JPS644468Y2 - - Google Patents

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Publication number
JPS644468Y2
JPS644468Y2 JP18617284U JP18617284U JPS644468Y2 JP S644468 Y2 JPS644468 Y2 JP S644468Y2 JP 18617284 U JP18617284 U JP 18617284U JP 18617284 U JP18617284 U JP 18617284U JP S644468 Y2 JPS644468 Y2 JP S644468Y2
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Japan
Prior art keywords
water
pipe
treated
tank
treated water
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Expired
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JP18617284U
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Japanese (ja)
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JPS61102290U (en
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Description

【考案の詳細な説明】 〔産業上の利用分野〕 本考案は、リン吸着能を有する固体粒子を接触
させることによつて、水中のリンを除去する接触
脱リン装置に関するものである。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a catalytic dephosphorization device that removes phosphorus from water by bringing solid particles having phosphorus adsorption ability into contact with the device.

〔従来技術〕[Prior art]

リン吸着能を有する固体粒子(以下「脱リン
材」という)を充填した層に、アルカリ剤及び、
又はカルシウム剤を注入した被処理水を通水しな
がら水中のリンを除去する接触脱リン装置は公知
である。
An alkaline agent and
Alternatively, a catalytic dephosphorization device is known that removes phosphorus from water while passing water to be treated into which a calcium agent has been injected.

また、被処理水中に存在する炭酸物質や、薬品
添加の過程で生成する炭酸カルシウムは、脱リン
材を汚染するため、始めに被処理水の脱炭酸を行
う工程と、次にアルカリ剤及びカルシウム剤を注
入する工程と、薬品中に含まれる炭酸カルシウム
や、薬品添加によつて生成する炭酸カルシウム及
び被処理水中に含まれる有機物を除去する砂ろ過
工程と、リンを除去する脱リン工程からなる装置
も提案されており、このような装置を用いれば脱
リン材の汚染はなく、長時間安定した水質の処理
水が得られるのである。
In addition, carbonic substances present in the water to be treated and calcium carbonate generated during the process of adding chemicals contaminate the dephosphorization material, so it is necessary to first decarbonate the water to be treated and then add alkaline agents and calcium carbonate. The process consists of a step of injecting the chemical, a sand filtration step to remove calcium carbonate contained in the chemicals, calcium carbonate generated by adding the chemicals, and organic matter contained in the water to be treated, and a dephosphorization step to remove phosphorus. A device has also been proposed, and if such a device is used, there will be no contamination of the dephosphorizing material, and treated water with stable quality for a long period of time can be obtained.

〔考案が解決しようとする問題点〕[Problem that the invention attempts to solve]

しかしながら、前記従来の各工程からなる装置
では、工程が複雑であり、脱炭酸に要する酸の使
用量が甚大であつた。また、脱炭酸や砂ろ過工程
を省略した装置を用いると、脱リン材の汚染とと
もに処理水の水質が悪化し、脱リン材を全量交換
する必要があつた。
However, in the conventional apparatus consisting of each step, the steps are complicated and the amount of acid required for decarboxylation is enormous. Furthermore, when a device that does not include decarbonation or sand filtration steps is used, the dephosphorization material becomes contaminated and the quality of the treated water deteriorates, making it necessary to replace the entire amount of the dephosphorization material.

さらに、汚染した脱リン材を再生する方法とし
て、酸を注入する方法を採用すれば、再生廃液の
処理に問題があるばかりでなく、再生用の多量の
酸と長い再生時間を必要としていた。
Furthermore, if the method of injecting acid is adopted as a method for regenerating contaminated dephosphorization material, not only will there be problems in processing the regenerated waste liquid, but it will also require a large amount of regenerating acid and a long regeneration time.

本考案は、上記の問題点を解決し、少量の薬品
で脱リン材を効率的に再生し、かつ工程を簡略化
した接触脱リン装置を提供しようとするものであ
る。
The present invention aims to solve the above problems and provide a catalytic dephosphorization device that efficiently regenerates dephosphorization material with a small amount of chemicals and simplifies the process.

〔問題点を解決するための手段〕[Means for solving problems]

本考案は、被処理水流入管、処理水流出管、酸
及びアルカリ剤注入設備を具備した槽内に、リン
吸着能を有する固体粒子を充填するとともに、槽
内底部に処理水の散水装置及び散気装置を配備
し、さらに槽内底部と上部間に循環水管を連設し
たことを特徴とする接触脱リン装置である。
In this invention, a tank equipped with an inflow pipe for treated water, an outflow pipe for treated water, and acid and alkali agent injection equipment is filled with solid particles having phosphorus adsorption ability, and at the same time, a water sprinkling device and a sprinkling system for treated water are installed at the bottom of the tank. This is a catalytic dephosphorization device that is equipped with an air system and further has a circulating water pipe connected between the bottom and top of the tank.

〔実施例〕〔Example〕

本考案の実施例を図面を参照しながら説明する
と、第1図は下向流の接触脱リン装置の実施例で
あつて、1は槽体で、被処理水流入管2と処理水
流出管3、酸注入管4とアルカリ剤注入管5が具
備されており、この酸注入管4とアルカリ剤注入
管5とは兼用たらしめることもできる。槽体1内
には、砂利その他の支持床6上に脱リン材7の充
填層が形成され、また底部の支持床6内又はその
下方には、処理水流出管3に連なる集散水器8
と、コンプレツサ9に連なる散気器10とが配備
されている。
An embodiment of the present invention will be described with reference to the drawings. Fig. 1 shows an embodiment of a downward flow catalytic dephosphorization device, in which 1 is a tank body, a water inflow pipe 2 to be treated, and a water outflow pipe 3. , an acid injection tube 4 and an alkaline agent injection tube 5 are provided, and the acid injection tube 4 and alkali agent injection tube 5 can also be used for the same purpose. Inside the tank body 1, a packed layer of dephosphorization material 7 is formed on a supporting bed 6 such as gravel, and a water collector 8 connected to the treated water outflow pipe 3 is provided in or below the supporting bed 6 at the bottom.
and a diffuser 10 connected to the compressor 9 are provided.

集散水器8は、処理水の集水ならびに散水を併
せ行うようにするとよく、処理水流出管3が連な
る処理水槽11から返送ポンプ12を介して処理
水が返送される如くなつており、この集散水器8
は適宜の配管によつて散気器10と兼用にするこ
ともできる。
It is preferable that the water collector and sprinkler 8 collects and sprinkles the treated water, and the treated water is returned from the treated water tank 11 connected to the treated water outflow pipe 3 via the return pump 12. Water collector 8
can also be used as the diffuser 10 by using appropriate piping.

さらに、槽体1の底部と上部とは、循環ポンプ
13を介在させた循環水管14にて連結され、水
が槽体1内を循環するようになつている。
Furthermore, the bottom and top of the tank 1 are connected by a circulation water pipe 14 with a circulation pump 13 interposed therebetween, so that water circulates within the tank 1.

なお、図示例では、酸注入管4とアルカリ剤注
入管5を循環水管14中に開口させてあるが、こ
れらを槽体1に直接開口させることもできる。
In the illustrated example, the acid injection pipe 4 and the alkaline agent injection pipe 5 are opened into the circulating water pipe 14, but they can also be opened directly into the tank body 1.

また、循環水管14に流動型のPH計15を有す
るようにし、このPH計15を酸注入管4の注入ポ
ンプ16及びアルカリ剤注入管5の注入ポンプ1
7に連動させて自動運転を可能にするのも好まし
い態様の一つである。
In addition, the circulating water pipe 14 is provided with a flow type PH meter 15, and this PH meter 15 is connected to the injection pump 16 of the acid injection pipe 4 and the injection pump 1 of the alkaline agent injection pipe 5.
7 to enable automatic driving.

図中、18は槽体1上部に接続された逆洗排水
管、19は槽体1下部に接続された捨水管を示
す。
In the figure, 18 indicates a backwash drain pipe connected to the upper part of the tank body 1, and 19 indicates a waste water pipe connected to the lower part of the tank body 1.

しかして、被処理水は、必要に応じてカルシウ
ム剤及び、又はアルカリ剤が添加されたのち、被
処理水流入管2から槽体1内に導かれ、下向きに
脱リン材7の充填層を流過し、脱リンされた処理
水となつて集散水器8を経て処理水流出管3から
処理水槽11へ流入する。
Thus, the water to be treated is introduced into the tank body 1 from the water inflow pipe 2 after adding a calcium agent and/or an alkaline agent as necessary, and flows downward through a packed bed of dephosphorization material 7. The dephosphorized treated water flows through the water collector 8 and from the treated water outlet pipe 3 into the treated water tank 11 .

所定期間(例えば1〜3日)前記通水を行い、
脱リン材7の充填層が目詰り生じ、ろ過抵抗が上
昇したときには、被処理水の流入を停止し、返送
ポンプ12を起動して処理水槽11より処理水を
集散水器8から槽体1内下部へ散水し、上向きに
流通させて脱リン材7を洗浄し、洗浄排水は逆洗
排水管18から外部へ排出される。この脱リン材
7の洗浄を強力に行わしめるためには、コンプレ
ツサより散気器10を経て槽体内に通気し、いわ
ゆる空気併用洗浄を行うこともできる。
Perform the water flow for a predetermined period (for example, 1 to 3 days),
When the packed bed of the dephosphorization material 7 becomes clogged and the filtration resistance increases, the inflow of the water to be treated is stopped, the return pump 12 is activated, and the treated water is transferred from the treated water tank 11 to the water collector 8 and the tank body 1. Water is sprayed to the inner lower part and circulated upward to wash the dephosphorizing material 7, and the washing waste water is discharged to the outside from the backwash drain pipe 18. In order to strongly clean the dephosphorizing material 7, it is also possible to carry out so-called combined air cleaning by ventilating the inside of the tank from a compressor through an aeration diffuser 10.

以上のような脱リン材7の洗浄を間欠的に行い
ながら処理を継続するわけであるが、長期間(例
えば5〜6ケ月程度)のうちに次第に脱リン材7
が炭酸カルシウムや有機物により汚染され、処理
水の水質も悪化してくる。そこで、被処理水の流
入を停止したのち、捨水管19を開いて槽体1内
の水を引き抜く。この水の引き抜きは、後述の曝
気を行つたときに、脱リン材7が水に浸る程度に
水を残すものとし、捨水管19の開口高さを適宜
定めることによつてもよい。
The process continues while cleaning the dephosphorizing material 7 intermittently as described above, but over a long period of time (for example, about 5 to 6 months), the dephosphorizing material 7 is gradually removed.
The water becomes contaminated with calcium carbonate and organic matter, and the quality of the treated water also deteriorates. Therefore, after stopping the inflow of the water to be treated, the drain pipe 19 is opened and the water in the tank body 1 is drawn out. This water may be drawn out by leaving enough water so that the dephosphorizing material 7 is immersed in the water when aeration, which will be described later, is carried out, and by appropriately determining the opening height of the drain pipe 19.

槽体1内の水を引き抜いたのちは、循環ポンプ
13によつて循環水管14を介して槽体1内の水
を循環し、同時に酸注入管4から酸を注入して槽
体1内の水のPHを効率よく低下させ、その後コン
プレツサ9を起動し、散気器10から空気を吹き
込み脱リン材7を撹拌する。この操作により脱リ
ン材7上の炭酸カルシウムや有機物が効果的に除
去される。次いで、酸の注入及びコンプレツサ9
を停止し、アルカリ剤注入管5からアルカリを注
入し、循環水管14による槽体1内水の循環を行
いながら槽体1内の水のPHを7〜8に上昇させ
る。
After the water is removed from the tank 1, the water in the tank 1 is circulated through the circulating water pipe 14 by the circulating pump 13, and at the same time, acid is injected from the acid injection pipe 4 to efficiently lower the pH of the water in the tank 1. After that, the compressor 9 is started and air is blown in from the aeration device 10 to agitate the dephosphorization material 7. This operation effectively removes calcium carbonate and organic matter on the dephosphorization material 7. Next, the injection of acid and the compressor 9 are started.
The process is stopped, alkali is injected through the alkaline agent injection pipe 5, and the pH of the water in the tank 1 is increased to 7-8 while circulating the water in the tank 1 through the circulating water pipe 14.

かくてアルカリ剤の注入及びコンプレツサ9を
停止したのち一定期間放置し、再び被処理水を通
水して脱リン処理を再開する。
After the injection of the alkaline agent and the compressor 9 are stopped, the system is left for a certain period of time, and the water to be treated is passed through again to restart the dephosphorization process.

また、循環水管14中に流通型のPH計15を有
し、このPH計15を酸及びアルカリ剤の注入ポン
プ16,17に連動させておけば、循環水管14
中を流過する水のPH値に応じて各注入ポンプ1
6,17の運動を自動化することができる。
In addition, if a flow-type PH meter 15 is provided in the circulating water pipe 14 and this PH meter 15 is linked to the acid and alkali agent injection pumps 16 and 17, the circulating water pipe 14
Each injection pump 1 according to the PH value of the water flowing through it.
6,17 movements can be automated.

第2図示例は、上向流式の実施例を示し、被処
理水流入管2は槽体1の下部に、処理水流出管3
が槽体1の上部に具備されたもので、その他は第
1図示例とほとんど同一である。したがつて、ア
ルカリ剤及び、又はカルシウム剤を添加された被
処理水は槽体1の下部に通水され、脱リン材7の
充填層を上向きに流過する以外は前記第1図示例
の作用と同様である。
The second illustrated example shows an upward flow type embodiment, in which the treated water inflow pipe 2 is located at the lower part of the tank body 1, and the treated water outflow pipe 3 is located at the bottom of the tank body 1.
is provided on the upper part of the tank body 1, and the rest is almost the same as the first illustrated example. Therefore, the water to be treated to which the alkaline agent and/or calcium agent has been added is passed through the lower part of the tank body 1 and flows upward through the packed bed of the dephosphorizing material 7, except that it is similar to the first illustrated example. The effect is similar.

なお、第2図示例においては、通水による脱リ
ン処理中に返送ポンプ12により集散水器8から
処理水の一部を被処理水に循環混合することによ
つて、被処理液中のリン濃度を低下させ、脱リン
効率を高めることができる。この例の集散水器8
は、散水機能のみで集水機能をもたないものでよ
い。また、酸とアルカリ剤の注入をPH計15と連
動させることができることも、第1図示例と同様
である。
In the second illustrated example, phosphorus in the liquid to be treated is removed by circulating and mixing a part of the treated water from the water collector 8 with the water to be treated using the return pump 12 during the dephosphorization process by water flow. The concentration can be lowered and the dephosphorization efficiency can be increased. Water collector 8 in this example
may have only a water sprinkling function and no water collection function. Also, as in the first illustrated example, the injection of acid and alkali agents can be linked with the PH meter 15.

第3図示例は流動床式の実施例を示し、被処理
水流入管2が槽体1の下部に、処理水流出管3が
槽体1の上部に具備されたもので、カルシウム剤
及び、又はアルカリ剤を添加した被処理水を槽体
1の下部に導入し、同時に処理水の一部を返送ポ
ンプ12により槽体1の下部に流入させて混合
し、脱リン効率を高めるものである。この混合を
良好にするために、槽体1内下部に円錐形の構造
物20を設けるとよい。
The third illustrated example shows an embodiment of a fluidized bed type, with a treated water inlet pipe 2 at the bottom of the tank body 1 and a treated water outlet pipe 3 at the top of the tank body 1. The treated water to which calcium and/or alkaline agents have been added is introduced into the bottom of the tank body 1, and at the same time, a part of the treated water is caused to flow into the bottom of the tank body 1 by a return pump 12 to mix with the water, thereby improving the efficiency of dephosphorization. To improve this mixing, it is advisable to provide a conical structure 20 at the bottom of the tank body 1.

したがつて、被処理水は槽体1内を上向きに流
れ、返送ポンプ12により処理水の一部が混合さ
れ、脱リン材7を流動化させながら脱リン処理が
行われるが、処理を継続していると、長期間のう
ちに次第に脱リン材7が炭酸カルシウムや有機物
によつて汚染されてくる。そこで被処理水の流入
及び返送ポンプ12を停止したのち、捨水管19
を開き、槽体1内の水を適当量引き抜く。次に循
環ポンプ13を起動し、循環水管14によつて槽
体1内の水を循環し、同時に酸注入管4から酸を
注入して水のPHを低下させ、その後コンプレツサ
9を起動し、散気器10より空気を吹き込む。
Therefore, the water to be treated flows upward in the tank body 1, and a part of the treated water is mixed by the return pump 12, and the dephosphorization treatment is performed while fluidizing the dephosphorization material 7, but the treatment continues. If this is done, the dephosphorization material 7 will gradually become contaminated with calcium carbonate and organic matter over a long period of time. After stopping the inflow and return pump 12 of the water to be treated, the wastewater pipe 19
, and draw out an appropriate amount of water from the tank body 1. Next, the circulation pump 13 is started, the water in the tank body 1 is circulated through the circulation water pipe 14, and at the same time, acid is injected from the acid injection pipe 4 to lower the pH of the water, and then the compressor 9 is started, Air is blown in from the diffuser 10.

その後は、アルカリ剤の注入を行うことになる
が、前記第1図及び第2図の実施例と同様であ
り、また酸とアルカリ剤の注入をPH計15と連動
させるたとができることも同様である。
After that, the alkaline agent is injected, which is the same as in the embodiments shown in FIGS. be.

なお、酸注入管4から注入される酸としては、
塩酸、硫酸、有機酸類などを用いることができ、
有機物汚染がひどい場合は、有機酸を用いるとよ
い。またアルカリ剤注入管5から注入されるアル
カリ剤としては、消石灰、水酸化マグネシウム、
苛性ソーダが用いられる。これら薬品の混合をさ
らに良好たらしめるためには、循環水管14の注
入点付近にラインミキサを設けることも好ましい
一例である。
Note that the acid injected from the acid injection tube 4 is as follows:
Hydrochloric acid, sulfuric acid, organic acids, etc. can be used,
If organic contamination is severe, it is recommended to use an organic acid. The alkaline agents injected from the alkaline agent injection pipe 5 include slaked lime, magnesium hydroxide,
Caustic soda is used. In order to improve the mixing of these chemicals, it is also a preferable example to provide a line mixer near the injection point of the circulating water pipe 14.

脱リン材7としては、リン鉱石、骨炭、鹿沼
土、転炉スラグ、軽焼マグネシアが使用できる。
As the dephosphorizing material 7, phosphate rock, bone charcoal, Kanuma soil, converter slag, and light burnt magnesia can be used.

また、槽体1の内壁、集散水器8、散気器10
等槽体1内で水と接触する部分は、耐酸性の材質
又は樹脂などを用いることも必要である。
In addition, the inner wall of the tank body 1, the water collector 8, the air diffuser 10
It is also necessary to use an acid-resistant material or resin for the parts of the tank body 1 that come into contact with water.

〔考案の効果〕[Effect of idea]

以上述べたように本考案によれば、脱炭酸、砂
ろ過等の前処理工程が不要となり、工程及び設備
が簡略化され、また脱リン材の再生を散気及び水
循環を利用して、短時間で効率的に行い得るた
め、酸等の薬品の使用量を低減することができる
という極めて有用なる効果を有するものである。
As described above, the present invention eliminates the need for pretreatment processes such as decarboxylation and sand filtration, simplifies the process and equipment, and enables the regeneration of dephosphorizing material to be carried out in a short period of time by using aeration and water circulation. Since it can be carried out efficiently and in a short amount of time, it has the extremely useful effect of reducing the amount of chemicals such as acids used.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図〜第3図はそれぞれ本考案の実施例を示
す縦断面図である。 1……槽体、2……被処理水流入管、3……処
理水流出管、4……酸注入管、5……アルカリ剤
注入管、6……支持床、7……脱リン材、8……
集散水器、9……コンプレツサ、10……散気
器、11……処理水槽、12……返送ポンプ、1
3……循環ポンプ、14……循環水管、15……
PH計、16,17……注入ポンプ、18……逆洗
排水管、19……捨水管、20……構造物。
1 to 3 are longitudinal sectional views showing embodiments of the present invention, respectively. 1... Tank body, 2... Treated water inflow pipe, 3... Treated water outflow pipe, 4... Acid injection pipe, 5... Alkaline agent injection pipe, 6... Support bed, 7... Dephosphorization material, 8...
Water collector, 9...Compressor, 10...Aeration diffuser, 11...Treatment water tank, 12...Return pump, 1
3...Circulation pump, 14...Circulation water pipe, 15...
PH meter, 16, 17... Injection pump, 18... Backwash drain pipe, 19... Waste water pipe, 20... Structure.

Claims (1)

【実用新案登録請求の範囲】 1 被処理水流入管、処理水流出管、酸及びアル
カリ剤注入設備を具備した槽内に、リン吸着能
を有する固体粒子を充填するとともに、槽内底
部に処理水の散水装置及び散気装置を配備し、
さらに槽内底部と上部間に循環水管を連設した
ことを特徴とする接触脱リン装置。 2 前記被処理水流入管が槽上部に、前記処理水
流出管が前記処理水の散水装置に接続され、該
散水装置に集水機能を併せもたせたものである
実用新案登録請求の範囲第1項記載の接触脱リ
ン装置。 3 前記酸及びアルカリ剤注入設備を前記循環水
管に開口させたものである実用新案登録請求の
範囲第1項又は第2項記載の接触脱リン装置。 4 前記循環水管が前記酸又はアルカリ剤注入設
備に連動するPH計を有するものである実用新案
登録請求の範囲第1項〜第3項記載の接触脱リ
ン装置。
[Claims for Utility Model Registration] 1. A tank equipped with a treated water inflow pipe, a treated water outflow pipe, and acid and alkali agent injection equipment is filled with solid particles having phosphorus adsorption ability, and the treated water is poured into the bottom of the tank. equipped with water sprinklers and air diffusers,
The catalytic dephosphorization device is further characterized in that a circulating water pipe is connected between the bottom and top of the tank. 2 The treated water inflow pipe is connected to the upper part of the tank, the treated water outflow pipe is connected to the treated water sprinkling device, and the sprinkling device also has a water collection function, Claim 1 Catalytic dephosphorization equipment as described. 3. The catalytic dephosphorization apparatus according to claim 1 or 2, wherein the acid and alkaline agent injection equipment is opened in the circulating water pipe. 4. The catalytic dephosphorization apparatus according to claims 1 to 3, wherein the circulating water pipe has a PH meter linked to the acid or alkali injection equipment.
JP18617284U 1984-12-10 1984-12-10 Expired JPS644468Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP18617284U JPS644468Y2 (en) 1984-12-10 1984-12-10

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP18617284U JPS644468Y2 (en) 1984-12-10 1984-12-10

Publications (2)

Publication Number Publication Date
JPS61102290U JPS61102290U (en) 1986-06-30
JPS644468Y2 true JPS644468Y2 (en) 1989-02-06

Family

ID=30743638

Family Applications (1)

Application Number Title Priority Date Filing Date
JP18617284U Expired JPS644468Y2 (en) 1984-12-10 1984-12-10

Country Status (1)

Country Link
JP (1) JPS644468Y2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4519485B2 (en) * 2004-03-04 2010-08-04 荏原エンジニアリングサービス株式会社 Phosphorus recovery method and apparatus

Also Published As

Publication number Publication date
JPS61102290U (en) 1986-06-30

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