JPH11216306A - Purification device of bathtub water and circulating system of bathtub water - Google Patents

Purification device of bathtub water and circulating system of bathtub water

Info

Publication number
JPH11216306A
JPH11216306A JP10315798A JP31579898A JPH11216306A JP H11216306 A JPH11216306 A JP H11216306A JP 10315798 A JP10315798 A JP 10315798A JP 31579898 A JP31579898 A JP 31579898A JP H11216306 A JPH11216306 A JP H11216306A
Authority
JP
Japan
Prior art keywords
filter material
biodegradation
bathtub water
filter
physical removal
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10315798A
Other languages
Japanese (ja)
Inventor
Masahiro Tokida
昌広 常田
Naohito Wajima
尚人 輪島
Takashi Kinoshita
崇 木下
Hidetoshi Motoyama
英俊 本山
Hiroshi Kanamaru
宏 金丸
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toto Ltd
Original Assignee
Toto Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toto Ltd filed Critical Toto Ltd
Priority to JP10315798A priority Critical patent/JPH11216306A/en
Publication of JPH11216306A publication Critical patent/JPH11216306A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Filtering Materials (AREA)
  • Filtration Of Liquid (AREA)
  • Water Treatment By Sorption (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

PROBLEM TO BE SOLVED: To always maintain a microbial membrane of a suitable thickness on a surface of a filter material by a method wherein the filter material for physical removal is so arranged in a mode capable of scraping off the microbial membrane formed on the surface of the filter material for biological degradation in backwashing. SOLUTION: A vertical space is partitioned with a support 8 such as a stainless steel mesh or the like in a purification device 5, a filter material for biological degradation 10, in order to degradate a contaminated constituent dissolved in a bathtub water with a microbial membrane 11 formed on the surface is filled on the filter material 9. Then, a passage changeover valve is operated to reverse an inflow direction of the bathtub water into the purification device 5, the filter material 9 is wound up from down, and the microbial membrane 11 on the surface of the filter material 10 is thinned by scratching off by collision with the filter material and improval of fluidity of the filter material 10 itself owing to that collision. Further, a contaminant stuck to the filter material 9 is also simultaneously peeled off from the filter material 9 and exhausted outside via a drain pipe.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は浴槽水を浄化する浄
化装置とこの浄化装置を組み込んだ浴槽水の循環システ
ムに関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a purifier for purifying bath water and a bath water circulation system incorporating the purifier.

【0002】[0002]

【従来の技術】従来の浄化装置と、それを組み込んだ循
環システムを図10に基づいて説明すると、浴槽100
に浴槽水の循環路101を設け、この循環路101に
は、物理除去用の濾過材を充填した浄化装置102と、
生物分解用の濾過材を充填した浄化装置103と、ヒー
タ等の保温部104と、殺菌部105とを備えた構成と
なっている。
2. Description of the Related Art A conventional purifying apparatus and a circulation system incorporating the same will be described with reference to FIG.
A circulation path 101 for bathtub water, a purification device 102 filled with a filtering material for physical removal,
It is configured to include a purification device 103 filled with a filter material for biodegradation, a heat retaining unit 104 such as a heater, and a sterilizing unit 105.

【0003】そして、ポンプPによって浴槽水を浄化装
置102に送り込むことで、浴槽水中のゴミ等を濾過材
106で物理的に除去し、このゴミ等が除かれた浴槽水
を浄化装置103に送り込むことで、浴槽水中の汚れ成
分を濾過材107の表面に形成された微生物膜で分解す
るようにしている。
[0003] By sending the bathtub water to the purifying device 102 by the pump P, the dust and the like in the bathtub water are physically removed by the filter material 106, and the bathtub water from which the dust and the like have been removed is sent to the purifying device 103. Thus, the dirt component in the bath water is decomposed by the microbial membrane formed on the surface of the filter medium 107.

【0004】尚、浄化装置としては図11に示すよう
に、表面に微生物膜が形成された大径の濾過材107を
カートリッジ109に充填し、このカートリッジ109
を浄化装置本体110内に取出し自在に装填したものも
ある。
As shown in FIG. 11, a cartridge 109 is filled with a large-diameter filter material 107 having a microbial membrane formed on the surface thereof.
There is also a device which is loaded in the purifier main body 110 so as to be able to be taken out.

【0005】[0005]

【発明が解決しようとする課題】上述した従来の浄化装
置にあっては、濾過材107は微生物膜を表面に形成す
るため、その径は5〜15mmと大径になっている。し
かしながら、大径になると逆に流動性と攪拌性が低く、
濾過材洗浄性が悪い。その結果、濾過材107の表面に
形成される微生物膜が肥厚化し、逆洗時以外の運転時に
突然濾過材107表面から剥離してスライム状になっ
て、浴槽内に戻される。
In the above-mentioned conventional purifying apparatus, the diameter of the filter medium 107 is as large as 5 to 15 mm because a microbial membrane is formed on the surface. However, when the diameter becomes large, on the contrary, the fluidity and the stirring property are low,
Poor filter media washability. As a result, the microbial membrane formed on the surface of the filter medium 107 is thickened, and suddenly peels off from the surface of the filter medium 107 during operation other than the time of backwashing to form a slime and is returned to the bathtub.

【0006】上記スライム状の微生物膜は、感触が悪
く、目詰りを生じて浄化装置の商品価値を低下するだけ
でなく、レジオネラ属菌をはじめとする雑菌の繁殖を助
長することにもなる。
[0006] The slime-like microbial membrane has a bad feel, causes clogging and lowers the commercial value of the purification device, and also promotes the propagation of various bacteria such as Legionella spp.

【0007】[0007]

【課題を解決するための手段】上記課題を解決すべく本
発明に係る浴槽水の浄化装置は、浴槽水中の汚れ成分を
分解する微生物膜を表面に形成した生物分解用の濾過材
と、浴槽水中のゴミ等を物理的に除去する物理除去用の
濾過材とを備え、前記物理除去用の濾過材は逆洗時に生
物分解用の濾過材の表面に形成されている微生物膜を掻
き取ることが可能な態様で配置されている構成とした。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, a bathtub water purifying apparatus according to the present invention comprises a filter material for biodegradation having a microbial membrane on its surface for decomposing dirt components in bathtub water, and a bathtub. A filter for physical removal that physically removes dirt and the like in water, wherein the filter for physical removal scrapes off a microbial membrane formed on the surface of the filter for biodegradation during backwashing. Are arranged in a possible manner.

【0008】上記した微生物膜を掻き取ることが可能な
態様としては、例えば、同一の浄化筒内に物理除去用の
濾過材と生物分解用の濾過材を充填し、物理除去用の濾
過材を生物分解用の濾過材に比べて小径で且つ比重が大
となるものを選定する。
[0008] As an embodiment capable of scraping the above-mentioned microbial membrane, for example, a filter material for physical removal and a filter material for biodegradation are filled in the same purification column, and the filter material for physical removal is filled. A filter having a smaller diameter and a higher specific gravity than a filter material for biodegradation is selected.

【0009】上記した微生物膜を掻き取ることが可能な
別の態様としては、例えば、生物分解用の濾過材をハニ
カム構造体とし、物理除去用の濾過材を前記ハニカム構
造体の孔内を流動するのに十分な粒径のものとする。
[0009] As another mode in which the above-mentioned microbial membrane can be scraped off, for example, a filter material for biodegradation is a honeycomb structure, and a filter material for physical removal flows through the pores of the honeycomb structure. Particle size sufficient for

【0010】尚、前記物理除去用の濾過材の粒径は0.
4〜1mmとするのが掻き取り効果を発揮する上で好ま
しく、前記生物分解用の濾過材の粒径は3mm以上とす
るのが糸状菌等の微生物膜を形成する上で好ましい。
The filter material for physical removal has a particle size of 0.1.
The thickness is preferably 4 to 1 mm for exhibiting a scraping effect, and the particle size of the biodegradation filter is preferably 3 mm or more for forming a microbial membrane such as a filamentous fungus.

【0011】また、物理除去用の濾過材と生物分解用の
濾過材とがその一部が重なるように、即ち、生物分解用
の濾過材の一部が物理除去用の濾過材内に埋没するよう
に配置することができる。
The filter material for physical removal and the filter material for biodegradation are partially overlapped, that is, a part of the filter material for biodegradation is buried in the filter material for physical removal. Can be arranged as follows.

【0012】前記物理除去用の濾過材の具体例として
は、ガラスビーズ、アルミナビーズ等の無機ビーズが挙
げられ、前記生物分解用の濾過材の具体例としては、活
性炭が挙げられる。
Specific examples of the filter material for physical removal include inorganic beads such as glass beads and alumina beads, and specific examples of the filter material for biodegradation include activated carbon.

【0013】更に、物理除去用または生物分解用の濾過
材に、Ag等の抗菌剤を担持することも可能である。こ
のような構成とすることで、雑菌の効果的な除去が行え
る。
Further, it is possible to carry an antibacterial agent such as Ag on a filter for physical removal or biodegradation. With such a configuration, it is possible to effectively remove germs.

【0014】また、生物分解用の濾過材としては、活性
炭に無機バインダーを配合して構成することが可能であ
る。具体的には、生物分解用の濾過材は、活性炭に無機
バインダーを30〜70wt%配合して構成することが
好ましい。また、生物分解用の濾過材の活性炭に対する
無機バインダーの配合割合は、物理浄化用の濾過材と生
物分解用の濾過材との嵩比重が1.5:0.5〜1.
5:0.7となる割合とすることが好ましく、また、物
理浄化用の濾過材と生物分解用の濾過材との容積比が
5:70〜2:7となるように充填することが好まし
い。
[0014] The filter material for biodegradation can be constituted by blending an inorganic binder with activated carbon. Specifically, it is preferable that the filter material for biodegradation is constituted by mixing 30 to 70 wt% of an inorganic binder with activated carbon. The mixing ratio of the inorganic binder to the activated carbon of the filter material for biodegradation is such that the bulk specific gravity of the filter material for physical purification and the filter material for biodegradation is 1.5: 0.5 to 1.
The ratio is preferably 5: 0.7, and it is preferable to fill the filter so that the volume ratio of the filter material for physical purification and the filter material for biodegradation is 5:70 to 2: 7. .

【0015】また、本発明に係る浴槽水の循環システム
は、上記の浄化装置を浴槽水を取り出して再び浴槽に戻
す循環経路の途中に配置することで構成され、特に循環
経路には紫外線ランプ、オゾン発生器、電解殺菌装置等
の殺菌手段を配置することも可能である。
Further, the bathtub water circulation system according to the present invention is constituted by disposing the purifying device in the middle of a circulation path for taking out the bathtub water and returning it to the bathtub. It is also possible to arrange a sterilizing means such as an ozone generator and an electrolytic sterilizing device.

【0016】[0016]

【発明の実施の形態】以下に本発明の実施の形態を添付
図面に基づいて説明する。図1は本発明に係る浄化装置
を組み込んだ浴槽水の循環システムの全体図であり、浴
槽1内にはバスアダプタ2が設けられ、このバスアダプ
タ2には循環ポンプPを備えた吸上げ管3a及び戻し管
3bの一端が接続され、これら吸上げ管3a及び戻し管
3bの他端は流路切替弁4に接続されている。
Embodiments of the present invention will be described below with reference to the accompanying drawings. FIG. 1 is a general view of a bathtub water circulation system incorporating a purifying device according to the present invention. A bath adapter 2 is provided in a bathtub 1, and the bus adapter 2 has a suction pipe provided with a circulation pump P. One ends of the return pipe 3a and the return pipe 3b are connected, and the other ends of the suction pipe 3a and the return pipe 3b are connected to the flow path switching valve 4.

【0017】流路切替弁4には配管3c及び3dの一端
が接続され、配管3c及び3dの他端は本発明に係る浄
化装置5に接続され、吸上げ管3a、戻し管3b、配管
3c,3d、流路切替弁4および浄化装置5によって循
環路3が形成される。また配管3dの途中にはヒータ6
が設けられ、更に流路切替弁4からは排水管7が伸びて
いる。
One end of each of the pipes 3c and 3d is connected to the flow path switching valve 4, and the other end of each of the pipes 3c and 3d is connected to the purifying device 5 according to the present invention. The suction pipe 3a, the return pipe 3b, and the pipe 3c , 3d, the flow path switching valve 4, and the purifying device 5, the circulation path 3 is formed. In the middle of the pipe 3d, a heater 6 is provided.
And a drain pipe 7 extends from the flow path switching valve 4.

【0018】図2は前記浄化装置5の断面図であり、浄
化装置5内はステンレスメッシュ等の支持体8にて上下
の空間が仕切られ、支持体8上には物理除去用の濾過材
9が充填され、この濾過材9の上に、表面に形成した微
生物膜で浴槽水中に溶存する汚れ成分を分解するため生
物分解用の濾過材10が充填されている。これら濾過材
9,10には銀、銅等の重金属や有機系の抗菌剤を担持
せしめることが可能で、このようにすることで、浴槽水
の安全性が高まる。
FIG. 2 is a cross-sectional view of the purifying device 5. The inside of the purifying device 5 is divided into upper and lower spaces by a support 8 such as a stainless steel mesh. The filter material 9 is filled with a biodegradation filter material 10 for decomposing dirt components dissolved in bath water with a microbial membrane formed on the surface. These filtering materials 9 and 10 can carry a heavy metal such as silver or copper or an organic antibacterial agent, whereby the safety of bath water is improved.

【0019】濾過材9は、例えば、直径0.4〜1mm
のガラスビーズとし、濾過材10は、例えば、直径7m
mで長さが10mmの円柱状活性炭を用いる。そして、
これら濾過材9,10を浄化装置5内に250CCずつ
充填すると、濾過材9の方が濾過材10よりも比重が大
きいので、濾過材9が下方に濾過材10が上方になり、
更に濾過材9の上部と濾過材10の下部が重複する。
The filtering material 9 has a diameter of, for example, 0.4 to 1 mm.
And the filtering material 10 is, for example, 7 m in diameter.
A columnar activated carbon having a length of 10 m and a length of 10 mm is used. And
When these filtration materials 9 and 10 are filled into the purification device 5 by 250 CC each, the filtration material 9 has a higher specific gravity than the filtration material 10, so that the filtration material 9 becomes lower and the filtration material 10 becomes upper,
Furthermore, the upper part of the filter medium 9 and the lower part of the filter medium 10 overlap.

【0020】図3(a)は濾過材9としてのガラスビー
ズ表面の顕微鏡写真(150倍)、(b)は濾過材10
としての活性炭表面の顕微鏡写真(1000倍)であ
り、ガラスビーズは表面が平滑であり、且つそれ自身流
動性が大であるので、その表面には微生物膜は形成され
ていないが、活性炭表面には微生物膜が形成されている
ことが確認できる。
FIG. 3A is a photomicrograph (150 ×) of the surface of a glass bead serving as a filter medium 9, and FIG.
Is a micrograph (× 1000) of the surface of activated carbon as glass beads. Since the surface of glass beads is smooth and has a high fluidity, no microbial membrane is formed on the surface. Can be confirmed that a microbial membrane is formed.

【0021】次に、図4乃至図7に基づいて浄化装置の
作用を説明する。先ず、通常の濾過運転を継続して行く
と、図5(a)及び(b)に示すように、濾過材10の
表面に着床した菌により形成される微生物膜11が浴槽
水中の汚れ成分を捕捉・分解しながらも肥厚化し、また
濾過材9により汚濁物質が物理濾過される。
Next, the operation of the purifying device will be described with reference to FIGS. First, when the normal filtration operation is continued, as shown in FIGS. 5A and 5B, the microbial membrane 11 formed by the bacteria immobilized on the surface of the filter medium 10 causes the dirt component in the bathtub water to be removed. While thickening while trapping / decomposing, and pollutants are physically filtered by the filter medium 9.

【0022】そこで、図4に示すように、流路切替弁4
を操作して、浄化装置5への浴槽水の流入方向を逆にす
る。すると、図6(a)及び(b)に示すように、下方
から濾過材9が巻上げられ、濾過材9による衝突及びそ
の衝突による濾過材10自体の流動性向上によって濾過
材10表面の微生物膜11は適度に掻き取られて薄くな
り、また、濾過材9に付着している汚濁物質も同時に濾
過材9から剥離され、排水管7を介して外部に排出され
る。
Therefore, as shown in FIG.
To reverse the inflow direction of the bathtub water into the purification device 5. Then, as shown in FIGS. 6 (a) and 6 (b), the filter medium 9 is wound up from below, and the microbial membrane on the surface of the filter medium 10 due to the collision with the filter medium 9 and the improvement of the fluidity of the filter medium 10 itself due to the collision. Numeral 11 is appropriately scraped off and thinned, and pollutants adhering to the filter medium 9 are simultaneously peeled off from the filter medium 9 and discharged to the outside via the drain pipe 7.

【0023】以上の操作により、図7(a)及び(b)
に示すように、濾過材10表面には生物分解を行うのに
適度な厚みの微生物膜11が残され、常に衛生的な濾過
材の状態が維持される。
By the above operation, FIGS. 7A and 7B
As shown in (1), a microbial membrane 11 having an appropriate thickness for biodegradation is left on the surface of the filter medium 10, and the state of the sanitary filter medium is always maintained.

【0024】図8(a)〜(d)は浄化装置の別実施例
を示す断面図であり、図8(a)に示す実施例にあって
は、浄化装置5内を下段の支持体8及び上段の支持体1
2にて仕切り、下段の支持体8上には前記同様、物理除
去用の濾過材9を充填し、一方、上段の支持体12上に
は生物分解用の濾過材10を充填し、更に上段の支持体
12の目の粗さを下段の支持体8よりも大きくし、逆洗
時に濾過材9が支持体12を透過して濾過材10まで届
くようにしている。
FIGS. 8A to 8D are cross-sectional views showing another embodiment of the purifying apparatus. In the embodiment shown in FIG. And upper support 1
2, the lower support 8 is filled with the filter material 9 for physical removal as described above, while the upper support 12 is filled with the filter material 10 for biodegradation. The coarseness of the support 12 is larger than that of the lower support 8 so that the filter medium 9 permeates the support 12 and reaches the filter medium 10 during backwashing.

【0025】図8(b)に示す実施例にあっては、浄化
装置5の天井部から目の粗い材料からなる筒体13を垂
下し、この筒体13内に濾過材10を充填するようにし
ている。このような構成としても、逆洗時に濾過材9に
よって濾過材10表面の微生物膜を削り取ることができ
る。
In the embodiment shown in FIG. 8 (b), a cylindrical body 13 made of a coarse material is hung down from the ceiling of the purification device 5, and the filter medium 10 is filled in the cylindrical body 13. I have to. Even with such a configuration, the microbial membrane on the surface of the filter medium 10 can be scraped off by the filter medium 9 during backwashing.

【0026】図8(c)に示す実施例は、図8(b)に
示す実施例よりも濾過材9の層の厚みを大とし、濾過材
9の層内に濾過材10が埋没する構造にしている。この
ような構成としても、前記同様、逆洗時に濾過材10表
面の微生物膜を削り取ることができる。
In the embodiment shown in FIG. 8C, the thickness of the filter medium 9 is made larger than that of the embodiment shown in FIG. 8B, and the filter medium 10 is buried in the filter medium 9 layer. I have to. Even with such a configuration, the microbial membrane on the surface of the filter medium 10 can be scraped off at the time of backwashing, as described above.

【0027】図8(d)に示す実施例は、粒子状の濾過
材10を用いる代りに、活性体をハニカム状に成形した
濾過材10を用いている。粒子状の濾過材10を用いた
場合には、逆洗時に濾過材10の体積膨張を考慮した設
計を行わなければならなかったが、このように、濾過材
10をハニカム状とすることによって、濾過材10が膨
張することがなく、浄化装置5内の空間を有効に利用で
きる。
In the embodiment shown in FIG. 8D, instead of using the particulate filter material 10, a filter material 10 in which the active material is formed into a honeycomb shape is used. When the particulate filter medium 10 is used, a design considering the volume expansion of the filter medium 10 at the time of backwashing has to be performed. In this way, by forming the filter medium 10 into a honeycomb shape, The space inside the purification device 5 can be used effectively without the filter medium 10 expanding.

【0028】図9は別実施例に係る浴槽水の循環システ
ムの全体図であり、この実施例にあっては、戻し管3b
に殺菌手段14を設け、浴槽水の安全性を高めている。
殺菌手段としては、紫外線ランプ、オゾン発生器、電解
殺菌装置等が考えられる。
FIG. 9 is an overall view of a bathtub water circulation system according to another embodiment. In this embodiment, a return pipe 3b is provided.
Is provided with a sterilizing means 14 to enhance the safety of bathtub water.
Examples of the sterilizing means include an ultraviolet lamp, an ozone generator, and an electrolytic sterilizing device.

【0029】[0029]

【発明の効果】以上に説明した如く本発明の浄化装置よ
れば、逆洗時等に、浴槽水中の汚れ成分を物理的に除去
する物理除去用の濾過材によって、生物分解用の濾過材
の表面に必要以上の厚さで形成された微生物膜を掻き取
るようにしたので、常に適切な厚さの微生物膜を濾過材
の表面に維持することができる。
As described above, according to the purification apparatus of the present invention, the filter material for biodegradation can be removed by the filter material for physical removal that physically removes dirt components in bath water during backwashing. Since the microbial membrane formed with a thickness more than necessary on the surface is scraped off, a microbial membrane having an appropriate thickness can always be maintained on the surface of the filter medium.

【0030】以下の(表1)は、従来の濾過材と本願発
明の濾過材の表面に寄宿するレジオネラ属菌数を比較し
たものである。この(表1)から、常に適切な厚さの微
生物膜が形成される濾過材にあっては、レジオネラ属菌
の繁殖の温床になりにくいことが分かる。
The following (Table 1) compares the numbers of Legionella genus living on the surface of the conventional filter medium and the filter medium of the present invention. From this (Table 1), it can be seen that a filter medium in which a microbial membrane having an appropriate thickness is always formed does not easily become a breeding ground for propagation of Legionella spp.

【0031】[0031]

【表1】 [Table 1]

【0032】また以下の(表2)は、従来の濾過材と本
願発明の更なる具体的な濾過材の表面に寄宿するレジオ
ネラ属菌数を比較したものである。尚、浄化装置として
図2に示す構造のものを用い、物理除去用の濾過材は嵩
比重1.5g/ccで直径0.8mmのガラスビーズと
し、生物分解用の濾過材は嵩比重0.5g/ccで直径
4mm、長さ3mm且つ無機バインダーを50%配合し
た円柱状活性炭とし、ガラスビーズ(物理除去用の濾過
材)を150cc、円柱状活性炭(生物分解用の濾過
材)を700cc、同一の浄化筒に充填した。そして、
通常の濾過運転時には図5に示すように比重差によって
ガラスビーズ(物理除去用の濾過材)が下方に、円柱状
活性炭(生物分解用の濾過材)が上方になり、更にガラ
スビーズ(物理除去用の濾過材)の上部と円柱状活性炭
(生物分解用の濾過材)の下部が重複した形態で構成さ
れ濾過・浄化し、また、逆洗時には図6に示すように、
ガラスビーズ(物理除去用の濾過材)と円柱状活性炭
(生物分解用の濾過材)とが同時に攪拌され、均一な流
動性を示すことによってガラスビーズ(物理除去用の濾
過材)に付着している汚濁物質が剥離し、円柱状活性炭
(生物分解用の濾過材)の表面に形成される過剰な微生
物膜は適度に掻き取られてゆく。更に逆洗終了後は図7
に示すように、比重差によって通常の濾過運転時の形態
に戻った。
The following (Table 2) compares the numbers of Legionella bacteria that lodge on the surfaces of the conventional filter material and further specific filter materials of the present invention. In addition, a purifying apparatus having a structure shown in FIG. 2 was used, a filter medium for physical removal was glass beads having a bulk specific gravity of 1.5 g / cc and a diameter of 0.8 mm, and a filter medium for biodegradation had a bulk specific gravity of 0.1 mm. 5 g / cc, 4 mm in diameter, 3 mm in length, and 50% of an inorganic binder were blended into a columnar activated carbon. The same purifying column was filled. And
During normal filtration operation, as shown in FIG. 5, due to the difference in specific gravity, the glass beads (filter material for physical removal) move downward, the columnar activated carbon (filter material for biodegradation) moves upward, and further the glass beads (filter material for physical removal). The upper part of the filter material for filtration) and the lower part of the columnar activated carbon (the filter material for biodegradation) are formed in an overlapping form to filter and purify. In addition, as shown in FIG.
The glass beads (filter material for physical removal) and the columnar activated carbon (filter material for biodegradation) are simultaneously stirred and adhere to the glass beads (filter material for physical removal) by exhibiting uniform fluidity. The excess contaminants are exfoliated, and the excess microbial membrane formed on the surface of the columnar activated carbon (filter material for biodegradation) is appropriately scraped off. After the backwash is completed,
As shown in the figure, the state returned to the normal filtration operation due to the difference in specific gravity.

【0033】[0033]

【表2】 [Table 2]

【0034】また、濾過材表面に常に適切な厚さの微生
物膜が形成される結果、効果的な汚れ成分の分解がなさ
れ、また、微生物膜が剥離してスライム状になって浴槽
内に戻ることもなくなる。
In addition, as a result of the formation of a microbial membrane of an appropriate thickness on the surface of the filter medium, the soil components are effectively decomposed, and the microbial membrane is peeled off and returned to the bath as a slime. No more.

【0033】更に本発明に係る循環システムによれば、
バルブ操作によって流路を切り替えることで、逆洗運転
にすることができるので、所定時間毎に自動的に逆洗モ
ードにするだけで、適切な厚さの微生物膜を濾過材の表
面に維持することができる。
Further, according to the circulation system of the present invention,
The backwashing operation can be performed by switching the flow path by operating the valve, so that the microbial membrane of an appropriate thickness is maintained on the surface of the filter medium only by automatically setting the backwash mode at predetermined time intervals. be able to.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明に係る浄化装置を組み込んだ浴槽水の循
環システムの全体図
FIG. 1 is an overall view of a bathtub water circulation system incorporating a purification device according to the present invention.

【図2】本発明に係る浄化装置の断面図FIG. 2 is a sectional view of a purification device according to the present invention.

【図3】(a)はガラスビーズ表面の顕微鏡写真、
(b)は活性炭表面の顕微鏡写真
FIG. 3 (a) is a micrograph of a glass bead surface,
(B) Micrograph of activated carbon surface

【図4】逆洗時の浴槽水の流れを示す図1と同様の循環
システムの全体図
FIG. 4 is an overall view of a circulation system similar to FIG. 1, showing the flow of bathtub water during backwashing.

【図5】(a)は活性炭表面に微生物膜が厚く形成され
た状態の浄化装置の断面図、(b)は(a)に示す活性
炭の拡大図
5 (a) is a cross-sectional view of a purification device in which a microbial membrane is formed thick on the activated carbon surface, and (b) is an enlarged view of the activated carbon shown in (a).

【図6】(a)は浄化装置を逆洗している状態の断面
図、(b)は(a)に示す活性炭の拡大図
6 (a) is a cross-sectional view of a state where the purification device is being backwashed, and FIG. 6 (b) is an enlarged view of the activated carbon shown in FIG. 6 (a).

【図7】(a)は浄化装置を逆洗した後の状態の断面
図、(b)は(a)に示す活性炭の拡大図
FIG. 7A is a cross-sectional view of the state after the cleaning device has been backwashed, and FIG. 7B is an enlarged view of the activated carbon shown in FIG.

【図8】(a)〜(d)は浄化装置の別実施例を示す断
面図
FIGS. 8A to 8D are cross-sectional views showing another embodiment of the purification device.

【図9】別実施例に係る浴槽水の循環システムの全体図FIG. 9 is an overall view of a bathtub water circulation system according to another embodiment.

【図10】従来の浄化装置を組み込んだ循環システムの
全体図
FIG. 10 is an overall view of a circulation system incorporating a conventional purification device.

【図11】従来の浄化装置の別例を示す断面図FIG. 11 is a sectional view showing another example of the conventional purification device.

【符号の説明】[Explanation of symbols]

1…浴槽、2…バスアダプタ、3…循環路、3a…吸上
げ管、3b…戻し管、3c,3d…配管、4…流路切替
弁、5…浄化装置、6…ヒータ、7…排水管、8,12
…支持体、9…物理除去用の濾過材、10…生物分解用
の濾過材、11…微生物膜、14…殺菌手段。
DESCRIPTION OF SYMBOLS 1 ... bathtub, 2 ... bus adapter, 3 ... circulation path, 3a ... suction pipe, 3b ... return pipe, 3c, 3d ... piping, 4 ... flow path switching valve, 5 ... purification device, 6 ... heater, 7 ... drainage Tubes, 8,12
... Support, 9 ... Filter for physical removal, 10 ... Filter for biodegradation, 11 ... Microbial membrane, 14 ... Sterilization means.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI B01D 39/14 C02F 1/28 D C02F 1/28 1/50 510A 1/50 510 520L 520 531D 531 540F 540 550B 550 550H 560B 560 560H 560Z 3/06 ZAB 3/06 ZAB 3/10 A 3/10 B01D 29/08 530D 540A 35/02 J (72)発明者 木下 崇 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内 (72)発明者 本山 英俊 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内 (72)発明者 金丸 宏 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI B01D 39/14 C02F 1/28 D C02F 1/28 1/50 510A 1/50 510 520L 520 531D 531 540F 540 550B 550 550H 560B 560 560H 560Z 3/06 ZAB 3/06 ZAB 3/10 A 3/10 B01D 29/08 530D 540A 35/02 J (72) Inventor Takashi Kinoshita 2-1-1 Nakajima, Kokurakita-ku, Kitakyushu City, Fukuoka Prefecture Inside Equipment Co., Ltd. (72) Inventor Hidetoshi Motoyama 2-1-1 Nakajima, Kokurakita-ku, Kitakyushu-city, Fukuoka Prefecture Inside Totoki Equipment Co., Ltd. (72) Inventor Hiroshi Kanamaru 2-1-1 Nakajima, Kokurakita-ku, Kitakyushu-city, Fukuoka Prefecture No. 1 Toto Kiki Co., Ltd.

Claims (13)

【特許請求の範囲】[Claims] 【請求項1】 浴槽水中の汚れ成分を分解する微生物膜
を表面に形成した生物分解用の濾過材と、浴槽水中のゴ
ミ等を物理的に除去する物理除去用の濾過材とを備えた
浴槽水の浄化装置において、前記物理除去用の濾過材は
逆洗時に生物分解用の濾過材の表面に形成されている微
生物膜を掻き取ることが可能な態様で配置されているこ
とを特徴とする浴槽水の浄化装置。
1. A bath tub comprising a biodegradation filter having a microbial membrane formed on a surface thereof for decomposing a dirt component in bath tub water, and a physical removal filter for physically removing dust and the like in the bath tub water. In the water purification device, the filter material for physical removal is arranged in a manner capable of scraping a microbial membrane formed on a surface of the filter material for biodegradation during backwashing. Bathtub water purification equipment.
【請求項2】 請求項1に記載の浴槽水の浄化装置にお
いて、前記物理除去用の濾過材は生物分解用の濾過材よ
りも小径で且つ比重が大であることを特徴とする浴槽水
の浄化装置。
2. The bathtub water purifying apparatus according to claim 1, wherein the filter material for physical removal has a smaller diameter and a larger specific gravity than a filter material for biodegradation. Purification device.
【請求項3】 請求項1に記載の浴槽水の浄化装置にお
いて、前記生物分解用の濾過材はハニカム構造体であ
り、前記物理除去用の濾過材は前記ハニカム構造体の孔
内を流動するのに十分な粒径であることを特徴とする浴
槽水の浄化装置。
3. The bathtub water purifying apparatus according to claim 1, wherein the filter material for biodegradation is a honeycomb structure, and the filter material for physical removal flows in the holes of the honeycomb structure. A bath tub water purifier characterized by having a particle size sufficient for water.
【請求項4】 請求項2に記載の浴槽水の浄化装置にお
いて、前記物理除去用の濾過材の粒径は0.4〜1m
m、前記生物分解用の濾過材の粒径は3mm以上である
ことを特徴とする浴槽水の浄化装置。
4. The bath tub water purifying apparatus according to claim 2, wherein the particle size of the filter medium for physical removal is 0.4 to 1 m.
m, a bath tub water purification apparatus, wherein the particle size of the biodegradation filter material is 3 mm or more.
【請求項5】 請求項2または請求項3に記載の浴槽水
の浄化装置において、前記物理除去用の濾過材と生物分
解用の濾過材とはその一部が重なるように配置されるこ
とを特徴とする浴槽水の浄化装置。
5. The bathtub water purifier according to claim 2, wherein the filter material for physical removal and the filter material for biodegradation are arranged so that a part thereof overlaps. Bathtub water purifier characterized.
【請求項6】 請求項2または請求項3に記載の浴槽水
の浄化装置において、前記物理除去用の濾過材はガラス
ビーズ、アルミナビーズ等の無機ビーズであり、前記生
物分解用の濾過材は活性炭であることを特徴とする浴槽
水の浄化装置。
6. The bathtub water purifying apparatus according to claim 2, wherein the filter material for physical removal is inorganic beads such as glass beads and alumina beads, and the filter material for biodegradation is A bathtub water purifier characterized by being activated carbon.
【請求項7】 請求項2または請求項3に記載の浴槽水
の浄化装置において、前記物理除去用または生物分解用
の濾過材には抗菌剤が担持されていることを特徴とする
浴槽水の浄化装置。
7. The bathtub water purifying apparatus according to claim 2, wherein an antimicrobial agent is carried on the filter material for physical removal or biodegradation. Purification device.
【請求項8】 請求項2または請求項4に記載の浴槽水
の浄化装置において、前記生物分解用の濾過材は活性炭
に無機バインダーを配合していることを特徴とする浴槽
水の浄化装置。
8. The bathtub water purifying apparatus according to claim 2, wherein the filter material for biodegradation contains activated carbon and an inorganic binder.
【請求項9】 請求項8に記載の浴槽水の浄化装置にお
いて、前記生物分解用の濾過材は活性炭に無機バインダ
ーを30〜70wt%配合していることを特徴とする浴
槽水の浄化装置。
9. The bathtub water purifying apparatus according to claim 8, wherein the filter material for biodegradation contains 30 to 70 wt% of an inorganic binder in activated carbon.
【請求項10】 請求項8に記載の浴槽水の浄化装置に
おいて、前記生物分解用の濾過材の活性炭に対する無機
バインダーの配合割合は、物理浄化用の濾過材と生物分
解用の濾過材との嵩比重が1.5:0.5〜1.5:
0.7となる割合であることを特徴とする浴槽水の浄化
装置。
10. The bathtub water purifying apparatus according to claim 8, wherein the mixing ratio of the inorganic binder to the activated carbon of the biodegradation filter material is determined by the ratio of the physical purification filter material to the biodegradation filter material. The bulk specific gravity is 1.5: 0.5 to 1.5:
A bathtub water purifier characterized by a ratio of 0.7.
【請求項11】 請求項8乃至請求項10に記載の浴槽
水の浄化装置において、前記物理浄化用の濾過材と生物
分解用の濾過材との容積比が5:70〜2:7となるよ
うに充填されていることを特徴とする浴槽水の浄化装
置。
11. The bathtub water purifying apparatus according to claim 8, wherein a volume ratio of the filtering material for physical purification and the filtering material for biodegradation is 5:70 to 2: 7. Bath water purifier characterized by being filled as follows.
【請求項12】 浴槽水を取り出して再び浴槽に戻す循
環経路の途中に請求項1乃至請求項11に記載の浄化装
置を配置したことを特徴とする浴槽水の循環システム。
12. A bathtub water circulation system, wherein the purifying device according to claim 1 is arranged in a circulation path for taking out bathtub water and returning it to the bathtub again.
【請求項13】 請求項12に記載の浴槽水の循環シス
テムにおいて、前記循環経路には殺菌手段を設けたこと
を特徴とする浴槽水の循環システム。
13. The bathtub water circulation system according to claim 12, wherein sterilization means is provided in said circulation path.
JP10315798A 1997-11-10 1998-11-06 Purification device of bathtub water and circulating system of bathtub water Pending JPH11216306A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10315798A JPH11216306A (en) 1997-11-10 1998-11-06 Purification device of bathtub water and circulating system of bathtub water

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP30692997 1997-11-10
JP9-306929 1997-11-10
JP10315798A JPH11216306A (en) 1997-11-10 1998-11-06 Purification device of bathtub water and circulating system of bathtub water

Publications (1)

Publication Number Publication Date
JPH11216306A true JPH11216306A (en) 1999-08-10

Family

ID=26564916

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10315798A Pending JPH11216306A (en) 1997-11-10 1998-11-06 Purification device of bathtub water and circulating system of bathtub water

Country Status (1)

Country Link
JP (1) JPH11216306A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006159130A (en) * 2004-12-09 2006-06-22 Toyohashi Univ Of Technology Control method of excess sludge generation
JP2013192982A (en) * 2012-03-16 2013-09-30 Ishigaki Co Ltd Filter
JP2013202560A (en) * 2012-03-29 2013-10-07 Ishigaki Co Ltd Deep layer filtration device
CN106007225A (en) * 2016-07-18 2016-10-12 程晨 Assembled water treatment unit and operating method thereof
CN106006960A (en) * 2016-07-18 2016-10-12 广德清源水处理设备有限公司 Anoxic baffled reactor and operation method thereof
CN106045211A (en) * 2016-07-18 2016-10-26 芮少春 Oxidation ditch wastewater purification process and operation method thereof
CN106045022A (en) * 2016-07-18 2016-10-26 程晨 Oxidation ditch process and application method thereof
JP2023537040A (en) * 2020-08-05 2023-08-30 アクセプタンス グループ インコーポレイテッド Biofilter with shaped underdrain assembly

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006159130A (en) * 2004-12-09 2006-06-22 Toyohashi Univ Of Technology Control method of excess sludge generation
JP2013192982A (en) * 2012-03-16 2013-09-30 Ishigaki Co Ltd Filter
JP2013202560A (en) * 2012-03-29 2013-10-07 Ishigaki Co Ltd Deep layer filtration device
CN106007225A (en) * 2016-07-18 2016-10-12 程晨 Assembled water treatment unit and operating method thereof
CN106006960A (en) * 2016-07-18 2016-10-12 广德清源水处理设备有限公司 Anoxic baffled reactor and operation method thereof
CN106045211A (en) * 2016-07-18 2016-10-26 芮少春 Oxidation ditch wastewater purification process and operation method thereof
CN106045022A (en) * 2016-07-18 2016-10-26 程晨 Oxidation ditch process and application method thereof
JP2023537040A (en) * 2020-08-05 2023-08-30 アクセプタンス グループ インコーポレイテッド Biofilter with shaped underdrain assembly

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