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JPH0117753B2 - - Google Patents
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JPH0117753B2 - - Google Patents

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Publication number
JPH0117753B2
JPH0117753B2 JP55068138A JP6813880A JPH0117753B2 JP H0117753 B2 JPH0117753 B2 JP H0117753B2 JP 55068138 A JP55068138 A JP 55068138A JP 6813880 A JP6813880 A JP 6813880A JP H0117753 B2 JPH0117753 B2 JP H0117753B2
Authority
JP
Japan
Prior art keywords
phosphoric acid
water
wastewater
reaction
salts
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
Application number
JP55068138A
Other languages
Japanese (ja)
Other versions
JPS56163792A (en
Inventor
Teruyoshi Tsukamoto
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.)
Ebara Corp
Original Assignee
Ebara Infilco Co 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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP6813880A priority Critical patent/JPS56163792A/en
Publication of JPS56163792A publication Critical patent/JPS56163792A/en
Publication of JPH0117753B2 publication Critical patent/JPH0117753B2/ja
Granted legal-status Critical Current

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  • Removal Of Specific Substances (AREA)

Description

【発明の詳細な説明】 本発明は、燐酸を含有する水から燐酸を除去す
る方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing phosphoric acid from water containing phosphoric acid.

水中の燐酸は、アンモニアと並んで富栄養化成
分といわれ、河川、湖沼等における富栄養の根源
と目され、その効果的除去方法が望まれており、
下水の高度処理、廃水の高度処理技術もこの燐酸
の除去に向けられている。
Phosphoric acid in water is said to be a eutrophicating component along with ammonia, and is considered to be the source of eutrophication in rivers, lakes, etc., and an effective method for its removal is desired.
Advanced treatment technologies for sewage and wastewater are also aimed at removing phosphoric acid.

近時、廃水の高度処理技術の開発が要望されつ
つあり、その目的は第一に環境汚染の防止、第二
には有価資源、水資源の節減、再生水の再利用な
どである。しかし、廃水を再利用あるいは系外へ
放流する際に第一に問題となるのが、廃水中の燐
成分である。廃水中の燐は、そのまま湖、河川な
どに放流すると、藻類が繁殖して湖水、河川など
を無酸素状態にし、有用な生物を死に至らしめ、
逐には死の湖、河川にすることが多い。例えば、
我が国における霞が浦、びわ湖などはその例で、
各方面からその対策が検討されている。また、農
業用水として、燐成分によつて汚染された河川水
を利用すると作物が徒長するのみで、結実に至ら
ず、収量を減ずる例が多い。
In recent years, there has been a growing demand for the development of advanced wastewater treatment technology, and its purpose is firstly to prevent environmental pollution, secondly to save valuable resources and water resources, and to reuse reclaimed water. However, the primary problem when reusing wastewater or discharging it outside the system is the phosphorus content in the wastewater. If phosphorus in wastewater is directly discharged into lakes, rivers, etc., algae will proliferate, making the lake water, rivers, etc. anoxic, leading to the death of useful organisms.
It is often used as a lake or river of death. for example,
Examples of this include Lake Kasumigaura and Lake Biwa in Japan.
Countermeasures are being considered from various angles. Furthermore, when river water contaminated with phosphorus components is used for agricultural purposes, the crops only grow taller, but do not bear fruit, and in many cases, yields are reduced.

従来、廃水中の燐を除去するため、廃水中に
鉄、アルミニウムなどの金属イオンを添加して、
燐を除去する方法がその一例としてあるが、廃水
中にかなり多重の金属塩を添加することが多く、
およそ金属塩として100〜300mg/程度で凝集沈
殿する例が多い。また、最近、し尿無稀釈処理が
おこなわれるようになり、生物処理において脱燐
がおこなわれない場合には、PO4として700〜800
mg/の燐酸化合物を含むため、これを前記のご
とく、鉄塩を添加して処理せんとすると、千数百
ppm程度の添加を必要とする。しかも生成沈殿物
は極めてかさ高で濃縮が悪く、固一液分離が容易
でない。しかも、これら金属塩を添加して脱燐を
おこなわんとすると、副生する酸のためPHは極度
に低下するから、その中和のために系外からわざ
わざアルカリ剤を添加してPHを中性附近に調整す
る必要がある。即ち、極めて不経済な処理を実施
しているのが現状である。また、消石灰、生石
灰、ドロマイトなどを添加し、燐をカルシウムと
の化合物、例えばカルシウムアパタイトなどにし
て沈殿分離したのち、炭酸ガスを吹き込んで余分
の石灰を炭酸塩として沈殿させてPHを低下させる
方法もあるが、稀薄な燐酸を沈殿として除去する
ときには、かなり大過剰の石灰を必要とし、その
ためPHも11.5程度になる。よつて中和のための酸
剤を必要とし、極めて不経済と云うべきである。
本発明は、これら従来実施されている両者の欠点
即ち、金属塩添加による脱燐法において相当量の
金属塩を添加することによるPHの低下、石灰、ド
ロマイト添加による脱燐法において、相当量の石
灰、ドロマイト添加によるPHの上昇を排除すべく
研究を重ねたところ、この両脱燐剤を任意の比率
で利用することによつて、従来の欠点を解消する
ことができ、しかも、従来問題となつていた沈殿
濃縮性、脱水性を著るしく改善できることがわか
つた。即ち水中に溶存する燐酸化合物は、燐酸以
外に燐酸塩として存在するもので、該水中の燐酸
および燐酸塩の除去に当り、鉄塩、アルミニウム
塩の少なくとも一種と、カルシウム、マグネシウ
ムの酸化物、水酸化物、炭酸塩の少なくとも一種
とを同時または別時に添加することを特徴とする
ものである。
Conventionally, in order to remove phosphorus from wastewater, metal ions such as iron and aluminum were added to the wastewater.
One example is the method of removing phosphorus, which often involves adding multiple metal salts to the wastewater.
In many cases, it coagulates and precipitates at approximately 100 to 300 mg/metal salt. In addition, recently, human waste has been treated without dilution, and if dephosphorization is not performed in biological treatment, 700 to 800
mg/mg of phosphoric acid compound, so if you try to treat it by adding iron salts as mentioned above, it will be more than 1,000
It is necessary to add about ppm. Moreover, the resulting precipitate is extremely bulky and difficult to concentrate, making solid-liquid separation difficult. Moreover, if you try to dephosphorize by adding these metal salts, the PH will drop extremely due to the by-produced acid, so in order to neutralize it, an alkaline agent is added from outside the system to neutralize the PH. You need to adjust it to suit your sexuality. In other words, the current situation is that extremely uneconomical processing is being carried out. Another method is to add slaked lime, quicklime, dolomite, etc. to precipitate and separate phosphorus into a compound with calcium, such as calcium apatite, and then blow carbon dioxide gas to precipitate excess lime as carbonate to lower the pH. However, when removing dilute phosphoric acid as precipitate, a large excess of lime is required, resulting in a pH of around 11.5. Therefore, an acid agent is required for neutralization, which is extremely uneconomical.
The present invention addresses the drawbacks of both of these conventional methods, namely, the reduction in pH due to the addition of a considerable amount of metal salts in the dephosphorization method by adding metal salts, and the reduction in PH due to the addition of a considerable amount of metal salts in the dephosphorization method by adding lime and dolomite. After repeated research to eliminate the increase in PH caused by the addition of lime and dolomite, we found that by using these two dephosphorizing agents in any ratio, it was possible to eliminate the conventional drawbacks, and also to solve the conventional problems. It was found that the problems of precipitation concentration and dehydration could be significantly improved. In other words, phosphoric acid compounds dissolved in water exist in the form of phosphates other than phosphoric acid, and when removing phosphoric acid and phosphates from water, at least one of iron salts and aluminum salts, calcium and magnesium oxides, and water are used to remove phosphoric acid and phosphates. It is characterized by adding at least one of an oxide and a carbonate at the same time or separately.

本発明における系内反応を推定すると、次のよ
うな反応が進行して脱燐がおこなわれるものとみ
られる。即ち 2H3PO4+2Fecl3→2FePO4↓+6Hcl 6Hcl+3ca(OH)2→3CaCl2+6H2O 2Na3PO4+3CaCl2→Ca3(PO42↓+6Nacl よつて全反応 2H3PO4+2FeCl3+2Na3PO4+3Ca(OH)2→ 2FePO4+Ca3(PO42+6NaCl+6H2O 勿論、水中においては燐酸はPHによつては他に酸
性燐酸イオンとして存在しているものと思われる
が、基本的にはここに列記した反応が進行するも
のと思われる。
Estimating the in-system reactions in the present invention, it appears that the following reactions proceed to effect dephosphorization. That is, 2H 3 PO 4 +2Fecl 3 →2FePO 4 ↓+6Hcl 6Hcl+3ca(OH) 2 →3CaCl 2 +6H 2 O 2Na 3 PO 4 +3CaCl 2 →Ca 3 (PO 4 ) 2 ↓+6Nacl Therefore, the total reaction 2H 3 PO 4 +2FeCl 3 +2Na 3 PO 4 +3Ca(OH) 2 → 2FePO 4 +Ca 3 (PO 4 ) 2 +6NaCl+6H 2 O Of course, depending on the pH, phosphoric acid may also exist as an acidic phosphate ion in water, but basically In general, it is thought that the reactions listed here will proceed.

即ち従来はの反応又は次に示すの反応、即
ち 2H3PO4+3Ca(OH)2→Ca3(PO42↓+6H2O を利用して脱燐をおこなつていたためににおい
ては酸を副生することによりPHが著るしく低下
し、その低下を阻止する目的で苛性ソーダ、炭酸
ソーダを添加することがおこなわれていた。ま
た、の反応においては、Ca(OH)2を過剰添加
する必要からPH上昇がおこり、この中和に当り、
酸剤の添加を余儀なくさせられていた。本発明に
おいては、,,の反応即ち全反応たるの
反応を利用し、従来の欠点を一度に解消し、の
反応によつて副生する酸の除去に消石灰などのカ
ルシウム、マグネシウムの酸化物、水酸化物、炭
酸塩の少なくとも一種を利用し、副生する金属塩
を更に利用しての反応のごとく、燐酸塩に結合
する燐を除去せんとするものである。このよう
に、本発明においては遊離の酸が存在することも
なく、また、アルカリ過剰となることもなく、ほ
ぼ中性附近において、脱燐を進行させることがで
きる。しかも、生成する沈殿は分離が容易で、脱
水性が良く、極めて取扱いが容易であるなどの長
所を有するものである。
In other words, in the conventional method, dephosphorization was performed using the reaction or the reaction shown below, that is, 2H 3 PO 4 +3Ca(OH) 2 →Ca 3 (PO 4 ) 2 ↓+6H 2 O. This by-product causes a significant drop in pH, and in order to prevent this drop, caustic soda and soda carbonate have been added. In addition, in the reaction, the pH increases due to the need to add excessive Ca(OH) 2 , and in order to neutralize it,
They were forced to add acid agents. In the present invention, the disadvantages of the conventional methods are solved at once by utilizing the reaction of , , which is the total reaction, and oxides of calcium and magnesium such as slaked lime are used to remove the acid by-produced by the reaction of . This is a reaction that uses at least one of hydroxides and carbonates, and further uses metal salts as by-products to remove phosphorus bonded to phosphates. In this way, in the present invention, dephosphorization can proceed in the vicinity of neutrality without the presence of free acid or excess alkali. Moreover, the produced precipitate has advantages such as easy separation, good dehydration properties, and extremely easy handling.

本発明において使用する金属塩としては、鉄
塩、アルミニウム塩に限定される。これ以外のも
のだと、同時あるいは別時に添加するカルシウ
ム、マグネシウムの酸化物、水酸化物、炭酸塩に
よつて中和できない。
The metal salts used in the present invention are limited to iron salts and aluminum salts. Other substances cannot be neutralized by calcium or magnesium oxides, hydroxides, or carbonates added at the same time or separately.

これら両者の添加順序はとくに制限はなく、ま
た、同時でも別時でもよい。反応時間は燐酸イオ
ンの濃度にもよるが少なくとも5分は必要であ
る。
There is no particular restriction on the order in which these two are added, and they may be added at the same time or at different times. The reaction time depends on the concentration of phosphate ions, but at least 5 minutes is required.

次に本発明の実施例について説明する。 Next, examples of the present invention will be described.

燐酸イオンとして760mg/含有する生物処理
した有機性廃水に塩化第二鉄として750mg/添
加して2分撹拌後、消石灰として510mg/添加
し、更に5分間撹拌後、沈降分離に服し、固一液
分離をおこなつた。その分離水を採取し、濾過し
て溶存する燐酸イオンの濃度を測定したところ
PO4として5mg/,PH6.0であつた。対照例
として、塩化第二鉄1400mg/を添加して同じレ
ベルの脱燐を実施したが、その分離水の濾過処理
水中の燐酸イオンはPO4として4〜5mg/,
PHは2.5〜2.7であり、処理水のPHを6.8〜7.0に調
整するために1010mg/の苛性ソーダを添加する
必要が生じた。
750 mg of ferric chloride was added to the biologically treated organic wastewater containing 760 mg of phosphate ion, and after stirring for 2 minutes, 510 mg of slaked lime was added, and after further stirring for 5 minutes, it was subjected to sedimentation and separation. Liquid separation was performed. The separated water was collected, filtered, and the concentration of dissolved phosphate ions was measured.
It was 5 mg/PO 4 and pH 6.0. As a control example, the same level of dephosphorization was carried out by adding 1400 mg/ferric chloride, but the phosphate ions in the filtered water of the separated water were 4 to 5 mg/, as PO4 .
The PH was 2.5 to 2.7, and it became necessary to add 1010 mg of caustic soda to adjust the PH of the treated water to 6.8 to 7.0.

なお、固一液分離の手段として透過膜装置を利
用したが同様な結果が得られた。透過膜としては
分画分子量6000の限外濾過膜を用いた。前記脱燐
剤添加後の反応時間は前記実施例と同様であつ
た。
Although a permeable membrane device was used as a means for solid-liquid separation, similar results were obtained. As the permeation membrane, an ultrafiltration membrane with a molecular weight cutoff of 6000 was used. The reaction time after addition of the dephosphorizing agent was the same as in the previous example.

このように本発明においては、鉄塩等の金属塩
単独使用、あるいはカルシウム化合物単独使用に
おける欠点を是正することができ、PH調整の目的
をもつて、特に薬剤の注入を必ずしも必要とせ
ず、添加したとしても従来法より極めて少ない量
ですませることができるので、経済的にも有利と
なる。
In this way, the present invention can correct the drawbacks of using metal salts such as iron salts alone or calcium compounds alone, and can be used for the purpose of pH adjustment without necessarily requiring injection of chemicals. Even if it does, it can be done in an extremely small amount compared to the conventional method, which is economically advantageous.

Claims (1)

【特許請求の範囲】[Claims] 1 燐酸含有液に、不溶性燐酸化合物を生成せし
める鉄塩、アルミニウム塩の少なくとも一種と、
カルシウム、マグネシウムの酸化物、水酸化物、
炭酸塩の少なくとも一種とを同時にまたは別時に
添加し、ほぼ中性付近で脱燐することを特徴とす
る水中に溶存する燐酸の除去方法。
1. At least one of iron salts and aluminum salts that produce an insoluble phosphoric acid compound in a phosphoric acid-containing liquid;
Calcium, magnesium oxides, hydroxides,
A method for removing phosphoric acid dissolved in water, which comprises adding at least one type of carbonate at the same time or separately, and dephosphorizing the water at a state near neutrality.
JP6813880A 1980-05-22 1980-05-22 Removing method for phosphoric acid dissolved in water Granted JPS56163792A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6813880A JPS56163792A (en) 1980-05-22 1980-05-22 Removing method for phosphoric acid dissolved in water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6813880A JPS56163792A (en) 1980-05-22 1980-05-22 Removing method for phosphoric acid dissolved in water

Publications (2)

Publication Number Publication Date
JPS56163792A JPS56163792A (en) 1981-12-16
JPH0117753B2 true JPH0117753B2 (en) 1989-03-31

Family

ID=13365078

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6813880A Granted JPS56163792A (en) 1980-05-22 1980-05-22 Removing method for phosphoric acid dissolved in water

Country Status (1)

Country Link
JP (1) JPS56163792A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4867269B2 (en) * 2005-10-06 2012-02-01 栗田工業株式会社 Method and apparatus for treating fluorine-containing water
JP2011062680A (en) * 2009-09-16 2011-03-31 Kimihiko Okanoe Liquid cleaning apparatus

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS535861A (en) * 1976-07-06 1978-01-19 Mitsui Toatsu Chem Inc Process for treating drain water containing phosphoric acid

Also Published As

Publication number Publication date
JPS56163792A (en) 1981-12-16

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