Next, fluorine in the waste water is primarily treated, and the waste 的简体中文翻译

Next, fluorine in the waste water i

Next, fluorine in the waste water is primarily treated, and the waste water the organic matters of which have been primarily and secondarily treated is filtrated by the submerged membrane 9 set at the reaction-tank upper part 3-1. The filtrated waste water is transferred to the slaked lime reaction tank 14 by the submerged membrane pump 7 connected to the submerged membrane 9 with piping. A rapid agitator 15 is set at this slaked lime reaction tank 14, where new slaked lime is added and agitated so as to react with fluorine in the waste water that has not completely reacted in the reaction tank 3, thus making the fluorine secondarily treated. That is, with respect to fluorine in the waste water, the reaction at the reaction-tank lower part 3-3 is primary coarse treatment and the reaction at the slaked lime reaction tank 14 is reliable secondary treatment of fluorine.In this slaked lime reaction tank 14, fluorine remaining in the waste water is formed into granular calcium fluoride by the addition of slaked lime and the agitation with the rapid agitator 15. Subsequently, the waste water is introduced into the polychlorinated aluminum flocculation tank 16, where polychlorinated aluminum as an inorganic flocculant is added, forming larger flocs. Then, the waste water containing the flocs is subsequently introduced into the polymer-flocculant flocculation tank 17, where a slow agitator 18 is set, and where the large flocs are formed into more stable, easy-to-settle even larger flocs by the addition of polymer flocculants. These more stable, easy-to-settle even larger flocs subsequently flow into the settling tank 19 having a settling-tank collector 20, where the flocs are settled to lower part of the settling tank 19. The resulting supernatant in this settling tank 19 is treated water.The flocs, or sludge, settled in the settling tank 19 contains unreacted slaked lime, unreacted polychlorinated aluminum and unreacted polymer flocculants, due to the fact that slaked lime is added, polychlorinated aluminum is excessively added and polymer flocculants are added in the slaked lime reaction tank 14, the polychlorinated aluminum flocculation tank 16 and the polymer-flocculant flocculation tank 17. All the sludge settled in this settling tank 19 is returned to upper part of the reaction-tank lower part 3-3 by a sludge return pump 21.As a result, the unreacted chemicals 29 are fully recycled for the treatment of organic matter-containing fluorine waste water, so that the sludge of the reaction-tank lower part 3-3 is settled, passing through the upper part of the inclined wall 27 and moving to the settling part 6. This sludge of the settling part 6 is transferred to the concentration tank 22 by the settling part pump 8, concentrated there, and then transferred to the filter press 25 by a filter press pump 24 and then dehydrated there.According to this embodiment, since the biological sludge 31 and the calcium-containing chemical sludge 28 are introduced to one reaction tank 3, organic matters in the waste water can be treated by microorganisms contained in the biological sludge 31 and fluorine can be treated by the calcium-containing chemical sludge 28.Also according to this embodiment, since the reaction tank 3 has the submerged membrane 9 as a membrane separation unit, the biological sludge 31 and the chemical sludge 28 can be prevented from flowing out of the reaction tank 3 so that the biological sludge 31 and the chemical sludge 28 can be effectively used for waste water treatment. Also, microorganisms contained in the biological sludge 31 do not flow out of the reaction tank 3 and therefore can be effectively used for waste water treatment. Further, since neither the biological sludge 31 nor the chemical sludge 28 flow out of the reaction tank 3, continuously introducing the biological sludge 31 and the chemical sludge 28 to the reaction tank 3 allows biological sludge concentration and chemical sludge concentration to be markedly increased, thus allowing the waste water treatment efficiency to be enhanced.Also according to this embodiment, the reaction tank 3 comprises the aeration zone 3-1 having the membrane separation unit 9, the biological sludge zone 3-2 and the chemical sludge zone 3-3, and organic matter-containing fluorine waste water showing acidity is introduced from the reaction-tank lower part. Therefore, first, fluorine in the organic matter-containing fluorine waste water can be treated (primary treatment of fluorine) and, simultaneously therewith, the waste water can be neutralized. Then, the organic matter-containing fluorine waste water that has been neutralized by the chemical sludge 28 goes up from the lower chemical sludge zone 3-3 so as to be introduced to the biological sludge zone 3-2. In this biological sludge zone 3-2, the organic matters in the waste water are biologically treated by the microorganisms contained in the biological sludge 31. Next, the waste water i
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接着,对废水中的氟进行一次处理,将有机物经过一次处理和二次处理后的废水通过设置在反应槽上部3-1的浸没膜9进行过滤。过滤后的废水由通过管道与浸没式膜9连接的浸没式膜泵7输送至熟石灰反应槽14。在该熟石灰反应槽14中设置快速搅拌器15,加入新的熟石灰搅拌,与反应槽3中未完全反应的废水中的氟反应,对氟进行二次处理。也就是说,对于废水中的氟,<br><br>在该熟石灰反应槽14中,通过加入熟石灰和快速搅拌器15的搅拌,将残留在废水中的氟形成粒状氟化钙。随后,将废水引入多氯化铝絮凝槽16中,其中加入多氯化铝作为无机絮凝剂,形成较大的絮凝体。然后,含有絮凝剂的废水随后被引入到聚合物絮凝剂絮凝池17中,在那里设置了一个慢速搅拌器18,在那里大的絮凝物通过添加形成更稳定、更容易沉降的更大的絮凝物。高分子絮凝剂。这些更稳定、更容易沉降甚至更大的絮凝物随后流入具有沉降罐收集器20的沉降罐19,<br><br>沉降槽19中沉降的絮凝物或污泥含有未反应的熟石灰、未反应的多氯铝和未反应的聚合物絮凝剂,这是由于在熟石灰反应中加入了熟石灰、过量加入了多氯铝和聚合物絮凝剂。沉淀池14、多氯铝絮凝池16和高分子絮凝剂絮凝池17。沉淀在该沉淀池19中的所有污泥通过污泥回流泵21返回到反应池下部3-3的上部。<br><br>结果,未反应的化学品29被充分回收用于处理含有机物的含氟废水,从而使反应池下部3-3的污泥沉降,通过倾斜壁27的上部。并移动到沉淀部分6。沉淀部分6的污泥被沉淀部分泵8转移到浓缩罐22,在那里浓缩,然后通过压滤泵24转移到压滤25,然后在那里脱水. <br><br>根据该实施例,由于生物污泥31和含钙化学污泥28被引入一个反应槽3,废水中的有机物可以被包含在生物污泥31中的微生物处理,氟可以被处理。含钙化学污泥 28.<br><br>同样根据本实施例,由于反应槽3具有作为膜分离单元的浸没膜9,所以可以防止生物污泥31和化学污泥28流出反应槽3,从而使生物污泥31和化学污泥28流出反应槽3。化学污泥28可有效用于废水处理。此外,生物污泥31中所含的微生物不会流出反应槽3,因此可以有效地用于废水处理。进一步地,由于生物污泥31和化学污泥28都不会流出反应槽3,因此将生物污泥31和化学污泥28连续引入反应槽3可以使生物污泥浓度和化学污泥浓度显着增加,<br><br>同样根据本实施例,反应槽3包括具有膜分离单元9的曝气区3-1、生物污泥区3-2和化学污泥区3-3,以及呈酸性的含有机物氟废水从反应罐下部引入。因此,首先,可以对含有机物的氟废水中的氟进行处理(氟的一次处理),同时中和废水。然后,已被化学污泥28中和的含有机物氟废水从下部化学污泥区3-3上升,以引入生物污泥区3-2。在这个生物污泥区3-2,
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其次,对废水中的氟进行初步处理,有机物经一、二次处理后的废水,由设置在反应罐上部3-1的浸没式膜9过滤,过滤后的废水经浸没式膜泵7输送至消石灰反应罐14,浸没式膜泵7与浸没式膜9通过管道连接。在该消石灰反应罐14处设置快速搅拌器15,在该反应罐14中加入新的消石灰并搅拌,使其与反应罐3中未完全反应的废水中的氟发生反应,从而使氟得到二次处理。也就是说,对于废水中的氟,反应槽下部3-3处的反应是一级粗处理,消石灰反应槽14处的反应是可靠的氟二级处理。<br>在该消石灰反应槽14中,废水中残留的氟通过加入消石灰并用快速搅拌器15搅拌而形成颗粒状氟化钙,然后将废水引入多氯铝絮凝槽16,加入多氯化铝作为无机絮凝剂,形成较大的絮体。然后,含有絮体的废水随后被引入聚合物絮凝剂絮凝池17,其中设置了慢搅拌器18,并且通过添加聚合物絮凝剂将大絮体形成更稳定、易于沉降甚至更大的絮体。这些更稳定、更容易沉淀的更大絮体随后流入具有沉淀池收集器20的沉淀池19,其中絮体沉淀到沉淀池19的下部。在该沉淀池19中产生的上清液为处理水。<br>沉淀池19中沉淀的絮体或污泥含有未反应的熟石灰、未反应的多氯铝和未反应的高分子絮凝剂,这是由于熟石灰反应池14中添加了熟石灰、过量添加了多氯铝和高分子絮凝剂,多氯铝絮凝池16和高分子絮凝剂絮凝池17。沉淀在该沉淀池19中的所有污泥通过污泥回流泵21回流至反应池下部3-3的上部。<br>因此,未反应的化学品29被完全回收用于含氟有机物废水的处理,从而使反应池下部3-3的污泥沉淀,通过斜壁27的上部进入沉降部6,沉降部6的污泥由沉降部泵8输送至浓缩池22,浓缩后由压滤泵24输送至压滤机25脱水。<br>根据本实施例,由于将生物污泥31和含钙化学污泥28引入一个反应池3,因此废水中的有机物可由生物污泥31中包含的微生物处理,并且氟可由含钙化学污泥28处理。<br>同样根据本实施例,由于反应槽3具有浸没膜9作为膜分离单元,因此可以防止生物污泥31和化学污泥28流出反应槽3,从而生物污泥31和化学污泥28可以有效地用于废水处理。此外,生物污泥31中含有的微生物不会流出反应罐3,因此可以有效地用于废水处理。此外,由于生物污泥31和化学污泥28均未流出反应槽3,因此将生物污泥31和化学污泥28连续引入反应槽3可使生物污泥浓度和化学污泥浓度显著增加,从而提高废水处理效率。<br>同样根据本实施例,反应池3包括具有膜分离单元9的曝气区3-1、生物污泥区3-2和化学污泥区3-3,并且从反应池下部引入显示酸性的含氟有机物废水。因此,首先,含氟有机物废水中的氟可以被处理(氟的初级处理),同时,废水可以被中和。然后,经化学污泥28中和后的含氟废水有机物从下化学污泥区3-3上升,进入生物污泥区3-2,废水中的有机物通过生物污泥31中的微生物进行生物处理<br>
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