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JP3237337B2 - Bath water purification method and purification device - Google Patents
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JP3237337B2 - Bath water purification method and purification device - Google Patents

Bath water purification method and purification device

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Publication number
JP3237337B2
JP3237337B2 JP23948993A JP23948993A JP3237337B2 JP 3237337 B2 JP3237337 B2 JP 3237337B2 JP 23948993 A JP23948993 A JP 23948993A JP 23948993 A JP23948993 A JP 23948993A JP 3237337 B2 JP3237337 B2 JP 3237337B2
Authority
JP
Japan
Prior art keywords
filter
bath water
shear stress
water
mass transfer
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.)
Expired - Fee Related
Application number
JP23948993A
Other languages
Japanese (ja)
Other versions
JPH0796114A (en
Inventor
正吉 桁山
純子 福田
信吾 佐藤
伸太郎 幡手
恵美香 小川
太門 木村
卓男 今坂
高生 寺岡
Original Assignee
東陶機器株式会社
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 東陶機器株式会社 filed Critical 東陶機器株式会社
Priority to JP23948993A priority Critical patent/JP3237337B2/en
Publication of JPH0796114A publication Critical patent/JPH0796114A/en
Application granted granted Critical
Publication of JP3237337B2 publication Critical patent/JP3237337B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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

  • Bathtub Accessories (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Filtration Of Liquid (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は浴槽や小型プール等の浴
水槽内の水を浄化する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for purifying water in a bathtub such as a bathtub or a small pool.

【0002】[0002]

【従来の技術】従来から浴槽の水を濾過装置を用いて浄
化し、洗濯水等に再利用することが行われている。この
濾過装置としてはフィルターや金網等のストレーナを容
器内に充填したものが一般的であるが、浴槽の水には湯
垢などが含まれており、目詰りを起こす。そこで、実開
昭60−79514号公報では、浄化する浴槽水に乱流
を起こさせて付着した湯垢を取り除くようにしている。
2. Description of the Related Art Conventionally, water in a bathtub is purified using a filtration device and reused as washing water. As this filtering device, a device in which a strainer such as a filter or a wire net is filled in a container is generally used. However, the water in the bath tub contains scale and causes clogging. Therefore, in Japanese Utility Model Laid-Open No. 60-79514, turbulence is caused in the bath water to be purified to remove attached scale.

【0003】一方最近では、浴槽やプールの水を捨てる
ことなく、浄化して再び元に戻して水の無駄使いをなく
すシステムが開発されており、このようなシステムでは
濾過装置の濾材表面に水中の有機物を分解する微生物等
を繁殖させ、物理的な浄化の他に生物的な浄化を行うよ
うにしている。
On the other hand, recently, a system has been developed in which the water in a bathtub or a pool is purified without being discarded and returned again to eliminate waste of water. Microorganisms that decompose organic substances are propagated, and biological purification is performed in addition to physical purification.

【0004】[0004]

【発明が解決しようとする課題】上述した生物浄化処理
を伴なう濾過においても、水垢等による目詰りが生じ得
る。そこで、実開昭60−79514号公報に開示され
るように乱流を生じさせて目詰りを防止することが考え
られるが、単に乱流にするだけでは生物膜の剥離を生
じ、却って生物浄化効率が低下することになる。
In the filtration accompanied by the biological purification treatment described above, clogging due to water scale or the like may occur. Therefore, it is conceivable to prevent clogging by generating a turbulent flow as disclosed in Japanese Utility Model Application Laid-Open No. 60-79514. Efficiency will be reduced.

【0005】[0005]

【課題を解決するための手段】上記課題を解決すべく本
発明は、表面に生物膜が付着した濾材を充填した濾過器
内における浴水槽水の物質移動係数が0.036[m/h]以上
かつ剪断応力が1.1×107[kg/m・h2]以下となるように
した。ここで、物質移動係数及び剪断応力を調整するに
は浴水槽水の流量、濾材の空間率若しくは空塔速度を調
整する。また、濾過器を複数個直列に配置し、各濾過器
に充填している濾材が異なる場合には濾過器の流路断面
積を異ならせることで、各濾過器における浴水槽水の物
質移動係数が0.036[m/h]以上かつ剪断応力が1.1×107
[kg/m・h2]以下となるようにする。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention provides a filter in which the mass transfer coefficient of bath water in a filter filled with a filter medium having a biofilm adhered on its surface is 0.036 [m / h] or more. The shear stress was adjusted to be 1.1 × 10 7 [kg / m · h 2 ] or less. Here, in order to adjust the mass transfer coefficient and the shear stress, the flow rate of the bath water, the porosity of the filter medium, or the superficial velocity are adjusted. In addition, a plurality of filters are arranged in series, and when the filter material filled in each filter is different, the mass transfer coefficient of bath water in each filter is changed by changing the flow path cross-sectional area of the filter. Is 0.036 [m / h] or more and the shear stress is 1.1 × 10 7
[Kg / m · h 2 ] or less.

【0006】[0006]

【作用】層流状態では濾材表面に付着した生物膜に対し
て処理水が直線的に流れるため、生物浄化効率は高くな
らない。逆に乱流状態が過度になると、生物膜の剥離が
生じる。そこで、効率良く生物処理を行うには物質移動
係数及び剪断応力を指標として浄化条件を定める。
In the laminar flow state, the treated water flows linearly to the biofilm attached to the surface of the filter medium, so that the biological purification efficiency does not increase. Conversely, excessive turbulence conditions can cause biofilm detachment. Therefore, in order to efficiently perform biological treatment, purification conditions are determined using the mass transfer coefficient and the shear stress as indices.

【0007】[0007]

【実施例】以下に本発明の実施例を添付図面に基づいて
説明する。ここで、図1は本発明に係る浴水槽水の浄化
方法を適用した循環浄化システムの全体図、図2は本発
明に係る浄化の実施に用いる濾過装置の縦断面図であ
り、循環浄化システムは、浴槽1、浴槽1内の水を取り
出して再び浴槽1に戻す主循環経路2、逆洗用の副循環
経路3及び浴槽水を生物浄化する濾過装置10を備えて
いる。
Embodiments of the present invention will be described below with reference to the accompanying drawings. Here, FIG. 1 is an overall view of a circulating purification system to which the method for purifying bathtub water according to the present invention is applied, and FIG. 2 is a longitudinal sectional view of a filtration device used for performing purification according to the present invention. Includes a bathtub 1, a main circulation path 2 for taking out water from the bathtub 1 and returning it to the bathtub 1 again, a sub-circulation path 3 for backwashing, and a filtering device 10 for biologically purifying the bathtub water.

【0008】主循環経路2は管路2a,2b,2c,2
d,2eから構成され副循環経路3は管路3a,2d,
3b,3c,2b,3d及び排出管3eから構成されて
いる。即ち主循環経路2と副循環経路3とは2b,2d
及び2cの一部を共通管路とし、共通の管路2bには循
環ポンプ4を、共通の管路2dにはヒータ5及び紫外線
殺菌装置6を、更に管路3aにはバルブを備えたエア配
管7からのエアを導入するエジェクタ8をそれぞれ設け
ている。
[0008] The main circulation path 2 includes pipes 2a, 2b, 2c, 2
d, 2e, and the auxiliary circulation path 3 is provided with pipes 3a, 2d,
3b, 3c, 2b, 3d and a discharge pipe 3e. That is, the main circulation path 2 and the sub circulation path 3 are 2b, 2d
, A part of 2c as a common pipe, a common pipe 2b with a circulating pump 4, a common pipe 2d with a heater 5 and an ultraviolet sterilizer 6, and a pipe 3a with air provided with a valve. An ejector 8 for introducing air from the pipe 7 is provided.

【0009】また、管路2a,2b,3cの交点には三
方弁V1を、管路2b,2c,3aの交点には三方弁V2
を、管路2d,2e,3bの交点には三方弁V3を、管
路3c,3d,3eの交点には三方弁V4を設けてい
る。尚、三方弁の代りにスプール弁等任意の管路切り換
え手段を用いることができる。
Further, the conduit 2a, 2b, the three-way valve V 1 was at the intersection of 3c, the conduit 2b, 2c, the three-way valve V 2 is the intersection of 3a
A conduit 2d, 2e, a three-way valve V 3 is the intersection of 3b, the conduit 3c, 3d, are provided three-way valve V 4 is the intersection of 3e. Incidentally, any pipe switching means such as a spool valve can be used instead of the three-way valve.

【0010】一方、濾過装置10は図2に示すように円
筒状本体11の上面をエア抜き弁12を備えた蓋体13
で閉塞し、また本体11の上部側面には浴水槽水の流入
口14を設け、本体11の底部中央には浴槽水の流出口
15を設け、この流出口15の中心に逆洗用流入口16
を設け、この逆洗用流入口16の本体内に臨む部分には
前記流出口15に逆洗時にエアが巻き込まれるのを防止
する邪魔板17を取り付けている。尚、本体11の底部
側面には濾過通水時に濾材から剥離した汚泥をドレイン
部25に溜め、溜めた汚泥を排出するためのドレインパ
イプ18を設けている。
On the other hand, as shown in FIG. 2, a filter device 10 is provided with a lid 13 provided with an air vent valve 12 on the upper surface of a cylindrical main body 11.
A bath water inlet 14 is provided on the upper side surface of the main body 11, and a bath water outlet 15 is provided at the center of the bottom of the main body 11. A back washing inlet is provided at the center of the outlet 15. 16
A baffle plate 17 is attached to a portion of the backwashing inlet 16 facing the main body to prevent air from being trapped in the outlet 15 during backwashing. In addition, a drain pipe 18 is provided on the bottom side surface of the main body 11 for storing sludge separated from the filter medium at the time of filtration water passage in a drain portion 25 and discharging the stored sludge.

【0011】また、円筒状本体11内にはカートリッジ
状の濾過器21,22を上下に2段直列に重ねて配置し
ている。これら濾過器21,22はバケツ状をなし、底
面には通水方向に貫通する孔21a、22aを形成して
いる。
Further, in the cylindrical main body 11, filter units 21 and 22 in the form of cartridges are arranged vertically one above the other in two stages. These filters 21 and 22 are formed in a bucket shape, and have holes 21a and 22a penetrating in the water flow direction on the bottom surface.

【0012】そして、濾過器21内には濾材23として
粒状或いは球状の麦飯石を充填している。尚、麦飯石の
代りに美濃活性石、美濃セラミックボール、鉱物をセメ
ント系バインダーで固めた濾材、ケイソウ土原料からな
る濾材、三次元網目構造のセラミックフォーム或いは繊
維状の濾材等を用いてもよい。また、濾過器22内には
活性炭を一定方向に複数の貫通孔を有するハニカム形状
に成形した濾材24を納めている。
The filter 21 is filled with granular or spherical malt stone as a filter medium 23. In addition, instead of barley stone, Mino active stone, Mino ceramic balls, a filter medium obtained by solidifying a mineral with a cement-based binder, a filter medium composed of diatomaceous earth raw material, a ceramic foam having a three-dimensional network structure, or a fibrous filter medium may be used. . In the filter 22, a filter medium 24 formed by forming activated carbon into a honeycomb shape having a plurality of through holes in a certain direction is placed.

【0013】ここで、前記濾材23,24の表面には処
理水(浴水槽水)中の有機物を分解する微生物等からな
る生物膜が繁殖して付着しており、この生物膜による生
物浄化に適した条件を以下に述べる。
Here, on the surfaces of the filter media 23 and 24, a biofilm composed of microorganisms or the like that decomposes organic substances in the treated water (bath water) propagates and adheres. Suitable conditions are described below.

【0014】先ず、実施例の濾過装置10は2つの濾過
器21,22を直列に配置しているので、上部の濾過器
21における条件について下部の濾過器22を外して考
察する。尚、条件を決定するにあたっての剪断応力
(τ)、物質移動係数(kc)、一次反応速度定数
(k)の算出式は以下の(数1)、(数2)及び(数
3)に従った。
First, in the filter device 10 of the embodiment, since two filters 21 and 22 are arranged in series, the conditions in the upper filter 21 will be considered with the lower filter 22 removed. The formulas for calculating the shear stress (τ), the mass transfer coefficient (kc), and the first-order reaction rate constant (k) in determining the conditions follow the following (Equation 1), (Equation 2) and (Equation 3). Was.

【0015】[0015]

【数1】 (Equation 1)

【数2】 (Equation 2)

【数3】 (Equation 3)

【0016】上部の平均粒子径4.5mmの麦飯石を充
填した濾過器21に送り込む浴槽水の量を徐々に多く
し、空塔速度を高めてゆくと(表1)に示すように4.
5m/hで生物膜への物質移動が促進され、生物浄化機
能が働き、更に空塔速度を高めてゆくと160m/hで
剪断応力による生物膜の剥離が生じた。
The amount of bath water to be fed into the filter 21 filled with barley stone having an average particle diameter of 4.5 mm in the upper part was gradually increased, and the superficial velocity was increased as shown in Table 1.
At 5 m / h, mass transfer to the biofilm was promoted, the biological purification function worked, and when the superficial velocity was further increased, the biofilm was peeled off at 160 m / h due to shear stress.

【0017】[0017]

【表1】 [Table 1]

【0018】更に、任意の9点において測定した空塔速
度、物質移動係数(kc)、剪断応力(τ)、一次反応
速度定数(k)を(表2)に示すとともに物質移動係数
(kc)と一次反応速度定数(k)との関係を図3に示
す。同様に剪断応力(τ)と一次反応速度定数(k)と
の関係を図4に示す。ここで、一次反応速度定数(k)
は式で表わされ、k値が大きいほど急速に有機物が分
解されることになる。
Further, the superficial velocity, mass transfer coefficient (kc), shear stress (τ) and first-order reaction rate constant (k) measured at arbitrary 9 points are shown in Table 2 and the mass transfer coefficient (kc) FIG. 3 shows the relationship between and the first-order reaction rate constant (k). Similarly, FIG. 4 shows the relationship between the shear stress (τ) and the first-order reaction rate constant (k). Here, the first-order reaction rate constant (k)
Is represented by the formula, and the larger the k value, the more rapidly organic substances are decomposed.

【0019】[0019]

【表2】 [Table 2]

【0020】浴槽水に持込まれる有機物成分は、24時
間以内に分解されて、翌日は、再度きれいな水になって
いる必要がある。もし、前日より水が汚れていると、浄
化が不十分であり、汚れが蓄積していくことを意味す
る。よって、24時間以内にその日持ち込まれた有機物
をほぼ完全に浄化することが、必要条件となる。仮りに
24時間で有機物濃度が初期値の1/100になったと
すると、1次反応速度(k)は、k=ln(So/St)/
t=ln100/24=0.19[l/h]となる。即ち、
1次反応速度(k)は0.19以上は最低限必要である
ということになる。
The organic components brought into the bathtub water must be decomposed within 24 hours, and the next day, the water must be clean again. If the water is dirty from the previous day, it means that purification is insufficient and the dirt accumulates. Therefore, it is a necessary condition that the organic matter brought in that day is almost completely purified within 24 hours. Assuming that the organic matter concentration becomes 1/100 of the initial value in 24 hours, the first-order reaction rate (k) is k = ln (So / St) /
t = ln100 / 24 = 0.19 [l / h]. That is,
It means that the first-order reaction rate (k) must be at least 0.19 or more.

【0021】上記(表2)、図3及び図4から、一次反
応速度定数(k)は物質移動係数(kc)が増加するに
つれて高くなり、剪断応力(τ)が大きくなるにつれて
低くなる。このように、物質移動係数(kc)及び剪断
応力(τ)と一次反応速度定数(k)とは一定の関係が
あり、一次反応速度定数(k)を高めるには、物質移動
係数(kc)が0.036[m/h]以上、剪断応力(τ)が1.
1×107[kg/m・h2]以下、好ましくは物質移動係数(k
c)が0.049[m/h]以上、剪断応力(τ)が1.3×10
6[kg/m・h2]以下(k≧0.38)となるように浴水槽水の
流量、濾材の空間率若しくは空塔速度を調整する。
From Table 2 above and FIGS. 3 and 4, the first-order rate constant (k) increases as the mass transfer coefficient (kc) increases, and decreases as the shear stress (τ) increases. As described above, the mass transfer coefficient (kc) and the shear stress (τ) have a fixed relationship with the first-order reaction rate constant (k). To increase the first-order reaction rate constant (k), the mass transfer coefficient (kc) Is 0.036 [m / h] or more and the shear stress (τ) is 1.
1 × 10 7 [kg / m · h 2 ] or less, preferably a mass transfer coefficient (k
c) is 0.049 [m / h] or more, and the shear stress (τ) is 1.3 × 10
6 Adjust the flow rate of the bath water, the porosity of the filter medium, or the superficial velocity so that it is less than 6 [kg / m · h 2 ] (k ≧ 0.38).

【0022】次に、濾材としてセルサイズ1.5mmの
活性炭ハニカムを用いた下部の濾過器22のみをセット
して下部の濾過器22における条件について考察する。
下部の濾過器22においては前記(表1)に示すように
空塔速度が560m/hで剪断応力によって生物膜の剥
離が生じた。ただし、下部の濾過器22では空塔速度が
50m/h以上であれば十分な浄化が行えた。
Next, only the lower filter 22 using activated carbon honeycomb having a cell size of 1.5 mm as a filter medium is set, and conditions in the lower filter 22 will be considered.
In the lower filter 22, as shown in the above (Table 1), the biofilm was peeled off by the shear stress at the superficial velocity of 560 m / h. However, in the lower filter 22, if the superficial velocity was 50 m / h or more, sufficient purification could be performed.

【0023】因みに、実施例にあっては20リットル/分の
容量のポンプを用いて浴槽水を濾過装置に送り込むよう
にしており、上部の濾過器21の直径D1は18cmで
あるので、式から実際の空塔速度は47m/hであ
り、この時の物質移動係数(kc)は0.12[m/h]であ
り、剪断応力(τ)は1.6×106[kg/m・h2]である。ま
た下部の濾過器22の直径D2は16.5cmであり物
質移動係数(kc)は0.038[m/h]であり、剪断応力
(τ)は1.2×106[kg/m・h2]である。
By the way, in the embodiment, the bath water is fed into the filtration device by using a pump having a capacity of 20 liter / min, and the diameter D 1 of the upper filter 21 is 18 cm. Therefore, the actual superficial velocity is 47 m / h, the mass transfer coefficient (kc) at this time is 0.12 [m / h], and the shear stress (τ) is 1.6 × 10 6 [kg / m · h 2 ]. It is. The diameter D 2 of the lower filter 22 is 16.5 cm, the mass transfer coefficient (kc) is 0.038 [m / h], and the shear stress (τ) is 1.2 × 10 6 [kg / m · h 2 ]. It is.

【0024】[0024]

【発明の効果】以上に説明した如く本発明によれば、表
面に生物膜が付着した濾材を充填した濾過器内での浴水
槽水の物質移動係数が0.036[m/h]以上かつ剪断応力が
1.1×107[kg/m・h2]以下となるようにしたので、剪断
応力が生物膜を剥離することなくしかも生物膜に対して
処理水(浴水槽水)が適度にぶつかるように流れるた
め、生物膜との接触の機会が増加し生物浄化効率が高く
なる。また、濾過器を例えば上下に直列に配置する場合
には、各々の濾過器の流路断面積を同一にせずに濾過器
内の濾材に合せて変えることで、物質移動係数が0.036
[m/h]以上かつ剪断応力が1.1×107[kg/m・h2]以下と
なるようにすることができ、効率良く生物浄化が行え
る。
As described above, according to the present invention, the mass transfer coefficient of bath water in a filter filled with a filter medium having a biofilm adhered on its surface is 0.036 [m / h] or more and the shear stress is increased. But
Since it was set to be 1.1 × 10 7 [kg / m · h 2 ] or less, the shear stress does not peel off the biofilm, and the treated water (bath water) flows to the biofilm appropriately. Therefore, the chance of contact with the biofilm increases, and the biopurification efficiency increases. In addition, for example, when filters are arranged vertically in series, the mass transfer coefficient is set to 0.036 by changing the cross-sectional area of each filter according to the filter medium in the filters without making them the same.
[M / h] or more and the shear stress can be 1.1 × 10 7 [kg / m · h 2 ] or less, so that biological purification can be performed efficiently.

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

【図1】本発明に係る浴水槽水の浄化方法を適用した循
環浄化システムの全体図
FIG. 1 is an overall view of a circulation purification system to which a bath water purification method according to the present invention is applied.

【図2】本発明に係る浄化の実施に用いる濾過装置の縦
断面図
FIG. 2 is a longitudinal sectional view of a filtration device used for performing purification according to the present invention.

【図3】物質移動係数と一次反応速度定数との関係を示
すグラフ
FIG. 3 is a graph showing a relationship between a mass transfer coefficient and a first-order reaction rate constant.

【図4】剪断応力と一次反応速度定数との関係を示すグ
ラフ
FIG. 4 is a graph showing a relationship between a shear stress and a first-order reaction rate constant.

【符号の説明】[Explanation of symbols]

1…浴槽、2…主循環経路、3…副循環経路、4…循環
ポンプ、10…濾過装置、11…装置本体、14…浴水
槽水の流入口、15…浴槽水の流出口、16…逆洗用流
入口、21,22…濾過器、23、24…濾材
DESCRIPTION OF SYMBOLS 1 ... Bath tub, 2 ... Main circulation path, 3 ... Sub circulation path, 4 ... Circulation pump, 10 ... Filtration device, 11 ... Device main body, 14 ... Bath water inlet, 15 ... Bath water outlet, 16 ... Backwash inlet, 22, 22, ... filter, 23, 24 ... filter media

───────────────────────────────────────────────────── フロントページの続き (72)発明者 幡手 伸太郎 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 小川 恵美香 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 木村 太門 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 今坂 卓男 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 寺岡 高生 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 (56)参考文献 特開 平6−335607(JP,A) 特開 平3−148563(JP,A) 特開 平6−218386(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 35/02 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Shintaro Hatate 2-1, 1-1 Nakajima, Kokurakita-ku, Kitakyushu-shi, Fukuoka Tochiki Kiki Co., Ltd. 2-1-1 Nakajima Totoki Kiki Co., Ltd. (72) Inventor Taimon Kimura 2-1-1 1-1 Nakajima, Kokurakita-ku, Kitakyushu-shi, Fukuoka Prefecture Touchi Kiki Co., Ltd. (72) Inventor Takuo Imasaka Fukuoka (1-1) Nakatomi, Inc. 2-1-1 Nakajima, Kokurakita-ku, Kitakyushu City (72) Inventor Takao Teraoka 2-1-1, Nakashima, Kokurakita-ku, Kitakyushu-shi, Fukuoka Prefecture (56) References JP-A-6-335607 (JP, A) JP-A-3-148563 (JP, A) JP-A-6-218386 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01D 35/02

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 表面に生物膜が付着した濾材を充填した
濾過器に浴水槽水を供給して浄化する方法において、前
記濾過器内における浴水槽水の物質移動係数が0.036[m
/h]以上かつ剪断応力が1.1×107[kg/m・h2]以下とな
るように浴水槽水の流量、濾材の空間率若しくは空塔速
度を調整するようにしたことを特徴とする浴水槽水の浄
化方法。
1. A method for purifying by supplying bath water to a filter filled with a filter medium having a biofilm adhered on the surface thereof, wherein a mass transfer coefficient of the bath water in the filter is 0.036 [m
/ h] and the flow rate of the bath water, the porosity of the filter medium or the superficial velocity are adjusted so that the shear stress is 1.1 × 10 7 [kg / m · h 2 ] or less. Bathtub water purification method.
【請求項2】 表面に生物膜が付着した濾材を充填した
濾過器を複数個直列に配置し、これら濾過器に浴水槽水
を供給して浄化する方法において、前記各濾過器には異
なる濾材が充填され、各濾過器における浴水槽水の物質
移動係数が0.036[m/h]以上かつ剪断応力が1.1×10
7[kg/m・h2]以下となるように濾過器の流路断面積を設
定するようにしたことを特徴とする浴水槽水の浄化装
置。
2. A method in which a plurality of filters filled with a filter material having a biofilm adhered to its surface are arranged in series, and the filter is supplied with bath water to purify the filter. And the mass transfer coefficient of bath water in each filter is 0.036 [m / h] or more and the shear stress is 1.1 × 10
A bath water purifier characterized in that the cross-sectional area of the flow passage of the filter is set so as to be 7 [kg / m · h 2 ] or less.
JP23948993A 1993-09-27 1993-09-27 Bath water purification method and purification device Expired - Fee Related JP3237337B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP23948993A JP3237337B2 (en) 1993-09-27 1993-09-27 Bath water purification method and purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP23948993A JP3237337B2 (en) 1993-09-27 1993-09-27 Bath water purification method and purification device

Publications (2)

Publication Number Publication Date
JPH0796114A JPH0796114A (en) 1995-04-11
JP3237337B2 true JP3237337B2 (en) 2001-12-10

Family

ID=17045541

Family Applications (1)

Application Number Title Priority Date Filing Date
JP23948993A Expired - Fee Related JP3237337B2 (en) 1993-09-27 1993-09-27 Bath water purification method and purification device

Country Status (1)

Country Link
JP (1) JP3237337B2 (en)

Also Published As

Publication number Publication date
JPH0796114A (en) 1995-04-11

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