽的底部向外部移动的输送机面朝上配置。[9] The suction filtration concentration device according to [6], wherein the concentrated sludge discharge unit is a bucket conveyor extending from the bottom of the filtration concentration tank through the upper opening of the filtration concentration tank to the outside. , so that the conveyor moving from the bottom of the filter concentration tank to the outside faces upward.
〔10〕根据〔6〕所述的吸引过滤浓缩装置,其中,在可以经由过滤室向滤布连续地压送水的上述单元中,多个水供给管在所述滤布的高度方向上,以彼此不同的高度与所述过滤室连通。[10] The suction filtration concentration device according to [6], wherein, in the unit capable of continuously pressure-feeding water to the filter cloth through the filter chamber, a plurality of water supply pipes are arranged in the height direction of the filter cloth to The heights different from each other communicate with the filter chamber.
根据本发明所涉及的吸引过滤浓缩方法以及吸引过滤浓缩装置,可以得到下述优越效果,即,不会在排出前使浓缩污泥再溶解,并可以高效地将浓缩污泥向外部排出。即,具有下述效果:通过在规定吸引压力下连续吸引,使浓缩污泥的结块变硬变大,并在剥离时连续压送水,由此,可以在具有不会再溶解的硬度和大小以及保形性的状态下,将浓缩污泥剥离。特别地,根据本发明的方法及装置,即使在水中使浓缩污泥移动,也可以防止再溶解。According to the suction filtration concentration method and the suction filtration concentration device according to the present invention, it is possible to efficiently discharge the concentrated sludge to the outside without redissolving the concentrated sludge before discharge. That is, it has the following effects: by continuously sucking under a predetermined suction pressure, the agglomeration of the concentrated sludge becomes hard and large, and the water is continuously pressure-fed when peeling off, thereby achieving a hardness and a size that will not be redissolved. And in the state of shape retention, the concentrated sludge is stripped. In particular, according to the method and apparatus of the present invention, redissolution can be prevented even if concentrated sludge is moved in water.
附图说明Description of drawings
图1是本发明的吸引过滤浓缩方法的流程图。Fig. 1 is a flow chart of the suction filtration concentration method of the present invention.
图2A是表示本发明的吸引过滤浓缩装置的一个实施方式的示意图。Fig. 2A is a schematic diagram showing one embodiment of the suction filtration concentration device of the present invention.
图2B是表示本发明的吸引过滤浓缩装置的其他实施方式的示意图。Fig. 2B is a schematic diagram showing another embodiment of the suction filtration concentration device of the present invention.
图2C是表示本发明的吸引过滤浓缩装置的其他实施方式的示意图。Fig. 2C is a schematic diagram showing another embodiment of the suction filtration concentration device of the present invention.
图2D是表示本发明的吸引过滤浓缩装置的其他实施方式的示意图。Fig. 2D is a schematic diagram showing another embodiment of the suction filtration concentration device of the present invention.
图2E是表示本发明的吸引过滤浓缩装置的其他实施方式的示意图。Fig. 2E is a schematic diagram showing another embodiment of the suction filtration concentration device of the present invention.
图2F是表示本发明的吸引过滤浓缩装置的其他实施方式的示意图。Fig. 2F is a schematic diagram showing another embodiment of the suction filtration concentration device of the present invention.
图2G是表示本发明的吸引过滤浓缩装置的其他实施方式的示意图。Fig. 2G is a schematic diagram showing another embodiment of the suction filtration concentration device of the present invention.
图3是表示本发明的吸引过滤浓缩装置中的过滤板的侧面的示意图。Fig. 3 is a schematic view showing a side surface of a filter plate in the suction filtration concentration device of the present invention.
图4是表示在本发明的吸引过滤浓缩装置中,利用过滤浓缩槽悬挂支撑多个过滤板的状态的作为局部俯视图的示意图。4 is a schematic partial plan view showing a state in which a plurality of filter plates are suspended and supported by a filter concentration tank in the suction filtration concentration device of the present invention.
图5是表示在本发明的吸引过滤浓缩装置中,将多个过滤板相邻配置的状态的斜视图。Fig. 5 is a perspective view showing a state in which a plurality of filter plates are arranged adjacent to each other in the suction filtration concentration device of the present invention.
图6A是针对本发明的吸引过滤浓缩装置的滤布,表示膨胀中的状态的概略图。Fig. 6A is a schematic diagram showing a state in which the filter cloth of the suction filtration concentration device of the present invention is inflated.
图6B是针对本发明的吸引过滤浓缩装置的滤布,表示过滤中的状态的概略图。Fig. 6B is a schematic diagram showing a state of filtration with respect to the filter cloth of the suction filtration concentration device of the present invention.
图7是表示本发明的吸引过滤浓缩装置的一个实施方式中的处理流程的示意图。Fig. 7 is a schematic diagram showing a process flow in one embodiment of the suction filtration concentration device of the present invention.
图8是表示本发明的吸引过滤浓缩装置的其他实施方式中的处理流程的示意图。Fig. 8 is a schematic diagram showing a processing flow in another embodiment of the suction filtration concentration device of the present invention.
图9A是本发明的吸引过滤浓缩方法的流程图。Fig. 9A is a flowchart of the suction filtration concentration method of the present invention.
图9B是本发明的吸引过滤浓缩方法的流程图。Fig. 9B is a flowchart of the suction filtration concentration method of the present invention.
图10是表示本发明的其他实施方式所涉及的吸引过滤浓缩装置的示意图。Fig. 10 is a schematic diagram showing a suction filtration concentration device according to another embodiment of the present invention.
图11A是表示本发明的吸引过滤浓缩装置中的剥离作用的示意图。Fig. 11A is a schematic diagram showing the peeling action in the suction filtration concentration device of the present invention.
图11B是表示本发明的吸引过滤浓缩装置中的剥离作用的示意图。Fig. 11B is a schematic diagram showing the peeling action in the suction filtration concentration device of the present invention.
图12是本发明的实施例所涉及的吸引过滤浓缩装置的概略结构图。Fig. 12 is a schematic configuration diagram of a suction filtration concentration device according to an embodiment of the present invention.
图13是关于图12的试验装置的试验结果,以剥离压力为参数表示剥离时间和剥离率之间的关系的曲线图。FIG. 13 is a graph showing the relationship between the peeling time and the peeling rate using the peeling pressure as a parameter regarding the test results of the test device in FIG. 12 .
符号的说明Explanation of symbols
2:净水槽,4:污泥供给管,6:污泥供给泵,8:污泥供给阀,10、10A、10B、10C、10D、10E:吸引过滤浓缩装置,12:过滤浓缩槽,13:平面部,14、14A、14B、14C、14D、14E:过滤板,15:水平管,16:吸引部,18:滤布,20:浓缩污泥剥离部,22:侧壁,24:污泥供给/排出管,26:污泥供给/排出阀,28:污泥供给/排出泵,30:浓缩污泥排出管,31:吸引管,32:浓缩污泥排出阀,33:吸引阀,34、34A、34B、34C、34D、34E、:分配管,35:真空泵,36:滤液储存槽,38:滤液排出管,40:滤液排出阀,42:水流入管,44:水流入阀,46:液体输送泵,47:切换阀,48:过滤框,50:支撑板,54:螺旋弹簧,56、57:上边,58、59:下边,60、61、62、63:侧边,64:延长部,65:支撑部件,66A:卡合板,67:未浓缩污泥排出管,68:未浓缩污泥排出阀,69:内侧面,70、70A、72、72A:引导板、74:线迹,76:过滤室,78:孔眼,80:把手,82:托盘,84a、84b、84c:斗式输送机,86:辊(驱动辊),88、90、92:辊,89a、89b、89c:铲斗,108a、108b、108c:分支管,112a、112b、112c:排出阀,113:抽水泵,114:挠性软管,120:吸引泵,150:剥离压力调整阀,152:原液槽,154:原液泵,156:浓缩污泥排出泵,158:过滤浓缩槽,160:洗净水泵,162:洗净水槽,164:洗净水压调整阀,166:压缩机,168:原液排出泵,C:净水,D:间隔,F:滤液,H:规定高度,P:凸出量,R:原水,S:移动量,W:浓缩污泥,X:污泥,T1:污泥供给步骤,T2:过滤浓缩步骤,T3:浓缩污泥剥离步骤,T4:浓缩污泥排出步骤。2: clean water tank, 4: sludge supply pipe, 6: sludge supply pump, 8: sludge supply valve, 10, 10A, 10B, 10C, 10D, 10E: suction filter concentration device, 12: filter concentration tank, 13 : Plane section, 14, 14A, 14B, 14C, 14D, 14E: Filter plate, 15: Horizontal tube, 16: Suction section, 18: Filter cloth, 20: Concentrated sludge stripping section, 22: Side wall, 24: Dirt Sludge supply/discharge pipe, 26: Sludge supply/discharge valve, 28: Sludge supply/discharge pump, 30: Concentrated sludge discharge pipe, 31: Suction pipe, 32: Concentrated sludge discharge valve, 33: Suction valve, 34, 34A, 34B, 34C, 34D, 34E,: distribution pipe, 35: vacuum pump, 36: filtrate storage tank, 38: filtrate discharge pipe, 40: filtrate discharge valve, 42: water inflow pipe, 44: water inflow valve, 46 : Liquid delivery pump, 47: Switching valve, 48: Filter frame, 50: Support plate, 54: Coil spring, 56, 57: Upper side, 58, 59: Lower side, 60, 61, 62, 63: Side side, 64: Extension, 65: Support member, 66A: Engaging plate, 67: Non-thickened sludge discharge pipe, 68: Non-thickened sludge discharge valve, 69: Inner side, 70, 70A, 72, 72A: Guide plate, 74: Wire trace, 76: filter chamber, 78: eyelet, 80: handle, 82: tray, 84a, 84b, 84c: bucket conveyor, 86: roller (drive roller), 88, 90, 92: roller, 89a, 89b, 89c: bucket, 108a, 108b, 108c: branch pipe, 112a, 112b, 112c: discharge valve, 113: suction pump, 114: flexible hose, 120: suction pump, 150: stripping pressure adjustment valve, 152: stock solution Tank, 154: stock solution pump, 156: thickened sludge discharge pump, 158: filter concentration tank, 160: washing water pump, 162: washing water tank, 164: washing water pressure adjustment valve, 166: compressor, 168: stock solution Discharge pump, C: Clean water, D: Interval, F: Filtrate, H: Specified height, P: Projection amount, R: Raw water, S: Movement amount, W: Concentrated sludge, X: Sludge, T1: Sewage Sludge supply step, T2: filtration thickening step, T3: thickened sludge stripping step, T4: thickened sludge discharge step.
具体实施方式Detailed ways
下面,参照附图,详细说明本发明所涉及的吸引过滤浓缩方法及装置的实施方式,本发明并不限定于上述实施方式。此外,下面,以将在净水厂、下水厂等产生的污泥作为过滤浓缩对象的情况为例进行说明。Hereinafter, embodiments of the suction filtration concentration method and apparatus according to the present invention will be described in detail with reference to the drawings, but the present invention is not limited to the above embodiments. In addition, below, the case where the sludge produced|generated in a water purification plant, a sewage plant, etc. are made into filtration concentration object is demonstrated as an example.
〔1〕本发明的吸引过滤浓缩方法的构成:[1] The composition of the suction filtration concentration method of the present invention:
本发明的吸引过滤浓缩方法如图1所示,使污泥在过滤浓缩槽内通过滤布而进行吸引过滤,由此,使滤液通过滤布内部的过滤室而进行回收,并且使污泥作为浓缩污泥而附着在滤布的外表面上,在该方法中,具有下述步骤,即:污泥供给步骤(T1),在该步骤中,向过滤浓缩槽内供给污泥;过滤浓缩步骤(T2),在该步骤中,在过滤浓缩槽内对所供给的污泥进行过滤浓缩;浓缩污泥剥离步骤(T3),在该步骤中,将过滤浓缩后的浓缩污泥从滤布的外表面剥离;以及浓缩污泥排出步骤(T4),在该步骤中,将剥离的浓缩污泥向过滤浓缩槽的外部排出,上述过滤浓缩步骤(T2)具有下述步骤,即,利用即使在未浓缩污泥中使浓缩污泥剥离也可以维持保形性的程度的规定吸引压力,连续地进行吸引,从而使浓缩污泥附着在滤布的外表面上,上述浓缩污泥剥离步骤(T3)具有下述步骤,即,通过在所供给的未浓缩的污泥中,经由过滤室向滤布连续地以规定时间压送水,从而将附着在滤布的外表面上的滤渣剥离。The suction filtration concentration method of the present invention is shown in Figure 1, makes sludge pass through filter cloth in filter concentration tank and carries out suction filtration, thereby, makes filtrate pass through the filter chamber inside filter cloth and reclaim, and make sludge as The sludge is concentrated and attached to the outer surface of the filter cloth. In this method, the following steps are included: a sludge supply step (T1) in which sludge is supplied to the filter concentration tank; a filter concentration step (T2), in this step, the supplied sludge is filtered and concentrated in the filter concentration tank; the concentrated sludge stripping step (T3), in this step, the concentrated sludge after the filter concentration is removed from the filter cloth peeling of the outer surface; and a concentrated sludge discharge step (T4) in which the stripped concentrated sludge is discharged to the outside of the filter concentration tank, the above-mentioned filter concentration step (T2) has the following steps, that is, using In the non-thickened sludge, the predetermined suction pressure of the degree that the shape retention can be maintained even when the concentrated sludge is peeled off is continuously sucked, so that the concentrated sludge is attached to the outer surface of the filter cloth, and the above-mentioned concentrated sludge peeling step (T3 ) has a step of peeling off filter residue adhering to the outer surface of the filter cloth by continuously pressure-feeding water to the filter cloth for a predetermined time through the filter chamber in the supplied unconcentrated sludge.
根据本发明的方法,附着在滤布上的浓缩污泥的结块不会形成为层状,可以使结块变硬,进而可以作为较大的结块片的浓缩污泥而剥离。因此,即使在未浓缩污泥中,结块片的浓缩污泥发生再溶解的情况也较少,可以高效地取出浓缩污泥。即,通过非间歇性地在规定吸引压力下连续地吸引含有过滤浓缩对象物的被处理液,并使其通过滤布,从而使被处理液被过滤,通过设置在滤布上的大量细孔。如上述所示将滤液回收。另一方面,过滤浓缩对象物无法通过大量细孔而附着在滤布的外表面上,由此被浓缩,也确保与滤布之间的附着力。换言之,通过非间歇性且连续地进行吸引,由此使浓缩污泥(滤渣)在滤布的外表面上形成致密化且较硬的浓缩污泥结块。According to the method of the present invention, the agglomeration of the concentrated sludge adhering to the filter cloth can be hardened without forming a layer, and can be peeled off as thickened sludge of a larger agglomerate sheet. Therefore, even in non-thickened sludge, the concentrated sludge of agglomerated pieces is rarely redissolved, and the concentrated sludge can be efficiently taken out. That is, the liquid to be treated is filtered by continuously sucking the liquid to be treated containing the object of filtration concentration under a predetermined suction pressure non-intermittently, and passing it through the filter cloth, and passing through a large number of fine pores provided on the filter cloth. . The filtrate was recovered as indicated above. On the other hand, the object to be filtered and concentrated cannot pass through a large number of pores and adheres to the outer surface of the filter cloth, thereby being concentrated, and the adhesion to the filter cloth is also ensured. In other words, by non-intermittently and continuously suctioning, the concentrated sludge (filter residue) is formed into dense and relatively hard concentrated sludge agglomerates on the outer surface of the filter cloth.
另外,在过滤浓缩结束后,在过滤浓缩后的被处理液中,从附着有浓缩污泥的面的相反侧的面,向滤布连续地以规定时间压送水。此时,压送的水(以下,适当称为“压送水”),要通过滤布的大量细孔而向被处理液中流出。但是,浓缩污泥附着在滤布的外表面整体上,堵塞滤布的大量细孔。因此,在附着有浓缩污泥的外表面上,同样地承载被处理液的液压。即,在向过滤室内压送的水的水压至少克服被处理液的液压之前,将附着在滤布的外表面上的浓缩污泥向被处理液中按压。因此,在向过滤室内压送的水的水压至少克服被处理液的液压之前,不会将浓缩污泥从滤布的表面剥离。由此,过滤室内的压送水的压力上升,与此同时使滤布膨胀。In addition, after the completion of filtration and concentration, in the liquid to be treated after filtration and concentration, water is continuously pressure-fed to the filter cloth for a predetermined time from the surface opposite to the surface on which the concentrated sludge is attached. At this time, the pressure-fed water (hereinafter, appropriately referred to as "pressure-fed water") passes through a large number of pores of the filter cloth and flows out into the liquid to be treated. However, the concentrated sludge adheres to the entire outer surface of the filter cloth and clogs many fine pores of the filter cloth. Therefore, the hydraulic pressure of the liquid to be treated is similarly carried on the outer surface to which the concentrated sludge adheres. That is, the concentrated sludge adhering to the outer surface of the filter cloth is pressed into the liquid to be treated until the hydraulic pressure of the water pressure-fed into the filter chamber at least overcomes the hydraulic pressure of the liquid to be treated. Therefore, the concentrated sludge will not be peeled off from the surface of the filter cloth until the hydraulic pressure of the water pressure-fed into the filter chamber at least overcomes the hydraulic pressure of the liquid to be treated. Thereby, the pressure of the pressure-fed water in the filter chamber rises, and at the same time, the filter cloth is expanded.
在这里,由于压送水是液体的水,所以与空气等气体相比,具有非压缩性的性质。因此,可以防止现有的利用大气中的空气进行剥离所引起的情况。即,在现有的空气压送的情况下,由于过滤室内的局部压力上升,所以从与该部分接近的滤布,将附着在滤布的表面上的浓缩污泥局部地向被处理液中按压。可以防止被按压的浓缩污泥从滤布的表面剥离,仅从此后开放的细孔继续流出空气等情况。换言之,在本发明中,可以在压送水的水压在过滤室内同样地达到规定压力的定时,在滤布的整体上,将附着在滤布的表面上的浓缩污泥一齐向被处理液中按压。因此,可以使浓缩污泥(滤渣)从滤布的表面沿周方向均匀地剥离。Here, since the pressure-fed water is liquid water, it has incompressibility compared with gas such as air. Therefore, it is possible to prevent the conventional peeling by air in the atmosphere. That is, in the case of conventional air pressure feeding, since the local pressure in the filter chamber rises, the concentrated sludge adhering to the surface of the filter cloth is locally injected into the liquid to be treated from the filter cloth close to this part. press. It is possible to prevent the pressed concentrated sludge from peeling off from the surface of the filter cloth, and air continue to flow out only from the pores opened thereafter. In other words, in the present invention, the concentrated sludge adhering to the surface of the filter cloth can be poured into the liquid to be treated at the same time when the hydraulic pressure of the pressure-fed water reaches a predetermined pressure in the filter chamber as a whole. press. Therefore, the concentrated sludge (filter residue) can be uniformly peeled off from the surface of the filter cloth in the circumferential direction.
另外,在本发明中,由于污泥在规定吸引压力下连续地被吸引,所以在滤布的表面形成致密化且较硬的浓缩污泥,与滤布之间的附着力也增加。因此,即使停止吸引并被一齐向被处理液中按压,也不会使浓缩污泥成为层状而一边破碎一边剥离。即,在以致密化且较硬的状态附着于滤布上的浓缩污泥的结块剥离时,作为较硬且较大的浓缩污泥的结块片,而积存在过滤浓缩槽的未浓缩污泥中。因此,在从过滤浓缩槽排出时,浓缩污泥的结块片不易破碎成较小或再溶解,可以将浓缩污泥高效且简单地向过滤浓缩槽的外部排出。In addition, in the present invention, since the sludge is continuously sucked under a predetermined suction pressure, dense and hard concentrated sludge is formed on the surface of the filter cloth, and the adhesion to the filter cloth is also increased. Therefore, even if the suction is stopped and the sludge is pressed all at once into the liquid to be treated, the concentrated sludge will not be peeled off while being broken into layers. That is, when the lumps of concentrated sludge attached to the filter cloth in a densified and relatively hard state are peeled off, the unconcentrated sludge accumulated in the filter concentration tank will be treated as relatively hard and large lumps of concentrated sludge. in the sludge. Therefore, when discharged from the filter concentration tank, the agglomerated pieces of the concentrated sludge are not easily broken into small pieces or redissolved, and the concentrated sludge can be efficiently and easily discharged to the outside of the filter concentration tank.
在本发明中,作为吸引过滤方式,可以采用虹吸式吸引过滤方法、或使用吸引泵的吸引过滤方法。In the present invention, as the suction filtration method, a siphon suction filtration method or a suction filtration method using a suction pump can be employed.
下面,与本发明的吸引过滤浓缩装置相对应,说明本发明的吸引过滤浓缩方法,在这里,使用虹吸式的吸引过滤浓缩装置及方法进行说明。Next, the suction filtration concentration method of the present invention will be described corresponding to the suction filtration concentration device of the present invention. Here, the suction filtration concentration device and method of the siphon type will be described.
〔2〕本发明的吸引过滤浓缩装置的结构:(2) The structure of the suction filtration concentration device of the present invention:
本发明的吸引过滤浓缩装置如图2A~图2G所示,使污泥通过滤布而进行虹吸式吸引过滤,从而使滤液通过滤布内部的过滤室而被回收,并且使污泥作为浓缩污泥(滤渣)而附着在滤布的外表面上,该装置作为虹吸式吸引过滤浓缩装置10而构成,具有:污泥供给单元,其向过滤浓缩槽内供给污泥;过滤浓缩单元,其在过滤浓缩槽内对所供给的污泥进行过滤浓缩;浓缩污泥剥离单元,其将过滤浓缩的浓缩污泥从滤布的外表面剥离;以及浓缩污泥排出单元,其将剥离的浓缩污泥向过滤浓缩槽的外部排出,上述过滤浓缩单元具有下述单元,即,利用即使在未浓缩污泥中使滤渣剥离也可以维持保形性的程度的规定吸引压力,连续地进行吸引,从而使浓缩污泥(滤渣)附着在滤布的外表面上,上述浓缩污泥剥离单元具有下述单元,即,通过在所供给的未浓缩的污泥中,经由过滤室向滤布连续地以规定时间压送水,从而将附着在滤布的外表面上的滤渣剥离。The suction filtration concentration device of the present invention is shown in Fig. 2A ~ Fig. 2G, makes sludge pass through filter cloth and carries out siphon type suction filtration, thereby makes filtrate pass through the filter chamber inside filter cloth to be recovered, and makes sludge become concentrated sewage. Mud (filter residue) is attached to the outer surface of the filter cloth, and the device is constituted as a siphon suction
具体地说,虹吸式吸引式过滤浓缩装置10如图2A~图2E所示,大致由下述部分构成,即:过滤浓缩槽12,其收容作为过滤浓缩对象的污泥;过滤板14,其配置在过滤浓缩槽12内;吸引部16,其吸引污泥;浓缩污泥剥离部20,其将浓缩污泥剥离,该浓缩污泥是利用吸引部16而附着在设置于过滤板14上的滤布18外表面的;以及浓缩污泥捞出部23,其用于将由浓缩污泥剥离部20剥离并积存在过滤浓缩槽12底部的结块片的浓缩污泥排出。另外,根据需要还具有:浓缩污泥排出管30以及浓缩污泥排出阀32,它们用于将结块的小片或液体状的浓缩污泥排出。通过将该浓缩污泥排出阀32打开,从而使积存在过滤浓缩槽12的底部的结块的小片或液体状的浓缩污泥在重力的作用下落下,通过浓缩污泥排出管30向外部排出。此外,浓缩污泥排出管30以及浓缩污泥排出阀32,为可以使小片的浓缩污泥排出的大口径,例如优选公称直径大于或等于200A(大于或等于200mmφ)。Specifically, the siphon type suction
(污泥供给步骤/污泥供给单元)(Sludge supply step/Sludge supply unit)
污泥供给步骤(单元)是向作为过滤浓缩槽的过滤浓缩槽12内供给污泥的步骤(单元)。即,污泥供给单元大致由图2A~图2F所示的污泥供给/排出管24、污泥供给/排出阀26、以及污泥供给/排出泵28等构成。另外,图1所示的污泥供给步骤(T1)中的污泥供给处理,是通过上述污泥供给/排出管24、污泥供给/排出阀26、以及污泥供给/排出泵28等实现的。但是,并不限定与此。另外,也可以将污泥供给泵和排出泵分别设置而作为不同的系统。A sludge supply process (means) is a process (means) of supplying sludge into the
更具体地说,过滤浓缩槽12是有底的矩形剖面的容器,具有可以在内部设置后述说明的过滤板14的容积。在过滤浓缩槽12的侧壁22上,与向过滤浓缩槽12内供给污泥的污泥供给/排出管24的一端连通。另外,经由设置在污泥供给/排出管24的中途的污泥供给/排出阀26,与可进行正反动作的污泥供给/排出泵28连接。由此,通过打开污泥供给/排出阀26,使污泥供给/排出泵28动作,从而可以向过滤浓缩槽12内供给污泥。另外,通过使污泥供给/排出泵28相反地动作,可以将过滤浓缩槽12内的未浓缩的污泥从过滤浓缩槽12排出。More specifically, the
另外,在图2A~图2F中,污泥通过污泥供给/排出管24向过滤浓缩槽12内供给,但如图2G所示,也可以在过滤浓缩槽12的上游侧设置净水槽2,将原水R预先分离为净水C和污泥X,将污泥X向过滤浓缩槽12供给。污泥X是通过打开污泥供给阀8,使污泥供给泵6动作,从而通过污泥供给管4向过滤浓缩槽12供给的。分离出的净水C进一步在下游侧被另外处理,例如作为饮用水而利用。此外,净水槽2可以是当前已知的构造,通过放入原水,并向槽内添加例如凝结剂,从而将原水分离为净水和污泥。In addition, in FIGS. 2A to 2F, the sludge is supplied to the
(过滤浓缩步骤/过滤浓缩单元)(Filter Concentration Step/Filter Concentration Unit)
过滤浓缩步骤(单元)是将由污泥供给步骤(单元)供给的污泥进一步在过滤浓缩槽内进行过滤浓缩的步骤(单元)。即,图1所示的过滤浓缩步骤(T2),是利用即使在未浓缩污泥中使浓缩污泥(滤渣)剥离也可以维持保形性的程度的规定吸引压力,连续地进行吸引的步骤。而且,是通过这种连续的吸引,使浓缩污泥(滤渣)附着在滤布的外表面上的步骤。该过滤浓缩步骤(T2)中的过滤浓缩处理,例如通过具有图2A~图2G所示的过滤板14、吸引管31、吸引阀33、分配管34、真空泵35等的过滤浓缩单元而实现。但是,并不限定于此。The filtration concentration step (unit) is a step (unit) in which the sludge supplied from the sludge supply step (unit) is further subjected to filtration concentration in the filtration concentration tank. That is, the filtration concentration step (T2) shown in FIG. 1 is a step of continuously performing suction using a predetermined suction pressure that maintains shape retention even if the concentrated sludge (filter residue) is peeled off from the unconcentrated sludge. . And, it is a step of making the concentrated sludge (filter residue) adhere to the outer surface of the filter cloth by this continuous suction. The filtration concentration treatment in this filtration concentration step ( T2 ) is realized by, for example, a filtration concentration unit having a
具体地说,过滤板14在其上部经由分配管34与滤液储存槽36连接。滤液储存槽36设置在过滤浓缩槽12外部,滤液排出管38的一端与滤液储存槽36连通并连接。滤液排出管38向铅垂下方延伸,在中途设置有滤液排出阀40。Specifically, the
另外,分配管34和滤液排出管38通过滤液储存槽36连接为倒U字状。由此,利用虹吸原理,将在过滤浓缩槽12内过滤后的滤液向过滤浓缩槽12外排出。另外,吸引管31是在分配管34上分支出而连接的,并且经由在中途设置的吸引阀33与真空泵35连接。由此,如果在将吸引阀33打开的状态下,使真空泵35动作,则在过滤浓缩槽12内进行处理的液体被吸引至分配管34内。如上述所示,可以利用虹吸原理,通过滤液排出管38将滤液向外部排出。In addition, the
在这里,虹吸式的吸引压力,与由分配管34和滤液排出管38构成的倒U字状管的端部和顶部之间的高度差相对应而确定。但是,在吸引过滤浓缩装置10中实际使用的吸引压力优选为0.02Mpa至0.08MPa。通过利用这种比较低压的吸引压力,连续地吸引过滤浓缩槽12内的污泥,可以使浓缩污泥附着在滤布18的外表面。特别地,通过连续地吸引,可以得到下述程度的浓缩污泥相对于滤布18的外表面的附着力、硬度,即,成为即使由浓缩污泥剥离部20将浓缩污泥从滤布18剥离,也可以在过滤浓缩槽12内的未浓缩污泥中,维持作为结块片的浓缩污泥的保形性的程度。连续吸引的标准为,直至附着于滤布上的浓缩污泥的厚度成为5mm至20mm、优选8mm至15mm左右为止,连续地持续吸引。作为此时的吸引持续时间,为30分钟至4小时左右。另外,本发明中的吸引方式并不限定于虹吸式,也可以利用真空泵等吸引泵产生上述吸引压力。Here, the suction pressure of the siphon is determined corresponding to the height difference between the end and the top of the inverted U-shaped pipe composed of the
此外,过滤板14如图5所示,在过滤浓缩槽12内,以平面部13沿上下方向延伸的状态配置多个。即,多个过滤板14(14A至14E)隔着规定的间隔D而彼此相邻配置。相邻的过滤板14彼此的间隔D越小,可设置在过滤浓缩槽12内的过滤板14的片数越多,由此可以增大总过滤面积。但是,可以从不使相邻的过滤板14接触,同时最大限度地确保过滤面积的角度出发,确定相邻的过滤板14彼此的间隔。其原因是,为了将附着在过滤板14的滤布18上的浓缩污泥剥离,需要使滤布18膨胀。即,其原因是,由于该滤布18的膨胀,使得滤布18向相邻的过滤板14凸出,所以滤布18可能与相邻的过滤板14接触,使过滤面积减小,从而无法充分地过滤。In addition, as shown in FIG. 5 , a plurality of
(浓缩污泥剥离步骤/浓缩污泥剥离单元)(Thickened sludge stripping step/Thickened sludge stripping unit)
浓缩污泥剥离步骤(单元),是将由过滤浓缩步骤(单元)进行过滤浓缩后的浓缩污泥从滤布的外表面剥离的步骤(单元)。该浓缩污泥剥离步骤(单元)具有下述步骤(单元),即:利用即使在未浓缩污泥中使浓缩污泥(滤渣)剥离也可以维持保形性的程度的规定吸引压力,连续地进行吸引,从而使浓缩污泥(滤渣)附着在滤布的外表面上。作为该浓缩污泥剥离单元(浓缩污泥剥离部20),例如可以举出具有图2A~图2G所示的水流入管42、水流入阀44、液体输送泵46等单元。另外,过滤板14也可以成为构成浓缩污泥剥离单元的部件。并且,图1所示的该浓缩污泥剥离步骤(T3)中的浓缩污泥的剥离,通过上述水流入管42、水流入阀44、液体输送泵46等浓缩污泥剥离单元而实现。但是,并不限定与此。The concentrated sludge peeling step (unit) is a step (unit) of peeling the concentrated sludge filtered and concentrated in the filtration concentration step (unit) from the outer surface of the filter cloth. This thickened sludge stripping step (unit) has the following step (unit): using a predetermined suction pressure to the extent that the shape retention can be maintained even if the thickened sludge (filter residue) is stripped from the non-thickened sludge, continuously Suction is performed so that concentrated sludge (filter residue) adheres to the outer surface of the filter cloth. As this concentrated sludge detachment means (concentrated sludge detachment part 20), the unit which has the
具体地说,水流入管42的一端与滤液储存槽36连通并连接,在其中途连接水流入阀44和液体输送泵46。由此,如果在将水流入阀44打开的状态下,使液体输送泵46动作,则通过水流入管42以及分配管34,将水(压送水)向形成在过滤板14内部的过滤室76(在后面说明)供给。在本实施方式中,作为压送水而利用滤液储存槽36的滤液,为此设置有切换阀47。如上述所示,在将浓缩污泥从滤布18剥离时,使滤布18膨胀。在此情况下,为了使附着的浓缩污泥作为结块片而从滤布18剥离,可以使用液体输送泵46以及水流入阀44,对剥离压力以及/或者剥离时间进行调整。Specifically, one end of the
在这里,在浓缩污泥剥离步骤(单元)中,以污泥为过滤浓缩对象的情况下,重要的是以规定时间连续地压送作为剥离介质的水,而不是间歇性地输送。即,通过将作为剥离介质的水以规定时间连续地压送,从而即使在未浓缩污泥中使附着于滤布上的浓缩污泥剥离,也可以不使浓缩污泥溶入未浓缩污泥中,而是作为结块片维持保形性。此外,在浓缩污泥剥离步骤中,作为向过滤室76内压送的水,优选利用如上述所示被回收至过滤室76内的滤液。即,作为浓缩污泥的剥离介质的水,优选使用由滤布18对污泥进行过滤并被回收至过滤室76内的滤液。Here, in the concentrated sludge stripping step (unit), when the sludge is the subject of filtration and concentration, it is important to continuously press-feed the water as the stripping medium for a predetermined time, not intermittently. That is, by continuously pressure-feeding water as a stripping medium for a predetermined time, even if the concentrated sludge adhering to the filter cloth is stripped in the non-concentrated sludge, the concentrated sludge can not be dissolved in the non-concentrated sludge. , but maintains shape retention as an agglomerated sheet. In addition, in the concentrated sludge stripping step, it is preferable to use the filtrate recovered in the
另外,过滤板14如图2A~图2G、图3所示,大致由下述部分构成,即:过滤框48;支撑板50,其配置在过滤框48的内部;袋状的滤布18,其在内部收容支撑板50;以及多个螺旋弹簧54,其设置在过滤框48和支撑板50之间。过滤框48形成为中空的矩形形状,具有上边56、下边58以及上下边之间的两侧边60、62。过滤板14利用上边56的两端部被过滤浓缩槽12的内侧面悬挂支撑。更详细地说,如图3及图4所示,在上边56的两端部分别设置延长部64。另一方面,在过滤浓缩槽12的内侧面68上,设置有向内部凸出的一对引导板70(70A)、72(72A)。另外,延长部64(64A、64B、64C)的端部配置在一对引导板70(70A)、72(72A)之间。另外,固定在延长部64(64A、64B、64C)的上表面上的卡合板66A,载置于一对引导板70(70A)、72(72A)的上表面上。由此,各过滤板14悬挂支撑在过滤浓缩槽12上。相邻的过滤板14彼此的间隔,是通过选择用于悬挂支撑过滤板14的一对引导板70(70A)、72(72A)而确定的。但是,也可以适当改变相邻的过滤板14的间隔D。作为这种情况,例如可以举出下述情况,即:与浓缩污泥在滤布18上的附着量、由吸引产生的负压的大小、滤布18的横向的分割长度等相对应,而选择用于悬挂支撑过滤板14的一对引导板70(70A)、72(72A)。In addition, the
支撑板50由网子或筛网等构成,形成为矩形形状。另外,在支撑板50上设置有大量的小开口。另外,在支撑板50的表面上,设置有沿其上下方向延伸的凹凸部(未图示)。在该支撑板50的凹部和滤布18的内表面之间,形成多条沿支撑板50的上下方向延伸的滤液流路。这种支撑板50优选由硬质的材质形成,从而在实质上不会产生与滤布18向污泥中浸渍的情况相伴的支撑板50的平面内的伸长,或者损害支撑板50的平面性的变形。并且,优选由硬质的材质形成,从而在实质上不会产生与使滤布18膨胀的情况相伴的支撑板50的平面内的收缩,或者损害支撑板50的平面性的变形。例如,更优选树脂制。具体地说,例如可以是聚乙烯制或EVA树脂制。通过采用这种材质,在使滤布18向污泥中长时间浸渍,或使滤布18膨胀的情况下,可以使利用后述说明的螺旋弹簧54向过滤板14(支撑板50)作用的张力持续地保持大致一定。The
滤布18优选为化学纤维制或金属制,在化学纤维制的情况下,特别优选尼龙、聚丙烯、聚酯。例如,关于纤维的种类,可以使用洗净效果好且难以引起筛眼堵塞的单丝的线。如果重视强度及微粒子的捕捉性,则也可以采用将多根纤维捻合而形成的多丝。此外,所采用的线的直径,只要考虑所要求的滤布18的强度、延伸率等,针对经线、纬线分别适当确定即可。关于布料的编织方法,可以使用洗净效果高且难以引起筛眼堵塞的缎织。如果重视筛眼的粗细度或微粒子的捕捉性,则也可以使用平织、斜纹织。另外,关于织线的密度,只要考虑所要求的滤布18的强度、延伸率等,针对经线、纬线分别适当确定即可。例如,滤布18可以形成为将一对矩形状的布体重合并将周缘部彼此缝合而成的袋状。或者也可以形成为将一片矩形状的布体以相对的缘部彼此重合的方式弯折,并将周缘部彼此缝合而成的袋状。在该滤布18的周围,设置多个孔眼78,螺旋弹簧54的一端钩挂在孔眼78中。The
另外,如图2A~图2G、图3所示,在滤布18上,设置有多条沿过滤浓缩槽12的上下方向延伸的线迹74,利用各线迹74,将滤布18与收容在其内部的支撑板50一体地缝合。由此,如图6A、图6B所示,在滤布18的内部,形成由相邻的线迹74隔开的过滤室76。在分支管34的前端,连接有设置在滤布18内上部的水平管15(参照图3)。在该水平管15上,朝下设置有与各过滤室76连通的流出孔(未图示)。并且,作为剥离介质的水通过分支管34以及设置在水平管15上的流出孔,向各过滤室76内压送。此外,图6A是表示膨胀中的状态的示意图,并且图6B是表示过滤中的状态的示意图。In addition, as shown in FIGS. 2A to 2G and FIG. 3 , on the
另外,在滤布18的上下方向的长度较长,过滤浓缩槽12的污泥的液压差较大的情况下,也可以设置为使多个水供给管沿滤布18的高度方向以彼此不同的高度与过滤室连通。例如,在利用作为剥离介质的水将附着在滤布18上的浓缩污泥剥离时,存在在滤布18上承受负载,过滤浓缩槽12的污泥的液压沿高度方向变化的情况。在这种情况下,如果将多个水供给管沿滤布的高度方向设置为相同高度,则无法将浓缩污泥沿滤布的高度方向同样地剥离,难以作为结块片而剥离,容易产生弊端。但是,作为可以经由过滤室向滤布连续地压送水的水压送单元,通过将多个水供给管沿滤布18的高度方向设置在彼此不同的高度上,可以防止该弊端。另外,作为其他例子,例如可以向液压低的滤布18的上部压送水压相对较低的水,向液压高的滤布18的下部压送水压相对较高的水。但是,与水输送时的压力(0.1~1.0MPa)相比,上下方向的液压差较小,在不成为问题的情况下也可以忽略。In addition, when the length of the
在这里,螺旋弹簧54是用于将向过滤板(具体地说,支撑板50)作用的张力调整为持续地大致一定的部件。具体地说,如图3所示,多个螺旋弹簧54配置在过滤框48的侧边60和滤布18的侧边61之间、过滤框48的侧边62和滤布18的侧边63之间、过滤框48的下边58和滤布18的下边59之间、以及过滤框48的上边56和滤布18的上边57之间。分别设置在过滤框48的两侧边部以及上下边部的相邻的螺旋弹簧54彼此的间隔,与滤布18的大小、附着的浓缩污泥量等相对应而适当设定即可。具体地说,各螺旋弹簧54的一端部钩挂在滤布18的孔眼78中,并且其另一端部固定在过滤框48的侧边60、62、上边56及下边58上。从耐腐蚀性的角度出发,优选上述多个螺旋弹簧54为SUS制。另外,通常,螺旋弹簧54在过滤板14的周围配置几十个,过滤板14的片数例如为几十片,因此优选不采用特制件,而是采用标准件。Here, the
此外,在过滤板14(14A、14B、14C、14D、14E)以及滤布18为大型且重量大于或等于规定量的情况下,如图3及图5所示,在过滤框48的上边56和滤布18的上边57之间,取代螺旋弹簧54,而设置刚性高的支撑部件65,其将大重量的滤布18以及支撑板50固定而不使其伸缩。其原因是,如果滤布18以及支撑板50的重量变大为大于或等于规定量,使位于滤布18上侧的螺旋弹簧54伸长,使位于滤布18下侧的螺旋弹簧54收缩,则向滤布18以及支撑板50作用的张力不能成为一定值,滤布18以及支撑板50因较小的外力而移动,因此,对于利用吸引使浓缩污泥在滤布18上附着、利用水输送将浓缩污泥剥离的动作,造成恶劣影响。In addition, when the filter plate 14 (14A, 14B, 14C, 14D, 14E) and the
(浓缩污泥排出步骤/浓缩污泥排出单元)(Concentrated sludge discharge step/Concentrated sludge discharge unit)
浓缩污泥排出步骤(单元)是将剥离的浓缩污泥向过滤浓缩槽的外部排出的步骤(单元)。在本实施方式中,浓缩污泥排出步骤(单元)不将过滤浓缩槽12内的未浓缩污泥排出。作为浓缩污泥排出单元,可以举出图2A~图2G所示的污泥供给/排出阀26、污泥供给/排出泵28、污泥供给/排出管24、浓缩污泥捞出部23(网眼状托盘82)等。利用上述浓缩污泥排出单元,实现图1所示的浓缩污泥排出步骤(T4)中的浓缩污泥排出处理。The thickened sludge discharge step (unit) is a step (unit) of discharging the stripped thickened sludge to the outside of the filter thickening tank. In the present embodiment, the concentrated sludge discharge step (means) does not discharge the unconcentrated sludge in the
浓缩污泥排出步骤(单元)具有在未浓缩污泥中将积存于过滤浓缩槽的底部的结块片的浓缩污泥捞出的步骤(单元)。通过如上述所示构成,不会如现有技术那样将未浓缩污泥从过滤浓缩槽排出,而是可以在未浓缩污泥中将积存于过滤浓缩槽的底部的结块片的浓缩污泥捞出。即,可以进行浓缩污泥的连续处理。另外,在具有不会再溶解的硬度和大小以及保形性的状态下,即使被剥离的浓缩污泥(结块片的浓缩污泥)在水中移动,也可以以不会再溶解的状态排出。因此,不会使浓缩污泥的浓缩度降低,可以简单且高效地将浓缩污泥从过滤浓缩槽向外部排出。到此为止,污泥的过滤浓缩作业完成。向过滤浓缩槽12外部排出的浓缩污泥,被另外的脱水机进一步浓缩,再次形成为结块,进行焚烧或填埋处理。The thickened sludge discharge process (unit) has the process (unit) of taking out the thickened sludge of agglomerated sheet accumulated in the bottom of a filter thickening tank among unconcentrated sludge. With the configuration as described above, the unconcentrated sludge is not discharged from the filter thickening tank as in the prior art, but the thickened sludge accumulated in the bottom of the filter thickening tank can be collected in the unconcentrated sludge fish out. That is, continuous treatment of concentrated sludge can be performed. In addition, in a state having hardness, size, and shape retention that cannot be redissolved, even if the peeled concentrated sludge (concentrated sludge of agglomerated pieces) moves in water, it can be discharged in a state that cannot be redissolved . Therefore, the concentrated sludge can be easily and efficiently discharged from the filter thickening tank to the outside without reducing the degree of concentration of the concentrated sludge. So far, the sludge filtration and concentration operation is completed. The concentrated sludge discharged to the outside of the
此外,在浓缩污泥排出步骤中,根据需要,利用上述结块片的浓缩污泥的排出步骤之外的其他工序,使积存在过滤浓缩槽12的底部的小片的结块或者液体状的浓缩污泥,通过浓缩污泥排出管30而排出,以将这些浓缩污泥向过滤浓缩槽12外部排出。此时,也可以将过滤浓缩槽12内的未浓缩污泥预先排出,或与这些浓缩污泥一起从浓缩污泥排出管30排出。In addition, in the step of discharging the concentrated sludge, if necessary, by using other steps than the step of discharging the concentrated sludge of the above-mentioned agglomerated pieces, the small pieces of agglomerated or liquid concentrated sludge accumulated at the bottom of the
作为上述浓缩污泥排出单元,可以举出图2A~图2G、图10所示的浓缩污泥捞出部23、网眼状托盘82、斗式输送机84(84a、84b、84c)等。并且,利用上述浓缩污泥排出单元,实现浓缩污泥排出步骤的浓缩污泥排出处理。具体地说,浓缩污泥捞出部23配置在过滤浓缩槽12的底部,具有用于捞出由浓缩污泥剥离部20剥离并积存在过滤浓缩槽12的底部的结块片的浓缩污泥的作用。本实施方式中的浓缩污泥捞出部23具有带把手80的网眼状托盘82,该把手80具有从过滤浓缩槽12的上部开口向上方延伸的程度的长度。As said concentrated sludge discharge means, the concentrated
在这里,优选网眼状托盘82的大小为,覆盖过滤浓缩槽12的底部整体,以捞出积存在过滤浓缩槽12的底部的浓缩污泥而不会漏掉。网眼的大小只要按照与浓缩污泥的结块片的大小关系适当确定即可。但是,优选以下述方式选择网眼的大小,即,在使用把手80将网眼状托盘82向上方抬起时,浓缩污泥中的水分通过筛网而被去除,并且,浓缩污泥被保持在筛网上。Here, the size of the mesh-shaped
此外,为了将网眼状托盘82向其上部拉出,在过滤浓缩槽12中设置确保比过滤板14的间隔大部分(例如比图5中的D宽的部位),并在该部分处设置网眼状托盘82。在过滤板14的下方,在过滤浓缩槽12的底部设置金属丝网状的带式输送机,利用该金属丝网状带式输送机,接收被剥离的结块片的浓缩污泥,并水平输送至网眼状托盘82。可以取代该输送机,通过设置铲运机而将被剥离的结块状的浓缩污泥,输送至网眼状托盘82。在过滤浓缩槽12的空间有富余的情况下,也可以将网眼状托盘82设置在过滤板14的正下方,使用把手80,使网眼状托盘82自身在过滤浓缩槽12的底部沿横向移动。然后,可以将网眼状托盘82向上方抬起,并将网眼状托盘82向外部取出。In addition, in order to pull out the mesh-shaped
另外,作为其他实施方式,如图10所示,也可以采用斗式输送机84(84a、84b、84c),以将积存在过滤浓缩槽12的底部的结块片形态的浓缩污泥W向外部排出。例如可以举出下述斗式输送机84作为一个例子,该斗式输送机84从过滤浓缩槽12的底部通过过滤浓缩槽12的上部开口向外部延伸,使从过滤浓缩槽12的底部向外部移动的输送机面朝向上方而配置。In addition, as another embodiment, as shown in FIG. 10 , bucket conveyors 84 (84a, 84b, 84c) may also be used to transfer the concentrated sludge W in the form of agglomerated sheets accumulated at the bottom of the
例如,在由于向过滤浓缩槽12内配置过滤板14而存在空间上的制约的情况下,如图10所示,优选采用3组斗式输送机84a、84b、84c。For example, when there is a space restriction due to the arrangement of the
具体地说,在第1组斗式输送机84a中,一侧作为驱动辊86而构成,在配置于过滤浓缩槽12的底部的两个辊86、88之间,架设输送机。另外,构成为在该架设的输送机上设置有多个铲斗89a,输送机沿过滤浓缩槽12的底面移动。另外,在第2组斗式输送机84b中,一侧的辊90配置在过滤浓缩槽12的上方。另外,构成为在架设于两个辊88、90之间的输送机上,设置多个铲斗89b,输送机沿过滤浓缩槽12的侧壁移动。另外,在第3组斗式输送机84c中,两个辊90、92配置在过滤浓缩槽12的上方(收容在过滤浓缩槽12内的污泥的上部),输送机架设在两个辊90、92之间。另外,构成为在该输送机中设置多个铲斗89c。如上述所示,如果采用3组斗式输送机84a、84b、84c,则例如可以与未浓缩污泥的过滤浓缩作业并行地进行浓缩污泥的排出作业。即,可以使用3组斗式输送机84a、84b、84c,将由第1组的各铲斗捞出的浓缩污泥,输送至第2组、第3组斗式输送机,最终向过滤浓缩槽12外部排出。Specifically, in the first group of
此外,斗式输送机并不限定于上述例子,例如,也可以是使用1组斗式输送机,在中途设置辊,从而能够变更路线的输送机。In addition, the bucket conveyor is not limited to the above-mentioned example, For example, the conveyor which can change the route by installing a roller in the middle using one set of bucket conveyors may be sufficient.
另外,也可以取代这种斗式输送机,使用从过滤浓缩槽12的底部通过过滤浓缩槽12的上部开口向外部延伸的金属丝网状的带式输送机。在此情况下,带式输送机同样地将从过滤浓缩槽12的底部向外部移动的输送机面配置为朝向上方。In addition, instead of such a bucket conveyor, a wire mesh belt conveyor extending from the bottom of the
另外,作为其他实施方式,在图7、图8所示的(D)的浓缩污泥排出步骤中,在过滤板14的下方、过滤浓缩槽12的底部设置金属丝网状的带式输送机,该金属丝网状带式输送机优选采用下述构造,即:延伸至在上方没有过滤板14的过滤浓缩槽12的底部部位,在那里与铲斗连接。在本实施方式的情况下,从过滤板14落下来的结块片的浓缩污泥W,载置在金属丝网状带式输送机上,被输送至铲斗,可以向过滤浓缩槽12外部取出。In addition, as another embodiment, in the step of discharging concentrated sludge (D) shown in FIG. 7 and FIG. , The wire mesh belt conveyor preferably adopts the following structure, that is, it extends to the bottom portion of the
作为未浓缩污泥排出单元,设置未浓缩污泥排出管67,将未浓缩污泥排出。此外,优选该未浓缩污泥排出管67在过滤浓缩槽的底部的上方规定高度与过滤浓缩槽连接,以不会将积存在过滤浓缩槽的底部的浓缩污泥排出。As the non-concentrated sludge discharge means, the non-concentrated
具体地说,在过滤浓缩槽12的底部的上方的规定高度H处,连通用于排出过滤浓缩槽12内的未浓缩污泥的未浓缩污泥排出管67的一端。在未浓缩污泥排出管67的中途,设置有未浓缩污泥排出阀68。该规定高度H设定在积存于过滤浓缩槽12的底部的结块片的浓缩污泥高度的上方。例如设置在网眼状托盘82的上端部的上方。通过如上述所示设定规定高度H,可以使得从滤布18剥离并积存于过滤浓缩槽12的底部的浓缩污泥,不会从未浓缩污泥排出管67与未浓缩污泥一起向外部排出。另外,如图2B所示,在过滤浓缩槽12的底部,连通用于将积存在过滤浓缩槽12的底部的小片的结块或者液体状的浓缩污泥排出的浓缩污泥排出管30的一端。另外,在浓缩污泥排出管30的中途,设置有浓缩污泥排出阀32。通过将该浓缩污泥排出阀32打开,从而使积存在过滤浓缩槽12的底部的上述浓缩污泥在重力作用下落下,通过浓缩污泥排出管30向外部排出。Specifically, one end of an unconcentrated
即,在未浓缩污泥中结块片状的浓缩污泥向过滤浓缩槽12的下部沉淀的过程中,必须将未浓缩污泥和浓缩污泥分别分离并向外部排出。在此情况下,如果从与过滤浓缩槽12的底部连接的未浓缩污泥排出管排出未浓缩污泥,则在未浓缩污泥中会混入浓缩污泥,从而难以仅回收未浓缩污泥。或者,可能由于具有保形性的结块片的浓缩污泥,将与未浓缩污泥排出管连接的排出口闭塞,甚至连未浓缩污泥的回收也变得困难。因此,根据具有上述结构的吸引式过滤浓缩装置,在通过未浓缩污泥排出管将未浓缩污泥排出时,可以不将底部积存的结块片的浓缩污泥排出,而仅将未浓缩污泥高效地向外部排出。此外,在本实施方式中,向外部排出的未浓缩污泥以循环的方式,利用污泥供给阀26以及污泥供给泵28等再次向过滤浓缩槽12供给(未图示管路)。That is, in the process of settling the concentrated sludge in the form of agglomerated flakes in the non-concentrated sludge to the lower part of the
另外,作为其他例子,可以进一步在过滤浓缩槽12的底部和未浓缩污泥排出管67之间,设置第2未浓缩污泥排出管(未图示)。即,在将未浓缩污泥向外部排出时,首先将未浓缩污泥从未浓缩污泥排出管67向外部排出。然后,将从过滤浓缩槽12的底部直至规定高度H为止残留的未浓缩污泥,从第2未浓缩污泥排出管向外部排出。在如上述所示设置第2未浓缩污泥排出管的情况下,不是从最初就通过第2未浓缩污泥排出管将未浓缩污泥排出,而是首先从未浓缩污泥排出管67将未浓缩污泥向外部排出,暂时使过滤浓缩槽12内的未浓缩污泥的高度下降,使水压降低。因此,限制与未浓缩污泥一起排出的浓缩污泥量,同时可以将从过滤浓缩槽12的底部至规定高度H为止残留的未浓缩污泥排出。特别地,在积存于过滤浓缩槽12的底部的结块片的浓缩污泥较大的情况下,设置于过滤浓缩槽12的底部的排出口,可能被通过第2未浓缩污泥排出管的该浓缩污泥闭塞。因此,可以将残留至规定高度H以下的未浓缩污泥以一定程度排出,另一方面,不将浓缩污泥向外部排出。In addition, as another example, a second non-concentrated sludge discharge pipe (not shown) may be further provided between the bottom of the
另外,作为其他未浓缩污泥排出管的例子,可以具有多个彼此并列地与上述未浓缩污泥排出管连接的分支管,各分支管在上述过滤浓缩槽的底部上方的不同高度,经由排出阀与上述过滤浓缩槽连接。例如,如图2C所示,未浓缩污泥排出管67构成为具有3个彼此并列地与未浓缩污泥排出管67连接的分支管108a、108b以及108c。并且,各分支管108a、108b、108c在过滤浓缩槽12的底部上方的不同高度,经由排出阀112a、112b、112c与过滤浓缩槽12连接。另外,在未浓缩污泥排出管67上设置有吸引泵120。根据具有上述结构的装置,可以与积存在过滤浓缩槽12的底部的浓缩污泥的沉淀高度相对应,选择从3个分支管108a、108b及108c中的某个分支管使未浓缩污泥通过未浓缩污泥排出管67而排出。例如,在浓缩污泥的沉淀高度与相距过滤浓缩槽12的底部最低高度的分支管108c最接近时,将最低高度的分支管的排出阀112c关闭。另一方面,将第2及第3高度水平的分支管的排出阀112a、112b打开,通过使吸引泵120动作,从而可以不将积存在过滤浓缩槽12的底部的浓缩污泥从未浓缩污泥排出管67向外部排出,而仅将未浓缩污泥向外部排出。另外,在因原水的水质变化使浓缩污泥的产生量发生变化的情况下,可以对排出阀112a、112b及112c进行切换。由此,无论浓缩污泥在过滤浓缩槽12内的沉淀高度如何变化,均可以仅将未浓缩污泥向外部排出。例如,在浓缩污泥的沉淀高度变高,与相距过滤浓缩槽1的底部为第2高度水平的分支管108b最接近时,将最低高度以及第2高度水平的分支管的排出阀112c及112b关闭。另一方面,只要将第3高度水平的分支管的排出阀112a打开即可。此外,在本实施方式中,最低高度的分支管108c的设置高度,位于网眼状托盘82上端的上方。In addition, as an example of other non-concentrated sludge discharge pipes, there may be a plurality of branch pipes connected to the above-mentioned non-concentrated sludge discharge pipe in parallel. The valve is connected with the above-mentioned filter concentration tank. For example, as shown in FIG. 2C, the unconcentrated
另外,作为其他例子可以举出下述实施方式。如图2D所示,可以例示出下述装置(下伸管),即,作为未浓缩污泥排水管67,设置为在过滤浓缩槽12内从过滤浓缩槽12的上部开口向下方延伸,使得未浓缩污泥排水管67的下端部成为过滤浓缩槽12的底部上方的规定高度H。通过设置多个下伸管,改变过滤浓缩槽12内的各下伸管端部的高度位置,从而也可以具有与上述分支管108a、108b、108c相同的功能。另外,在未浓缩污泥排水管67上设置有抽水泵113。根据这种装置,可以不将积存在过滤浓缩槽12的底部的浓缩污泥从未浓缩污泥排水管67向外部排出,而利用抽水泵113仅将未浓缩污泥向外部排出。另外,可以与因原水的水质变化使浓缩污泥的产生量发生变化的情况相对应,简单地更换这种下伸管构造的未浓缩污泥排水管。由此,无论浓缩污泥的沉淀高度如何变化,均可以不将积存在过滤浓缩槽12的底部的浓缩污泥从未浓缩污泥排出管67向外部排出,而仅将未浓缩污泥向外部排出。In addition, the following embodiments can be given as other examples. As shown in FIG. 2D, the following device (down pipe) can be exemplified, that is, as the unconcentrated
另外,作为其他例子,也可以设置挠性软管等。例如,如图2E所示,在未浓缩污泥排出管67的下端部,可连通地连接挠性软管114。并且,可以对挠性软管114的上下方向的长度进行调节,以使得未浓缩污泥排出管67的下端部成为过滤浓缩槽12的底部上方的规定高度H。更具体地说,由于挠性软管114具有挠性的蛇形部,所以使该蛇形部沿上下方向伸缩而进行使用。由此,可以调整挠性软管114的上下方向的长度。此外,在未浓缩污泥排水管67上设置有抽水泵113。根据具有上述结构的装置,不会将积存在过滤浓缩槽12的底部的浓缩污泥从未浓缩污泥排出管67向外部排出,通过使抽水泵113动作,可以仅将未浓缩污泥向外部排出。另外,可以与因原水的水质变化使浓缩污泥的产生量发生变化的情况相对应,使设置在上述下伸管下端部的挠性软管114的蛇形部沿上下方向伸缩,从而一边调节长度一边使用。由此,不需要更换未浓缩污泥排出管67本身,无论浓缩污泥的沉淀高度如何变化,均可以仅将未浓缩污泥向外部排出。In addition, as another example, a flexible hose or the like may be provided. For example, as shown in FIG. 2E , a
(吸引过滤浓缩装置的运转方法以及作用)(operation method and function of suction filtration concentration device)
下面,针对具有上述结构的吸引过滤浓缩装置10,说明运转方法及其作用。在图7中,在(A)的处理步骤中,首先,向过滤浓缩槽12内供给污泥X。具体地说,如图2A~图2F所示,打开污泥供给/排出阀26,使污泥供给/排出泵28动作。然后,通过污泥供给/排出管24,将作为过滤浓缩对象的污泥,向过滤浓缩槽12内供给至过滤板14的顶部的高度。然后,进行下述准备,即,利用虹吸式对过滤浓缩槽12内的污泥进行过滤浓缩。具体地说,打开吸引阀33,使真空泵35动作。由此,滤布18内的液体通过分配管34被吸引至滤液储存槽36内。另外,可以与分配管34的过滤板14侧的端部和滤液储存槽36之间的高度差相对应,利用虹吸作用,如图6B所示,将导入至过滤室76内的滤液通过污泥排出管38向外部排出。Next, the method of operation and the function of the suction
然后,在图7所示的(B)的处理步骤中,对过滤浓缩槽12内的污泥进行过滤浓缩。更详细地说,如图2A~图2G所示,过滤浓缩槽12内的污泥由于虹吸原理而被向滤布18的外表面吸引。此时,污泥中的水分通过滤布18,并作为滤液被引导至滤布18内的过滤室76内(参照图6B),使污泥脱水。该脱水并浓缩后的污泥W附着在滤布18的外表面。此时,即使是利用虹吸式进行的比较低压的连续吸引,也可以以期望的附着力使污泥附着在滤布18的外表面。即,可以以下述程度的硬度、附着力进行附着:即使在未浓缩污泥中使附着于滤布18的外表面上的浓缩污泥的结块W剥离,也可以作为结块片的浓缩污泥而维持保形性的程度的硬度、附着力。Then, in the processing procedure of (B) shown in FIG. 7, the sludge in the
此外,对于过滤板14的支撑板50,从其周围利用螺旋弹簧54持续地施加张力。因此,过滤板14的支撑板50维持不动的静止状态。由此,可以防止过滤板14(支撑板50)晃动或摆动。因此,可以防止附着在滤布18的外表面上的浓缩污泥W,在浓缩污泥剥离步骤前(或者,在利用浓缩污泥剥离单元进行剥离前),从滤布18的外表面剥离的情况。In addition, tension is continuously applied from the periphery of the
然后,在图7所示的(C)的处理步骤中,通过使滤布18膨胀,从而使附着在滤布18上的浓缩污泥W剥离。在进行该处理的情况下,过滤浓缩槽12内的未浓缩污泥也保持残留状态。具体地说,如图2A~图2G、图3所示,将水流入阀44打开,从液体输送泵46通过水流入管42、分配管34以及水平管15,将水向过滤板14的过滤室76内输送(参照图6A)。即,在过滤浓缩后的未浓缩污泥中,从附着有浓缩污泥的面的相反侧向滤布18连续地以规定时间压送水。此时,所压送的水要通过滤布18的大量细孔向未浓缩污泥中流出。另一方面,浓缩污泥附着在滤布18的外表面整体上,堵塞滤布18的大量细孔。另外,在附着有浓缩污泥的滤布18的外表面上,同样地承载未浓缩污泥的液压。因此,在至少克服未浓缩污泥的液压之前,向过滤室76内压送的水的水压,将附着在滤布18的外表面上的浓缩污泥向未浓缩污泥中按压。即,在至少克服未浓缩污泥的液压之前,不会将浓缩污泥从滤布18的表面剥离。因此,过滤室76内的压送水的压力上升,与此同时使滤布18膨胀。Then, in the processing step of (C) shown in FIG. 7 , the concentrated sludge W adhering to the
换言之,在浓缩污泥附着于滤布18的外表面整体上,将滤布18的大量细孔堵塞的情况下,滤布18的膨胀进行至所压送的水的水压在过滤室76内同样地达到规定压力为止。并且,在所压送的水的水压在过滤室76内同样地达到规定压力的定时,滤布18的膨胀结束。即,所压送的水可以在滤布18的整体上,将附着在滤布18的外表面上的浓缩污泥一齐向未浓缩污泥中按压。In other words, when the concentrated sludge adheres to the entire outer surface of the
如上述所示,浓缩污泥W如图11A所示,可以从滤布18的外表面沿周方向均匀地剥离。另外,如图11B所示,浓缩污泥W可以从滤布18的外表面沿高度方向均匀地剥离。As described above, the concentrated sludge W can be uniformly peeled off from the outer surface of the
另外,在将附着于滤布18的外表面上的浓缩污泥从滤布18剥离时,通过在未浓缩污泥中利用水进行剥离,从而可以减少与剥离相伴的噪音,可以消除对于吸引过滤浓缩装置设置场所的制约。In addition, when peeling the concentrated sludge attached to the outer surface of the
另外,由于可以在具有不会再溶解的程度的硬度和大小以及保形性的状态下,将浓缩污泥剥离,所以结块片的浓缩污泥在未浓缩污泥中一边受到浮力的作用,一边向过滤浓缩槽12的底部落下。由此,可以缓和与底部碰撞时的冲击。另外,由于较硬地形成结块状的浓缩污泥,所以可以防止因浓缩污泥向未浓缩污泥中溶入而使浓缩污泥的浓缩度降低。另外,由于结块状的浓缩污泥具有保形性,所以不会使结块成为层状而破碎。因此,可以从定位在过滤浓缩槽12的底部的网眼状托盘82内,以结块片的浓缩污泥的状态,或者以容易排出的程度保持结块状形态的状态,简单且高效地向外部排出。In addition, since the concentrated sludge can be peeled off in a state of hardness, size, and shape retention to the extent that it will not be redissolved, the concentrated sludge of the agglomerated sheet is subjected to buoyancy in the unconcentrated sludge. One side falls to the bottom of the
然后,在图7所示的(D)的处理步骤中,将剥离的浓缩污泥W向过滤浓缩槽12外部排出。例如,在浓缩污泥排出单元为图2F、图10所示的浓缩污泥捞出部23、网眼状托盘82、斗式输送机84等的情况下,首先,将过滤板14从过滤浓缩槽12向外部取出。此外,在该步骤中,过滤浓缩槽12的未浓缩污泥保持残留状态。然后,由操作人员抓住把手将网眼状托盘82抬起,将积存在网眼状托盘82内的结块片的浓缩污泥捞出等,并向外部排出。由于浓缩污泥具有不会再溶解的硬度和大小以及保形性,所以在剥离后直至向外部取出为止,可以在未浓缩污泥中作为结块片而保持保形性。因此,根据上述结构,不需要在排出浓缩污泥前将未浓缩污泥向外部排出,可以在未浓缩污泥中容易地进行固液分离。即,可以进行连续处理。到此为止,污泥的过滤浓缩作业完成。此外,向过滤浓缩槽12外部排出的浓缩污泥,利用另外的脱水机进一步进行浓缩,再次形成为结块状,并进行焚烧或者填埋处理。Then, in the processing step (D) shown in FIG. 7 , the peeled concentrated sludge W is discharged to the outside of the
在本发明中,优选在以规定次数反复进行由上述过滤浓缩步骤和上述浓缩污泥剥离步骤构成的循环后,进行浓缩污泥排出步骤,在各循环中的上述过滤浓缩步骤前,具有通过污泥供给步骤向过滤浓缩槽12内补给污泥的步骤。为了实现上述浓缩污泥排出步骤,例如如图9A所示,也可以具有将新的污泥向过滤浓缩槽12内补给(供给)的步骤。具体地说,如图9A所示,将未浓缩污泥向过滤浓缩槽12内供给,在过滤浓缩槽12内进行过滤浓缩,并将浓缩污泥剥离。然后,将所剥离的浓缩污泥向外部排出,也可以在将浓缩污泥向外部排出后,将新的污泥向过滤浓缩槽12内供给(补给)。或者,如图9A所示,以规定次数反复进行由过滤浓缩步骤和浓缩污泥剥离步骤构成的循环。并且,也可以在各循环中的过滤浓缩步骤前,利用污泥供给步骤向过滤浓缩槽12内供给新的污泥。此外,对于循环的次数,只要考虑过滤板14的过滤能力、应处理的污泥量等而适当确定即可。由此,可以更高效地进行污泥的过滤浓缩处理。In the present invention, it is preferable to perform the concentrated sludge discharge step after repeating the cycle consisting of the above-mentioned filtration concentration step and the above-mentioned concentrated sludge stripping step for a predetermined number of times, and there is a step of passing sludge before the above-mentioned filtration concentration step in each cycle. Sludge supply step is a step of supplying sludge into the
另外,优选上述浓缩污泥排出步骤在上述过滤浓缩步骤中并行进行,另一方面,在上述过滤浓缩步骤前,具有利用上述污泥供给步骤向过滤浓缩槽12内补给污泥的步骤。为了实现上述浓缩污泥排出步骤,例如如图8及图9B所示,也可以具有一边将所剥离的结块片的浓缩污泥向外部排出,一边将新的污泥向过滤浓缩槽12内补给(供给)的步骤,同时进行过滤浓缩。具体地说,可以在过滤浓缩槽12内的空间有富余,不需要为了将浓缩污泥向外部排出而将过滤板14暂时向外部取出的情况下应用。另外,可以在将多组斗式输送机或带式输送机沿过滤浓缩槽12的底部及侧壁配置而使用的情况下应用。由此,可以更高效地进行污泥的过滤浓缩处理。In addition, it is preferable that the above-mentioned concentrated sludge discharge step is performed in parallel with the above-mentioned filter concentration step, and on the other hand, there is a step of replenishing sludge into the
以上,详细说明了本发明的实施方式,但本领域的技术人员可以在不脱离本发明范围的范围内进行各种修正或变形。例如,在本实施方式中,说明了过滤浓缩对象为污泥的情况,但并不限定与此。例如,作为过滤浓缩对象,可以举出碱性溶液中含有的焚烧灰、牛奶、果汁等饮料液中含有的异物、浊质水中的浊质物等。只要与上述过滤浓缩对象相对应而适当地设定滤布18的种类、细孔直径的大小、吸引力等条件,则本发明所涉及的吸引过滤浓缩方法以及吸引式过滤浓缩装置,也可以针对它们而使用。As mentioned above, although embodiment of this invention was described in detail, those skilled in the art can make various corrections and deformation|transformation in the range which does not deviate from the range of this invention. For example, in this embodiment, although the case where the object of filtration concentration was sludge was demonstrated, it is not limited to this. For example, incineration ash contained in an alkaline solution, foreign matter contained in beverage liquids such as milk and fruit juice, and turbid matter contained in turbid water may be mentioned as objects of filtration concentration. As long as conditions such as the type of
实施例Example
本发明人为了确认本发明的效果,将净水厂的污泥作为过滤浓缩对象,使用滤布进行虹吸式的吸引过滤浓缩试验,将利用作为剥离介质的水得到的剥离压力作为参数,对剥离时间和剥离率之间的关系进行了调查。In order to confirm the effect of the present invention, the present inventors used the sludge of a water purification plant as the object of filtration and concentration, carried out a siphonic suction filtration concentration test using filter cloth, and used the peeling pressure obtained as the water of the peeling medium as a parameter to determine the effect of the peeling on the sludge. The relationship between time and peeling rate was investigated.
图12表示试验装置的整体。由于基本结构与从图2A中去除浓缩污泥捞出部23(网眼状托盘82)后的结构相同,所以省略其详细说明,但水流入管42连接在一端与过滤室76连通的倒U字管的中途,在该水流入管42上设置剥离压力调整阀150,通过对该剥离压力调整阀150的开度进行调整,从而调整水的压力、供给时间。具体地说,从洗净水槽162利用洗净水泵160,将洗净水通过水流入管42以及分配管34向形成于过滤板14内部的过滤室76供给。此外,作为净水厂的污泥的原液,从原液槽152利用原液泵154向过滤浓缩槽12供给。污泥被吸引管31连续地吸引,滤液F通过滤液排出管38向外部的滤液槽36排出,浓缩污泥W附着在滤布18的外表面上。积存在过滤浓缩槽12的底部的浓缩污泥,利用浓缩污泥排出泵156向外部的过滤浓缩槽158排出。此外,164表示洗净水压调整阀,166表示压缩机,168表示原液排出泵。另外,过滤板14的规格如下所示。Fig. 12 shows the whole of the test device. Since the basic structure is the same as that of FIG. 2A after removing the concentrated sludge removal part 23 (mesh tray 82), its detailed description is omitted, but the
(1)材质:滤布18··尼龙,支撑板50··树脂(1) Material: filter
(2)片数:1片(2) Number of pieces: 1 piece
(3)尺寸:1900mm×2500mm,过滤面积:9.5m2 (3) Size: 1900mm×2500mm, filter area: 9.5m 2
(4)制作方法:将滤布18和支撑板50一体缝制(4) Manufacturing method: sewing the
(5)过滤板容积:0.07m3(厚15mm)(5) Filter plate volume: 0.07m 3 (thickness 15mm)
(6)污泥的组成:Ig.loss:36.4%,SiO2:34.2%,Al2O3:18.7%,Fe2O3:4.1%,CaO:1.4%,SO4:1.8%,其他:3.4%(此外,%表示质量%)(6) Composition of sludge: Ig.loss: 36.4%, SiO 2 : 34.2%, Al 2 O 3 : 18.7%, Fe 2 O 3 : 4.1%, CaO: 1.4%, SO 4 : 1.8%, others: 3.4% (Also, % means mass%)
(7)过滤时间:90分钟(7) Filtration time: 90 minutes
图13表示剥离时间和剥离率之间的关系。如图13所示,如果剥离压力一定,则剥离时间越长,剥离率越上升。可知为了确保作为实际使用的剥离率大于或等于95%,无论剥离压力如何,作为连续的剥离时间至少需要30秒。Fig. 13 shows the relationship between the peeling time and the peeling rate. As shown in FIG. 13 , if the peeling pressure is constant, the peeling rate increases as the peeling time increases. It can be seen that in order to secure a peeling rate of 95% or more for practical use, at least 30 seconds is required as a continuous peeling time regardless of the peeling pressure.
工业实用性Industrial Applicability
本发明所涉及的吸引过滤浓缩方法以及吸引过滤浓缩装置,并不限于包括上水、中水及下水在内的水处理类技术领域,也可以应用于食品类领域、化学工业类领域等宽范围的技术领域,其中,对于在净水厂等的水处理步骤所产生的污泥的浓缩步骤中使用的吸引过滤浓缩装置,特别有用。The suction filtration concentration method and the suction filtration concentration device involved in the present invention are not limited to the technical field of water treatment including upper water, reclaimed water and sewage, and can also be applied to a wide range of food fields, chemical industry fields, etc. Among them, it is particularly useful for a suction filtration thickening device used in a thickening step of sludge generated in a water treatment step of a water purification plant or the like.
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| JP2009083065 | 2009-03-30 | ||
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| JP2009-083030 | 2009-03-30 | ||
| JP2009-083009 | 2009-03-30 | ||
| PCT/JP2010/055455 WO2010113822A1 (en) | 2009-03-30 | 2010-03-26 | Suction filtration/concentration method and suction filtration/concentration device |
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2010
- 2010-03-26 JP JP2010550766A patent/JPWO2010113822A1/en active Pending
- 2010-03-26 CN CN201080002629XA patent/CN102159509A/en active Pending
- 2010-03-26 WO PCT/JP2010/055455 patent/WO2010113822A1/en not_active Ceased
- 2010-03-26 KR KR1020117006038A patent/KR101396065B1/en active Active
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116969654A (en) * | 2023-07-24 | 2023-10-31 | 惠州金茂源环保科技有限公司 | Sludge concentration process and system |
| CN116969654B (en) * | 2023-07-24 | 2024-06-07 | 惠州金茂源环保科技有限公司 | Sludge concentration process and system |
Also Published As
| Publication number | Publication date |
|---|---|
| JPWO2010113822A1 (en) | 2012-10-11 |
| WO2010113822A1 (en) | 2010-10-07 |
| KR101396065B1 (en) | 2014-05-15 |
| KR20120002518A (en) | 2012-01-05 |
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