JP2003266085A - Operation method for manganese catalytic column - Google Patents

Operation method for manganese catalytic column

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Publication number
JP2003266085A
JP2003266085A JP2002069891A JP2002069891A JP2003266085A JP 2003266085 A JP2003266085 A JP 2003266085A JP 2002069891 A JP2002069891 A JP 2002069891A JP 2002069891 A JP2002069891 A JP 2002069891A JP 2003266085 A JP2003266085 A JP 2003266085A
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JP
Japan
Prior art keywords
manganese
linear velocity
raw water
day
oxide catalyst
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.)
Granted
Application number
JP2002069891A
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Japanese (ja)
Other versions
JP3786888B2 (en
Inventor
Miho Shigefuji
美保 重藤
Hiroyuki Oyachi
裕行 大矢知
Nobuhiro Aoki
伸浩 青木
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NGK Insulators Ltd
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NGK Insulators Ltd
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Priority to JP2002069891A priority Critical patent/JP3786888B2/en
Publication of JP2003266085A publication Critical patent/JP2003266085A/en
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Publication of JP3786888B2 publication Critical patent/JP3786888B2/en
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  • Removal Of Specific Substances (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Catalysts (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide an operation method for a manganese catalytic column capable of simply restoring treatment efficiency even if iron and manganese oxides adhere to a packed bed. <P>SOLUTION: At the time of usual operation, raw water is passed through the manganese catalytic column 1 as an ascending flow at a high linear velocity of 1,000 m/day or more while adding chlorine to the raw water to oxidize and precipitate soluble manganese in the raw water before filtering the raw water by a separation membrane 3. When the treatment capacity of the manganese catalytic column 1 lowers, the raw water is passed as the ascending flow at a linear velocity higher than the linear velocity at the time of usual operation but lower than 3,500 m/day to wash off the adherend on a manganese oxide catalyst. The manganese oxide catalyst comprises particles with a specific gravity of 3 or more, and high linear velocity ascending flow washing can be performed without generating the outflow of the catalyst. Washing is preferably performed so as to be divided into one or more times. <P>COPYRIGHT: (C)2003,JPO

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、浄水処理場などで
用いられるマンガン接触塔の運転方法に関するものであ
る。
TECHNICAL FIELD The present invention relates to a method for operating a manganese contact tower used in a water purification plant or the like.

【0002】[0002]

【従来の技術】上水源として用いられている河川水や地
下水中には、溶解性のマンガンや鉄が含まれている場合
があり、浄水中におけるこれらの含有量が多いと黒水や
赤水の原因となる。このような原水の浄水処理方法とし
ては、マンガン接触塔を用いた接触マンガン砂ろ過法が
知られている。
2. Description of the Related Art River water and groundwater used as a water source may contain soluble manganese and iron. Cause. A contact manganese sand filtration method using a manganese contact tower is known as such a method for treating raw water for purification.

【0003】この接触マンガン砂ろ過法は、溶解性マン
ガンを含む原水に連続的に塩素を添加しながら、二酸化
マンガンが被覆されたろ過砂(マンガン砂)の充填層に
下向流として通水する方法である。溶解性のマンガンは
二酸化マンガンを触媒として塩素により速やかに酸化さ
れ、二酸化マンガンとなって既存のマンガン砂の表面に
結合する。このようにして、原水がマンガン砂の充填層
中を下向流で通過する間に溶解性マンガンが酸化析出し
て捕捉されると同時に、原水中の濁質もマンガン砂の充
填層によりろ過され除去されることとなる。
In this contact manganese sand filtration method, chlorine is continuously added to raw water containing soluble manganese while water is passed as a downflow to a packed bed of manganese dioxide-coated filter sand (manganese sand). Is the way. Soluble manganese is rapidly oxidized by chlorine using manganese dioxide as a catalyst to become manganese dioxide and is bonded to the surface of the existing manganese sand. In this way, while the raw water is flowing downward in the packed bed of manganese sand, the soluble manganese is oxidatively precipitated and captured, and at the same time, the suspended matter in the raw water is also filtered by the packed bed of manganese sand. Will be removed.

【0004】ところがこの接触マンガン砂ろ過法は、原
水中のマンガンを酸化析出させたうえで濁質とともにマ
ンガン砂の充填層で除去する方法であるから、マンガン
及び濁質の除去率を確保するためには、充填層を通過す
る原水の線速を150m/日程度の低速としなければな
らない。このため処理水量が多い場合には、非常に大型
の槽を必要とするという問題があった。また、降雨時の
ように原水の濁度が上昇したときには充填層が目詰まり
しやすいため、頻繁に逆洗を行わねばならず、運転管理
に多くの手数を要するという問題があった。
However, since the contact manganese sand filtration method is a method of oxidizing and precipitating manganese in raw water and removing it together with suspended matter in a packed bed of manganese sand, in order to secure the removal rate of manganese and suspended matter. In order to achieve this, the linear velocity of the raw water passing through the packed bed must be as low as 150 m / day. Therefore, when the amount of treated water is large, there is a problem that a very large tank is required. Further, when the turbidity of the raw water increases, such as during rainfall, the packed bed is likely to be clogged, and therefore backwashing must be frequently performed, which requires a lot of trouble in operation management.

【0005】そこで本発明者等は、マンガンを含有する
原水に塩素を添加しながら、酸化マンガン触媒が充填さ
れたマンガン接触塔に1000m/日以上の高線速の上
向流として通水して原水中の溶解性マンガンを酸化析出
させ、このマンガン接触塔の通過水を膜ろ過することに
より、酸化析出物を除去する方法を開発した。この方法
では酸化マンガン触媒の充填層は膨張層となるために原
水中の濁質による閉塞がなく、また設備を小型化するこ
とができるうえ、運転管理が容易な利点がある。
Therefore, the present inventors have added chlorine to raw water containing manganese while passing it through a manganese contact tower filled with a manganese oxide catalyst as an upward flow of a high linear velocity of 1000 m / day or more. We developed a method to remove oxidative precipitates by oxidative precipitation of soluble manganese in raw water and membrane filtration of the water passing through the manganese contact tower. In this method, since the packed bed of the manganese oxide catalyst serves as an expanded bed, there is no clogging due to suspended matter in the raw water, the facility can be downsized, and the operation management is easy.

【0006】しかし、トリハロメタン発生を抑制するた
めに低塩素濃度で運転したような場合など、運転方法に
よっては酸化マンガン触媒の充填層に鉄、マンガン酸化
物の付着が起こり、処理効率が次第に低下する場合があ
った。そこでこのような場合には、マンガン接触塔から
酸化マンガン触媒を取り出して交換するか、洗浄・分級
する作業が必要であり、運転管理が容易であるという高
線速上向流方式のマンガン処理法の利点が損なわれるこ
とがあった。
However, depending on the operating method, such as when operating at a low chlorine concentration in order to suppress trihalomethane generation, iron and manganese oxide adhere to the packed bed of the manganese oxide catalyst, and the treatment efficiency gradually decreases. There were cases. Therefore, in such a case, it is necessary to take out the manganese oxide catalyst from the manganese contact tower and replace it, or to wash and classify the catalyst, and the operation management is easy. The advantage of was sometimes impaired.

【0007】[0007]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、マンガンを含有する原水を小型の設
備で原水中の濁質による閉塞を招くことなく浄水処理す
ることができ、しかも酸化マンガン触媒の充填層に鉄、
マンガン酸化物の付着が起こった場合にも、簡便に処理
効率を回復させることができるマンガン接触塔の運転方
法を提供するためになされたものである。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems and allows raw water containing manganese to be purified by a small-sized facility without causing clogging due to turbidity in the raw water. Moreover, iron is contained in the packed bed of the manganese oxide catalyst,
The purpose of the present invention is to provide a method for operating a manganese contact tower that can easily recover the treatment efficiency even if the manganese oxide adheres.

【0008】[0008]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明のマンガン接触塔の運転方法は、原
水に塩素を添加しながら、酸化マンガン触媒が充填され
たマンガン接触塔に1000m/日以上の高線速の上向
流として通水して原水中の溶解性マンガンを酸化析出さ
せるとともに、マンガン接触塔の処理能力が低下した際
には、平常運転時の線速を越え3500m/日までの更
に高線速の上向流として原水を通水し、酸化マンガン触
媒への付着物を洗浄することを特徴とするものである。
なお、酸化マンガン触媒として、比重が3以上の粒子を
用いることによって触媒を流出させることなく、高線速
の上向流洗浄を可能にすることが好ましく、マンガン接
触塔の処理能力が低下した際の洗浄を、複数回に分割し
て行うことが好ましい。
The method of operating a manganese contact tower according to the present invention, which has been made to solve the above-mentioned problems, is a method for operating a manganese contact tower filled with a manganese oxide catalyst at 1000 m while adding chlorine to raw water. When water is passed as an upward flow at a high linear velocity of at least 1 / day to oxidize and precipitate soluble manganese in the raw water, and the processing capacity of the manganese contact tower decreases, the linear velocity during normal operation exceeds 3500 m. This is characterized in that raw water is passed as an upward flow of a higher linear velocity up to / day to wash the deposits on the manganese oxide catalyst.
It should be noted that it is preferable to use particles having a specific gravity of 3 or more as the manganese oxide catalyst to enable upward linear flow washing at a high linear velocity without causing the catalyst to flow out. It is preferable to carry out the washing in step 2 dividedly.

【0009】本発明によれば、平常運転時にはマンガン
を含有する原水をマンガン接触塔に1000m/日以上
の高線速の上向流として通水するので、小型の設備で原
水中の濁質による閉塞を招くことなく浄水処理が可能で
ある。また処理能力が低下した際には、平常運転時の線
速を越え3500m/日までの更に高線速の上向流とし
て原水を通水し、酸化マンガン触媒への付着物を洗浄す
るようにしたので、酸化マンガン触媒を取り出して交換
したり、取り出した酸化マンガン触媒を洗浄・分級する
必要はなくなり、簡便に処理効率を回復させることがで
きる。
According to the present invention, during normal operation, raw water containing manganese is passed through the manganese contact tower as an upward flow of a high linear velocity of 1000 m / day or more. Water purification treatment is possible without causing blockage. In addition, when the processing capacity decreases, raw water is passed as an upward flow of a linear velocity exceeding 3500 m / day, which exceeds the linear velocity during normal operation, to wash the deposits on the manganese oxide catalyst. Therefore, it is not necessary to take out the manganese oxide catalyst and replace it, or to wash and classify the taken out manganese oxide catalyst, and the treatment efficiency can be easily recovered.

【0010】[0010]

【発明の実施の形態】以下に本発明の好ましい実施の形
態を示す。図1において、1は内部に充填層2を備えた
マンガン接触塔であり、この充填層2には酸化マンガン
触媒の粒子が充填されている。酸化マンガン触媒は比重
が3以上のものを用いることが好ましく、例えば比重が
3.48であるベータ型の結晶構造を持つ酸化マンガン
触媒を用いることが好ましい。なお従来の接触マンガン
砂ろ過法で用いられていたマンガン砂の比重は2.36
である。ベータ型の結晶構造を持つ酸化マンガン触媒は
10〜30m2/gの広い表面積を持つので、この点でも
好ましいものである。
BEST MODE FOR CARRYING OUT THE INVENTION Preferred embodiments of the present invention will be described below. In FIG. 1, reference numeral 1 denotes a manganese contact column having a packed bed 2 therein, and the packed bed 2 is packed with particles of a manganese oxide catalyst. It is preferable to use a manganese oxide catalyst having a specific gravity of 3 or more. For example, it is preferable to use a manganese oxide catalyst having a beta-type crystal structure having a specific gravity of 3.48. The specific gravity of manganese sand used in the conventional contact manganese sand filtration method is 2.36.
Is. A manganese oxide catalyst having a beta type crystal structure has a large surface area of 10 to 30 m 2 / g, and is also preferable in this respect.

【0011】マンガンを含む原水は必要量の塩素を連続
的に添加されながら、接触槽1の下部から1000m/
日以上の高線速の上向流として通水される。原水中の溶
解性マンガンは、酸化マンガンを触媒として塩素により
速やかに酸化され、二酸化マンガンの酸化不溶化物とし
て酸化析出する。実用的に好ましい線速は1000〜2
500m/日であり、充填層2中の触媒粒子は流動状態
となり膨張床を形成する。線速が1000m/日未満で
あると、触媒粒子の流動が不十分となって降雨時のよう
に原水の濁度が上昇したときに閉塞のおそれが生じ、逆
に2500m/日を越えると原水と触媒粒子との接触時
間が短くなるので、充填層2をかなり高くしなければな
らない。
Raw water containing manganese is continuously added with a necessary amount of chlorine, and 1000 m / m from the bottom of the contact tank 1 is supplied.
Water is passed as an upward flow of high linear speed for more than a day. Soluble manganese in raw water is rapidly oxidized by chlorine using manganese oxide as a catalyst, and is oxidized and precipitated as an insoluble oxidization product of manganese dioxide. Practically preferable linear velocity is 1000-2
It is 500 m / day, and the catalyst particles in the packed bed 2 are in a fluidized state to form an expanded bed. If the linear velocity is less than 1000 m / day, the flow of the catalyst particles becomes insufficient and the turbidity of the raw water increases, such as during rain, which may cause blockage. Conversely, if the linear velocity exceeds 2500 m / day, the raw water Since the contact time with the catalyst particles becomes short, the packed bed 2 must be made quite high.

【0012】このようにして溶解性マンガンを二酸化マ
ンガンに酸化不溶化した充填層通過水は、次に分離膜3
に導かれる。分離膜3の種類は特に限定されるものでは
ないが、逆洗操作が容易で処理水量が大きく、また高濁
に強いため、このような高い線速で濁質を接触槽で捕捉
させることなく直接膜分離させることが可能であるセラ
ミック膜を用いることが好ましい。この実施形態では孔
径が0.1μmのセラミック製MF膜が用いられてい
る。充填層通過水をこの分離膜3により膜ろ過すれば、
触媒粒子の充填層2において酸化不溶化された不溶性マ
ンガンを確実に除去することができる。またこれと同時
に、原水中に含まれていた濁質も分離膜3によりろ過さ
れ、清澄な処理水を得ることができる。この処理水は上
水として利用することができる。
The water passed through the packed bed obtained by oxidizing the soluble manganese into manganese dioxide in this way is then separated into the separation membrane 3.
Be led to. The type of the separation membrane 3 is not particularly limited, but since the backwashing operation is easy, the amount of treated water is large, and it is resistant to high turbidity, the turbidity is not captured in the contact tank at such a high linear velocity. It is preferable to use a ceramic membrane that allows direct membrane separation. In this embodiment, a ceramic MF membrane having a pore size of 0.1 μm is used. If the water passing through the packed bed is subjected to membrane filtration with this separation membrane 3,
Insoluble manganese that has been oxidatively insolubilized in the packed bed 2 of catalyst particles can be reliably removed. At the same time, the suspended matter contained in the raw water is also filtered by the separation membrane 3 to obtain clear treated water. This treated water can be used as clean water.

【0013】上記のようにして平常運転を継続するが、
運転方法によっては酸化マンガン触媒の充填層2に鉄、
マンガン酸化物の付着が起こり、処理効率が次第に低下
する場合がある。本発明ではこのような場合、平常運転
時の線速を越え3500m/日までの更に高線速の上向
流として原水を充填層2に通水する。すなわち、平常運
転時の線速が1000m/日である場合には1000m
/日を越え3500m/日まで、平常運転時の線速が1
500m/日である場合には1500m/日を越え35
00m/日までの高線速とする。
Normal operation is continued as described above,
Depending on the operating method, iron is used in the packed bed 2 of the manganese oxide catalyst,
Adhesion of manganese oxide may occur, and the treatment efficiency may gradually decrease. In the present invention, in such a case, the raw water is passed through the packed bed 2 as an upward flow of a linear velocity exceeding 3500 m / day, which exceeds the linear velocity during normal operation. That is, if the linear velocity during normal operation is 1000 m / day, 1000 m
/ Line up to 3500m / day, the linear speed during normal operation is 1
If it is 500m / day, it will exceed 1500m / day and 35
High linear velocity up to 00m / day.

【0014】このような高線速の上向流として充填層2
に通水することは、充填物の流失を招くおそれがあるた
めに、通常は行なわれない。しかし本発明で用いている
酸化マンガン触媒の比重は3以上と大きいため、350
0m/日までの非常に高線速の上向流として原水を充填
層2に通水しても、酸化マンガン触媒が流出することは
ない。この通水により酸化マンガン触媒は激しく攪拌さ
れ、触媒粒子が相互に接触することによって、表面の付
着物を分離・洗浄することができる。このため本発明に
よれば従来のように触媒を塔外に取り出さなくても、酸
化マンガン触媒の充填層2の処理能力を短時間で簡便に
洗浄することができる。また後記する実施例に示すよう
に、洗浄を一度に行なうのではなく、短い休止時間を置
いて複数回に分割して行うことにより、洗浄効果を高め
ることができる。
As the upward flow of such a high linear velocity, the packed bed 2
Passing water through is normally not done because it can lead to washout of the packing. However, since the specific gravity of the manganese oxide catalyst used in the present invention is as large as 3 or more, 350
Even if raw water is passed through the packed bed 2 as an upward flow of a very high linear velocity up to 0 m / day, the manganese oxide catalyst does not flow out. By this water passing, the manganese oxide catalyst is vigorously stirred, and the catalyst particles come into contact with each other, whereby the deposits on the surface can be separated and washed. Therefore, according to the present invention, the treatment capacity of the packed bed 2 of the manganese oxide catalyst can be easily washed in a short time without taking the catalyst out of the column as in the conventional case. Further, as shown in Examples described later, the cleaning effect can be enhanced by performing the cleaning not at once but in a plurality of times with a short rest time.

【0015】なお、本発明においては洗浄のための特別
は設備は不要であり、原水ポンプ4の容量を大きくして
おくだけでよい。洗浄時の排水は捨水してもよいが、そ
のまま分離膜3によりろ過処理して回収することもでき
る。
In the present invention, no special equipment for cleaning is required, and it is only necessary to increase the capacity of the raw water pump 4. The drainage water at the time of washing may be discarded, but it can also be directly recovered by filtration through the separation membrane 3.

【0016】[0016]

【実施例】(実施例1:洗浄時の線速)実施形態として
説明したマンガン接触塔に、塩素を添加した原水を15
00m/日の線速で通水する平常運転を1ヶ月間にわた
り行ない、触媒活性が運転開始時の70%にまで低下し
た段階で洗浄実験を行なった。表1に示すように洗浄速
度を様々に変化させ、洗浄後の触媒活性を測定した。表
1に示されるように、洗浄時の線速が平常運転時と同じ
であると触媒活性の回復は認められないが、それを越え
ると触媒活性の回復が大きくなり、2000〜3500
m/日とした場合に顕著な回復が認められた。しかし4
000m/日とすると触媒が流出し、運転不能となっ
た。なお、洗浄時間は非常に短時間でよい。
Example (Example 1: Linear velocity at the time of cleaning) The raw water containing chlorine was added to the manganese contact column described as an embodiment.
A normal operation of passing water at a linear velocity of 00 m / day was carried out for one month, and a cleaning experiment was conducted when the catalyst activity dropped to 70% of that at the start of the operation. As shown in Table 1, the washing rate was variously changed and the catalyst activity after washing was measured. As shown in Table 1, the recovery of the catalytic activity is not observed when the linear velocity at the time of washing is the same as that in the normal operation, but the recovery of the catalytic activity becomes large when the linear velocity at the time of washing exceeds 2000 to 3500.
A marked recovery was observed at m / day. But 4
At 000 m / day, the catalyst flowed out and it became impossible to operate. The cleaning time may be very short.

【0017】[0017]

【表1】 [Table 1]

【0018】(実施例2:触媒の流出)酸化マンガン触
媒(粒径0.5〜1mm、比重3.48、表面積15m2/
g)と、従来のマンガン砂(粒径0.6〜1.5mm、比重
2.36、表面積1m2/g)とをマンガン接触塔に充填
し、上向流の線速を様々に変化させて流出割合を測定し
た。その結果を図2に示す。従来のマンガン砂では粒径
の小さいものが流出してしまうために2000m/日を
越える線速で洗浄することはできないが、酸化マンガン
触媒を用いた場合には3500m/日までの線速では流
出しないことが確認された。
(Example 2: Outflow of catalyst) Manganese oxide catalyst (particle size 0.5 to 1 mm, specific gravity 3.48, surface area 15 m 2 /
g) and conventional manganese sand (particle size: 0.6 to 1.5 mm, specific gravity: 2.36, surface area: 1 m 2 / g) are packed in a manganese contact tower, and the linear velocity of the upward flow is variously changed. The outflow rate was measured. The result is shown in FIG. Conventional manganese sand cannot be washed at a linear velocity exceeding 2000 m / day because it will flow out with a small particle size, but when a manganese oxide catalyst is used, it will flow out at a linear velocity of up to 3500 m / day. It was confirmed not to do.

【0019】(実施例3:分割洗浄)平常運転線速を1
500m/日としたマンガン接触塔の洗浄を、図3aに
示すように2000m/日の線速で2回に分割して行な
った。1回の洗浄継続時間は3分であり、休止時間は1
分である。この洗浄中のマンガン接触塔からの流出水の
濁度は図3bに示す通りであり、触媒活性は図3cに示
す通りに回復した。このように分割洗浄を行なえば流出
水の濁度上昇は小さいので、膜ろ過が可能である。これ
に対して2500m/日の線速で3分間の洗浄を行なっ
ても触媒活性を90%以上にまで回復させることができ
たが、図4に示すように洗浄中の流出水の濁度上昇が著
しく、膜ろ過は困難となった。このように分割洗浄を行
なうことにより、洗浄水の膜ろ過が可能となる。
(Embodiment 3: Split cleaning) Normal operating linear velocity is 1
The washing of the manganese contact tower at 500 m / day was performed in two steps at a linear velocity of 2000 m / day as shown in FIG. 3a. One wash duration is 3 minutes, rest time is 1
Minutes. The turbidity of the effluent from the manganese contact tower during this wash was as shown in Figure 3b and the catalytic activity was restored as shown in Figure 3c. By performing the divided washing in this way, the turbidity of the outflow water does not increase so much, and membrane filtration is possible. On the other hand, the catalyst activity could be recovered to 90% or more even after washing for 3 minutes at a linear velocity of 2500 m / day, but as shown in Fig. 4, the turbidity of the effluent during washing increased. However, membrane filtration became difficult. By performing the divided washing in this way, it becomes possible to perform membrane filtration of the washing water.

【0020】[0020]

【発明の効果】以上に説明したように、本発明のマンガ
ン接触塔の運転方法によれば、平常運転時にはマンガン
を含有する原水を小型の設備で原水中の濁質による閉塞
を招くことなく浄水処理することができる。また運転継
続の結果、酸化マンガン触媒の充填層に鉄、マンガン酸
化物の付着が起こった場合にも、3500m/日までの
更に高線速の上向流として原水を通水することによっ
て、乱流流動による触媒どうしの接触効果と、高線速上
向流の洗浄効果とを生じさせ、付着物を剥離させること
ができる。またこのときに平常運転時には流出させるこ
とができなかったゴミ(濁質)も排出することができ
る。この結果、本発明によれば従来のように触媒を塔外
に取り出すことなく、簡便に処理効率を回復させること
ができる。
As described above, according to the operating method of the manganese contact tower of the present invention, during normal operation, the raw water containing manganese is purified by a small-sized facility without causing clogging due to suspended matter in the raw water. Can be processed. When iron and manganese oxide adhere to the packed bed of the manganese oxide catalyst as a result of continuous operation, turbulence is increased by passing raw water as an upward flow of a higher linear velocity up to 3500 m / day. The contact effect between the catalysts due to the flowing flow and the cleaning effect of the high linear velocity upward flow are generated, and the deposit can be separated. At this time, it is possible to discharge dust (suspended matter) that could not be discharged during normal operation. As a result, according to the present invention, the processing efficiency can be easily recovered without taking the catalyst out of the column as in the conventional case.

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

【図1】本発明の実施形態を示すブロック図である。FIG. 1 is a block diagram showing an embodiment of the present invention.

【図2】実施例2における線速と触媒の流出割合との関
係を示すグラフである。
FIG. 2 is a graph showing the relationship between the linear velocity and the outflow rate of catalyst in Example 2.

【図3】実施例3における分割洗浄のデータを示すグラ
フである。
FIG. 3 is a graph showing data of divided cleaning in Example 3.

【図4】実施例3における非分割洗浄のデータを示すグ
ラフである。
FIG. 4 is a graph showing data of non-division cleaning in Example 3.

【符号の説明】[Explanation of symbols]

1 マンガン接触塔、2 充填層、3 分離膜、4 原
水ポンプ
1 manganese contact tower, 2 packed bed, 3 separation membrane, 4 raw water pump

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01D 9/02 615 B01D 9/02 615A 615Z 621 621 625 625C 625D B01J 23/34 B01J 23/34 M C02F 1/76 C02F 1/76 Z (72)発明者 青木 伸浩 愛知県名古屋市瑞穂区須田町2番56号 日 本碍子株式会社内 Fターム(参考) 4D038 AA01 AB66 AB89 BA02 BA04 BA06 BB16 BB17 4D050 AA03 AB55 BB04 BC06 BD02 BD06 CA09 4G069 AA03 CA05 CA07 CA11 EA02Y─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) B01D 9/02 615 B01D 9/02 615A 615Z 621 621 625 625C 625D B01J 23/34 B01J 23/34 M C02F 1 / 76 C02F 1/76 Z (72) Inventor Nobuhiro Aoki No. 2-56, Suda-cho, Mizuho-ku, Nagoya, Aichi Prefecture Incorporated Insulator Nihonmoto F-term (reference) 4D038 AA01 AB66 AB89 BA02 BA04 BA06 BB16 BB17 4D050 AA03 AB55 BB04 BC06 BD02 BD06 CA09 4G069 AA03 CA05 CA07 CA11 EA02Y

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 原水に塩素を添加しながら、酸化マンガ
ン触媒が充填されたマンガン接触塔に1000m/日以
上の高線速の上向流として通水して原水中の溶解性マン
ガンを酸化析出させるとともに、マンガン接触塔の処理
能力が低下した際には、平常運転時の線速を越え350
0m/日までの更に高線速の上向流として原水を通水
し、酸化マンガン触媒への付着物を洗浄することを特徴
とするマンガン接触塔の運転方法。
1. While adding chlorine to raw water, water is passed through a manganese contact tower filled with a manganese oxide catalyst as an upward flow of high linear velocity of 1000 m / day or more to oxidize and precipitate soluble manganese in raw water. In addition, when the manganese contact tower's processing capacity declined, the linear velocity during normal operation was exceeded and 350
A method for operating a manganese contact tower, characterized in that raw water is passed as an upward flow of a higher linear velocity up to 0 m / day to wash deposits on the manganese oxide catalyst.
【請求項2】 酸化マンガン触媒として、比重が3以上
の粒子を用いることによって触媒を流出させることな
く、高線速の上向流洗浄を可能にした請求項1記載のマ
ンガン接触塔の運転方法。
2. The method for operating a manganese contact tower according to claim 1, wherein particles having a specific gravity of 3 or more are used as the manganese oxide catalyst to enable upward linear flow washing at a high linear velocity without causing the catalyst to flow out. .
【請求項3】 マンガン接触塔の処理能力が低下した際
の洗浄を、複数回に分割して行う請求項1記載のマンガ
ン接触塔の運転方法。
3. The method for operating a manganese contact tower according to claim 1, wherein the washing when the treatment capacity of the manganese contact tower is lowered is divided into a plurality of times.
JP2002069891A 2002-03-14 2002-03-14 Operation method of manganese contact tower Expired - Lifetime JP3786888B2 (en)

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JP2010214311A (en) * 2009-03-17 2010-09-30 Suido Kiko Kaisha Ltd Apparatus and method for manganese catalytic oxidation
US7922904B2 (en) 2006-11-14 2011-04-12 Metawater Co., Ltd. Upward-flow manganese contact column
JP2013056303A (en) * 2011-09-08 2013-03-28 Japan Organo Co Ltd Apparatus for oxidizing manganese
JP2014233657A (en) * 2013-05-31 2014-12-15 オルガノ株式会社 Treatment device and treatment method for iron/manganese-containing water
JP2015003316A (en) * 2013-05-21 2015-01-08 オルガノ株式会社 Processing apparatus and processing method of iron/manganese-containing water
JP2015147155A (en) * 2014-02-04 2015-08-20 オルガノ株式会社 Apparatus and method for treating water containing iron/manganese
JP2019098296A (en) * 2017-12-07 2019-06-24 オルガノ株式会社 Apparatus and method for treating iron/manganese containing water
CN110980916A (en) * 2019-11-14 2020-04-10 东北大学 Method for degrading thiocyanate in cyanogen-containing barren solution under acidic condition

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7922904B2 (en) 2006-11-14 2011-04-12 Metawater Co., Ltd. Upward-flow manganese contact column
JP2010214311A (en) * 2009-03-17 2010-09-30 Suido Kiko Kaisha Ltd Apparatus and method for manganese catalytic oxidation
JP2013056303A (en) * 2011-09-08 2013-03-28 Japan Organo Co Ltd Apparatus for oxidizing manganese
JP2015003316A (en) * 2013-05-21 2015-01-08 オルガノ株式会社 Processing apparatus and processing method of iron/manganese-containing water
JP2014233657A (en) * 2013-05-31 2014-12-15 オルガノ株式会社 Treatment device and treatment method for iron/manganese-containing water
JP2015147155A (en) * 2014-02-04 2015-08-20 オルガノ株式会社 Apparatus and method for treating water containing iron/manganese
JP2019098296A (en) * 2017-12-07 2019-06-24 オルガノ株式会社 Apparatus and method for treating iron/manganese containing water
JP7117099B2 (en) 2017-12-07 2022-08-12 オルガノ株式会社 Apparatus and method for treating iron/manganese-containing water
CN110980916A (en) * 2019-11-14 2020-04-10 东北大学 Method for degrading thiocyanate in cyanogen-containing barren solution under acidic condition

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