CN1119961A - Backwashing method of water treatment device using floating filter material - Google Patents
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 64
- 239000000463 material Substances 0.000 title claims abstract description 59
- 238000000034 method Methods 0.000 title claims abstract description 30
- 238000011001 backwashing Methods 0.000 title abstract description 35
- 238000001914 filtration Methods 0.000 claims abstract description 9
- 238000005406 washing Methods 0.000 claims 2
- 230000009182 swimming Effects 0.000 claims 1
- 230000002265 prevention Effects 0.000 abstract description 12
- 239000010802 sludge Substances 0.000 description 10
- 239000003921 oil Substances 0.000 description 5
- 235000019198 oils Nutrition 0.000 description 5
- 238000003756 stirring Methods 0.000 description 4
- 230000000813 microbial effect Effects 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 239000000654 additive Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000002984 plastic foam Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000006228 supernatant Substances 0.000 description 2
- 230000007704 transition Effects 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- BNTHCCKWMAYYPX-UHFFFAOYSA-N CCC(C)N1C(C)CCC1 Chemical compound CCC(C)N1C(C)CCC1 BNTHCCKWMAYYPX-UHFFFAOYSA-N 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- RHZUVFJBSILHOK-UHFFFAOYSA-N anthracen-1-ylmethanolate Chemical compound C1=CC=C2C=C3C(C[O-])=CC=CC3=CC2=C1 RHZUVFJBSILHOK-UHFFFAOYSA-N 0.000 description 1
- 239000003830 anthracite Substances 0.000 description 1
- 230000000903 blocking effect Effects 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000002062 proliferating effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 235000015112 vegetable and seed oil Nutrition 0.000 description 1
- 239000008158 vegetable oil Substances 0.000 description 1
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- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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Abstract
提供不破损过滤材料能均一地搅拌、洗净过滤层全域的使用浮游过滤材料的水处理装置的逆洗方法。该方法是在把处理槽的内部分成上下的过滤材料流失防止带的下侧充填浮游过滤材料而形成浮游过滤层的水处理装置的逆洗方法,将把水位降低到过滤材料流失带的下侧,从浮游过滤层的下面放出空气使该浮游过滤层流动化,从而把浮游过滤层内的闭塞物除去。过滤层全域均一而且适量地除去过滤层内的闭塞物,逆洗后的过滤时间短处理效率高。
Provides a backwashing method for a water treatment device using a floating filter material that can uniformly agitate and clean the entire area of the filter layer without damaging the filter material. This method is a backwashing method of a water treatment device that forms a floating filter layer by filling the lower side of the filter material loss prevention zone that divides the inside of the treatment tank into upper and lower filter material loss zones, and lowers the water level to the lower side of the filter material loss zone. , Release air from below the floating filter layer to fluidize the floating filter layer, thereby removing the occlusions in the floating filter layer. The whole area of the filter layer is uniform and the occlusion in the filter layer is removed in an appropriate amount, and the filtration time after backwashing is short and the treatment efficiency is high.
Description
本发明是关于在把处理槽的内部分成上下的过滤材料流失防止带的下面充填浮游过滤材料形成有浮游过滤层的水处理装置的逆洗方法。The present invention relates to a backwashing method of a water treatment device in which a floating filter material is filled under a filter material loss prevention belt dividing the inside of a treatment tank up and down to form a floating filter layer.
现在,使用用塑料发泡体等作成的浮游过滤材料进行水处理的精密过滤法和生物膜处理法等被越来越广泛地采用。精密过滤法是在充填浮游过滤材料的过滤层里将原水中的SS(浮游物质)捕捉过滤的,而生物膜处理法是由附着·增殖在过滤材料表面的微生物分解原水中的有机物。除此而外,作为使用浮游过滤材料的处理法,还有在具有亲油性的过滤材料表面把原水中的油滴凝集·粗粒化,将油分浮上分离的油水分离法。At present, the precision filtration method and biofilm treatment method of water treatment using floating filter materials made of plastic foam and the like are more and more widely used. The precision filtration method captures and filters SS (suspended matter) in raw water in a filter layer filled with floating filter materials, while the biofilm treatment method decomposes organic matter in raw water by microorganisms attached and proliferating on the surface of the filter material. In addition, as a treatment method using a floating filter material, there is an oil-water separation method in which the oil droplets in the raw water are aggregated and coarsened on the surface of the lipophilic filter material, and the oil is separated by floating.
象这样的水处理装置,随着处理的进行过滤层里所捕捉的原水中的SS和增大了的生物膜会将过滤材料之间的空隙渐渐阻塞,降低过滤效率。为避免阻塞,一般将空间率增大到98%左右,其结果限制了处理能力。如将空间率减小到50—80%而欲提高处理能力时,有必要进行适当的逆洗以把形成阻塞原因的阻塞物除去。这种逆洗通常是通过从过滤层的下面放出空气和水使过滤层流动,利用过滤材料粒子间的冲突把闭塞物剥离以及通过空气泡振动过滤层把阻塞物从过滤材料粒子上振落下来后,用水进行清洗。In such a water treatment device, as the treatment progresses, the SS in the raw water captured in the filter layer and the increased biofilm will gradually block the gaps between the filter materials and reduce the filtration efficiency. In order to avoid blocking, the space rate is generally increased to about 98%, which limits the processing capacity as a result. If the space rate is reduced to 50-80% and the processing capacity is to be increased, it is necessary to carry out appropriate backwashing to remove the blockages that form the cause of blockage. This kind of backwashing is usually performed by releasing air and water from the bottom of the filter layer to make the filter layer flow, using the friction between the filter material particles to peel off the occlusion and vibrating the filter layer through the air bubbles to shake the blockage off the filter material particles. Afterwards, wash with water.
但是,和使用无烟煤材料等无机质过滤材料的场合一样,这种从过滤层的下面同时放出空气和水的从前的逆洗方法,由于不能将过滤层全域进行有效、均一的洗净,其结果不仅过早地引起阻塞而增加逆洗频率,而且逆洗水量率(逆洗水量占被处理的原水量的比例)达30%、因需要大量的逆洗水而使处理能力降低。However, as in the case of using inorganic filter materials such as anthracite materials, the conventional backwash method in which air and water are released from the bottom of the filter layer at the same time cannot effectively and uniformly clean the entire filter layer. Not only does it cause blockage prematurely to increase the frequency of backwashing, but also the rate of backwashing water (the ratio of backwashing water to the treated raw water) reaches 30%, which reduces the processing capacity due to the need for a large amount of backwashing water.
也有用设置在过滤层中部或下部的搅拌机搅拌过滤层将阻塞物除去的方法,但有使过滤材料破损的缺点。特别在象生物膜处理那样的过滤层高达2.5—3.5m的装置里,不能达到充分的洗净效果。此外,即使过滤层在1m以下,在处理含有植物油的高粘度废水时,因过滤层全域不能达到均一地搅拌,导致了逆洗频率的增加和处理能力的下降。为此,用搅拌装置的逆洗方法未能达到实用化。There is also a method of stirring the filter layer with a stirrer arranged in the middle or lower part of the filter layer to remove the blockage, but it has the disadvantage of damaging the filter material. Especially in a device with a filter layer as high as 2.5-3.5m like biofilm treatment, a sufficient cleaning effect cannot be achieved. In addition, even if the filter layer is less than 1m, when treating high-viscosity wastewater containing vegetable oil, the entire area of the filter layer cannot be stirred uniformly, resulting in an increase in backwashing frequency and a decrease in treatment capacity. For this reason, fail to reach practicality with the backwashing method of stirring device.
本发明是为解决这种先有技术的缺点而设置的,其主要目的是提供不破损过滤材料能均一地搅拌·洗净过滤层全域的使用浮游过滤材料的水处理装置的逆洗方法。The present invention is designed to solve the disadvantages of the prior art, and its main purpose is to provide a method for backwashing a water treatment device using a floating filter material that can uniformly agitate and clean the entire area of the filter layer without damaging the filter material.
为了达到上述目的,本发明提供了一种使用浮游过滤材料的水处理装置,其特征在于,它是一种在把处理槽的内部分成上下的过滤材料流失防止带的下侧充填浮游过滤材料形成浮游过滤层的水处理装置的逆洗方法,其中,将水位降低到上述过滤材料流失带的下侧,从上述浮游过滤层的下面放出空气使该浮游过滤层流动,把该浮游过滤层内的阻塞物除去。In order to achieve the above object, the present invention provides a water treatment device using a floating filter material, which is characterized in that it is formed by filling the lower side of the filter material loss prevention belt that divides the inside of the treatment tank into upper and lower filter material loss prevention belts. The backwashing method of the water treatment device of the floating filter layer, wherein, the water level is lowered to the lower side of the above-mentioned filter material loss zone, the air is released from the bottom of the above-mentioned floating filter layer to make the floating filter layer flow, and the water in the floating filter layer Obstructions removed.
这样,通过把水位降低到过滤材料流失防止带的下侧,浮游着的浮游过滤材料的上面得到开放,使向上移动一直受到过滤材料流失防止带限制的上部的浮游过滤材料变得易于移动。这样从浮游过滤层的下面放出空气时、浮游过滤层全域的浮游过滤材料就能均一地摇动,能不破损过滤材料而将附着在浮游过滤材料表面的生物膜等的阻塞物剥离。In this way, by lowering the water level to the lower side of the filter material loss prevention belt, the upper surface of the floating floating filter material is opened, and the upward movement of the upper floating filter material that has been restricted by the filter material loss prevention belt becomes easy to move. When releasing air from the bottom of the floating filter layer like this, the floating filter material in the whole area of the floating filter layer can be shaken uniformly, and the clogs such as biofilm attached to the surface of the floating filter material can be peeled off without damaging the filter material.
实施例Example
以下,通过附图详细说明适用于本发明的实施例。实施例1Hereinafter, embodiments applicable to the present invention will be described in detail with reference to the drawings. Example 1
图1表示根据本发明而实施的逆洗方法的处理装置的一个例。这个处理装置是,使用浮游过滤材料的上向流动方式的生物膜处理装置,待处理的原水从设置在处理槽1的比较下面的原水流入口2被导入处理槽1,在以上向流动方式流过浮游过滤层3的内部时被净化处理。流过浮游过滤层3并到达其上侧的处理水从设置在那的处理水流出口4被送出装置外。FIG. 1 shows an example of a processing apparatus of the backwashing method implemented according to the present invention. This treatment device is a biofilm treatment device using an upward flow method of floating filter material. The raw water to be treated is introduced into the treatment tank 1 from the
浮游过滤层3里的浮游过滤材料7,充填在由上下成对的过滤材料流失防止带5·6切断而形成的空间内,其上浮到上面的过滤材料流失防止带5的限制。浮游过滤层3和下面的过滤材料流失防止带6之间保留有所规定的空间余量。浮游过滤材料7是塑料发泡体等的粒状体,表面上附着·增殖着呈膜状微生物,通过浮游过滤材料7能而被捕捉的SS和溶解性成分通过其表面的生物膜而被分解。The
浮游过滤层3的底板一侧配置着送气管9,其上面附有为进行曝气及逆洗放出从鼓风机8送来的空气的喷头。此外,处理槽1的下部设置有用来将逆洗时沉降·堆积下来的剩余污泥排出装置外的下部排出口10。One side of the bottom plate of the
进行逆洗时首先如图1(a)所表示的那样,通过下部排出口10将处理槽1内的水排出使水位降低到过滤材料流失防止带5的下侧。接着如(b)所表示的那样,开动鼓风机8从喷头放出空气使浮游过滤层3流动化、浮游过滤材料7表面的生物膜等被剥离。这样,约有1/3的微生物还残留在浮游过滤材料7上,其余约2/3作为剩余污泥如后述的那样通过逆洗水排出装置外。When performing backwashing, at first, as shown in FIG. Next, as shown in (b), start the
由剥离下来的生物膜等组成的污泥的一部分经放置一定时间后,如(c)所表示的那样沉淀下来堆积于底部并从下部排出口10被排出。最后如(d)所表示的那样,通过处理水流出口4用逆洗用水泵11送入处理槽(图中未示出)内的处理水、将滞留在浮游过滤材料7之间的污泥冲洗下来并从下部排出口10排出。A part of the sludge composed of the peeled off biofilm etc. is left for a certain period of time, as shown in (c), settles and accumulates at the bottom, and is discharged from the
为了对这种逆洗方法的效果加以确认,在形成有厚3m的浮游过滤层3,直径2m高6m的圆筒状处理槽装置上进行了实验。首先将水位降低到离上侧的过滤材料流失防止带5的下面约30cm、用送风量3.2m3/分,排出压力5,000mmAq的鼓风机,以3.2m3/分的速度从喷头将空气放出5分钟,搅拌浮游过滤槽3。然后放置2分钟,从浮游过滤材料7上剥离下来并堆积于处理槽1底部上的污泥从下部排出口10被排出。接着,用排出量65m3/小时,扬程10m的逆洗水泵11从处理槽1的上部将处理水以65m3/H的速度送入5—10分钟以洗净浮游过滤材料7,接着以上向流动方式洗净5分钟,逆洗终了。In order to confirm the effect of this backwashing method, an experiment was carried out on a cylindrical treatment tank device with a diameter of 2 m and a height of 6 m, in which a
这样,排出的全部逆洗排水的SS浓度为1,800mg/l,与在过滤层内配置旋转板的搅拌装置的逆洗方法的950mg/l相比较,除去污泥量约为2倍。此外,逆洗后立即就显示了与通常运转时同样的BOD·COD除去率,对逆洗过渡时间之短得到了确认。In this way, the SS concentration of the entire backwash wastewater discharged is 1,800 mg/l, which is about twice the amount of sludge removed compared to 950 mg/l in the backwash method with a stirring device equipped with a rotating plate in the filter layer. In addition, immediately after backwashing, the same BOD·COD removal rate as in normal operation was shown, and it was confirmed that the transition time to backwashing was short.
使用的逆洗水量为处理水量的5%。在不注入凝集剂等化学助剂时,逆洗排水经过30分钟的单纯沉降后微生物团块的绝大部分得到了沉降,因其上部50%的上清水被送回到了原水侧,其最终的逆洗水量率为2.5%。实施例2The amount of backwash water used is 5% of the amount of treated water. When chemical additives such as coagulants are not injected, most of the microbial agglomerates have been settled after 30 minutes of simple settlement in the backwash drainage, because 50% of the supernatant water in the upper part has been sent back to the raw water side, and its final The backwash water rate is 2.5%. Example 2
图2是根据本发明而实施的逆洗方法的装置的又一例,分段表示了逆洗的过程。该处理装置与实施例1一样是使用浮游过滤材料的生物膜处理装置,不同的是以下向流动方式。被处理的原水从设置在处理槽21的比较上面的原水流入口22被导入处理槽21,以下向流动方式流过浮游过滤层23内部时被净化处理。流过浮游过滤层23并到达其下面的处理水从设置在那里的处理水流出口24被送出装置外。Fig. 2 is another example of the device of the backwashing method implemented according to the present invention, showing the process of backwashing in sections. This processing device is the same as embodiment 1 and uses the biomembrane processing device of floating filter material, and difference is to flow downwards. The treated raw water is introduced into the treatment tank 21 from the raw water inflow port 22 arranged on the upper side of the treatment tank 21, and is purified while flowing downward through the floating filter layer 23. The treated water that has flowed through the floating filter layer 23 and reached the bottom thereof is sent out of the apparatus through the treated water outflow port 24 provided there.
和图1表示的基本一样,浮游过滤层23内充填着浮游过滤材料7。浮游过滤层23的底板一侧配置着附有放出从鼓风机8送来的空气的喷头的送气管9。此外,处理槽21的上面设置有排油口25,底部设置有用来将逆洗时沉降·堆积下来的剩余污泥排出装置外的下部排出口26。Basically the same as shown in FIG. 1 , the floating filter layer 23 is filled with the
进行逆洗时首先如图2(a)所表示的那样,通过下部排出口26将槽内的水排出使水位降低到过滤材料流失防止带5的下侧。接着如(b)所表示的那样,开动鼓风机8从喷头放出空气使浮游过滤层23流动。然后如(c)所表示的那样,放置一定时间后从浮游过滤材料7上剥离下来的污泥沉淀下来堆积于底部,并从下部排出口26被排出。最后如(d)所表示的那样,用水泵11送入处理水、将滞留在浮游过滤材料7之间的污泥冲洗下来并从上部排出口27排出。When carrying out backwashing, at first as shown in Figure 2 (a), the water in the tank is discharged through the lower discharge port 26 so that the water level is reduced to the lower side of the filter material
本实施例中只表示了使用浮游过滤材料的生物膜处理装置用的逆洗方法,但本发明不仅仅限于生物膜处理装置,还适用于使用浮游过滤材料的精密过滤装置和油水分离装置等。In this embodiment, only the backwashing method for the biofilm treatment device using the floating filter material is shown, but the present invention is not limited to the biofilm treatment device, but is also applicable to the precision filter device and the oil-water separation device using the floating filter material.
如上所说明的那样,本发明的使用浮游过滤材料的水处理装置的逆洗方法因为能将过滤层全域均一而且适量地从过滤层内除去阻塞物,逆洗后的过渡时间短,处理效率高。例如,在过滤层内保持的残留量,用生物膜处理法时微生物残量约1/3,油水分离法时油残量约1/3,精密过滤法时SS残量约1/3,能不导致净化能力的降低而立即以通常的能力开始运转。As explained above, the backwashing method of the water treatment device using the floating filter material of the present invention is because the filter layer can be uniformly removed from the filter layer in an appropriate amount, and the transition time after backwashing is short and the treatment efficiency is high. . For example, the residual amount kept in the filter layer is about 1/3 of the microbial residue when using the biofilm treatment method, about 1/3 of the oil residue when using the oil-water separation method, and about 1/3 of the SS residue when using the precision filtration method. Immediately start operation with normal capacity without causing reduction of purification capacity.
特别是生物膜处理法的剩余污泥也就是由逆洗排出的微生物团块比较坚固,化学助剂无注入的单纯沉降处理时30分钟后得到沉降,通过将上部的上清水送回原水槽,能由从前逆洗水量率的30%降低到3%以下。In particular, the residual sludge of the biofilm treatment method, that is, the microbial agglomerates discharged by backwashing, is relatively strong. When the chemical additives are not injected into the simple sedimentation treatment, they will settle after 30 minutes. By sending the upper supernatant water back to the original water tank, It can be reduced from 30% of the previous backwashing water rate to below 3%.
图1figure 1
由a、b、c和d构成,分段表示实施本发明的逆洗方法的过程图。Consisting of a, b, c and d, the segments represent the process diagram for implementing the backwashing method of the present invention.
图2figure 2
由a、b、c和d构成,分段表示其他水处理装置适用本发明的逆洗方法时的过程图。图中符号说明如下。Consisting of a, b, c and d, the subsections represent the process diagram of other water treatment devices when the backwashing method of the present invention is applicable. The symbols in the figure are explained as follows.
1 处理槽2 原水流入口3 浮游过滤层4 处理水流出口5·6 过滤材料流失防止带7 浮游过滤材料8 鼓风机9 送气管10 下部排出口11 逆洗水泵21 处理槽22 原水流入口23 浮游过滤层24 处理水流出口25 排油口26 下部排出口27 上部排出口1
Claims (1)
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6213193A JPH0857465A (en) | 1994-08-15 | 1994-08-15 | Backwashing of water treatment apparatus using floating filter material |
| JP213193/94 | 1994-08-15 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN1119961A true CN1119961A (en) | 1996-04-10 |
| CN1036975C CN1036975C (en) | 1998-01-14 |
Family
ID=16635084
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN95109613A Expired - Fee Related CN1036975C (en) | 1994-08-15 | 1995-07-26 | Backwashing method of water treatment device using floating filter material |
Country Status (3)
| Country | Link |
|---|---|
| JP (1) | JPH0857465A (en) |
| KR (1) | KR0166421B1 (en) |
| CN (1) | CN1036975C (en) |
Cited By (7)
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| CN105256861A (en) * | 2015-11-05 | 2016-01-20 | 南充市大禹水务科技有限责任公司 | Constant voltage equipment for water taking and water supply |
| CN105664553A (en) * | 2016-04-13 | 2016-06-15 | 胡小弟 | Filtration device |
| CN108348823A (en) * | 2015-11-04 | 2018-07-31 | 苏伊士水务工程公司 | It synthesizes compressible medium and filters backwash process |
| CN108479190A (en) * | 2018-06-13 | 2018-09-04 | 南京圣卡孚科技有限公司 | A kind of continuous floating bed filtering settled sand filter unit and application method |
| CN111847687A (en) * | 2019-08-30 | 2020-10-30 | 周建萍 | Oil-water separation and recovery equipment for catering industry |
| CN112169387A (en) * | 2020-11-12 | 2021-01-05 | 湖南澳维环保科技有限公司 | Upflow filter and filtering method |
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Families Citing this family (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH10337585A (en) * | 1997-06-05 | 1998-12-22 | Nippon Steel Corp | Backwashing method for buoyant filter media |
| JP3649382B2 (en) * | 2000-04-11 | 2005-05-18 | 株式会社石垣 | Filtration equipment using floating media |
| KR100712643B1 (en) * | 2004-12-28 | 2007-05-02 | 주식회사 태영건설 | Sewage, sewage and wastewater organic matter and nitrogen treatment equipment using air floating type biofilter and its method |
| JP4674188B2 (en) * | 2006-06-23 | 2011-04-20 | メタウォーター株式会社 | Primary treatment method for combined sewage |
| KR100724806B1 (en) * | 2006-07-20 | 2007-06-21 | 대한민국 | Fluidized Bed Filtration Tank in Seawater Circulation Filtration System |
| TWI407996B (en) * | 2010-06-21 | 2013-09-11 | Kuei Lin Tsai | Upward-flow type float-filter-backwashing method and a system thereof |
| JP6049005B2 (en) * | 2012-05-31 | 2016-12-21 | 鎌田バイオ・エンジニアリング株式会社 | Filtration device, filtration method thereof and backwashing method of filter medium |
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Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5126042A (en) * | 1991-10-31 | 1992-06-30 | Malone Ronald F | Floating media biofilter |
| US5232586A (en) * | 1992-09-25 | 1993-08-03 | Malone Ronald F | Floating media hourglass biofilter |
| JP2695624B2 (en) * | 1994-04-26 | 1998-01-14 | 東洋エンジニアリング株式会社 | How to clean floating filter media |
-
1994
- 1994-08-15 JP JP6213193A patent/JPH0857465A/en active Pending
-
1995
- 1995-07-18 KR KR1019950021078A patent/KR0166421B1/en not_active Expired - Fee Related
- 1995-07-26 CN CN95109613A patent/CN1036975C/en not_active Expired - Fee Related
Cited By (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108348823A (en) * | 2015-11-04 | 2018-07-31 | 苏伊士水务工程公司 | It synthesizes compressible medium and filters backwash process |
| CN108348823B (en) * | 2015-11-04 | 2020-10-23 | 苏伊士水务工程公司 | Synthetic Compressible Media Filtration Backwash Process |
| CN105256861A (en) * | 2015-11-05 | 2016-01-20 | 南充市大禹水务科技有限责任公司 | Constant voltage equipment for water taking and water supply |
| CN105664553A (en) * | 2016-04-13 | 2016-06-15 | 胡小弟 | Filtration device |
| CN108479190A (en) * | 2018-06-13 | 2018-09-04 | 南京圣卡孚科技有限公司 | A kind of continuous floating bed filtering settled sand filter unit and application method |
| CN111847687A (en) * | 2019-08-30 | 2020-10-30 | 周建萍 | Oil-water separation and recovery equipment for catering industry |
| CN111847687B (en) * | 2019-08-30 | 2022-08-12 | 苏州双福智能科技有限公司 | Oil-water separation and recovery equipment for catering industry |
| CN112169387A (en) * | 2020-11-12 | 2021-01-05 | 湖南澳维环保科技有限公司 | Upflow filter and filtering method |
| CN112169387B (en) * | 2020-11-12 | 2023-10-31 | 湖南澳维科技股份有限公司 | Filtration method of upflow filter |
| CN116139556A (en) * | 2023-02-22 | 2023-05-23 | 西安建筑科技大学 | A light-weight filter material annular filter device in front of a rainwater storage tank |
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Also Published As
| Publication number | Publication date |
|---|---|
| KR0166421B1 (en) | 1999-02-01 |
| CN1036975C (en) | 1998-01-14 |
| JPH0857465A (en) | 1996-03-05 |
| KR960007471A (en) | 1996-03-22 |
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