JPH06304552A - Removing method of phosphorus and ammonia - Google Patents

Removing method of phosphorus and ammonia

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Publication number
JPH06304552A
JPH06304552A JP9615893A JP9615893A JPH06304552A JP H06304552 A JPH06304552 A JP H06304552A JP 9615893 A JP9615893 A JP 9615893A JP 9615893 A JP9615893 A JP 9615893A JP H06304552 A JPH06304552 A JP H06304552A
Authority
JP
Japan
Prior art keywords
ammonia
zeolite
phosphorus
activated alumina
solution
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
JP9615893A
Other languages
Japanese (ja)
Inventor
Isamu Norimatsu
勇 則松
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.)
Hazama Corp
Original Assignee
Hazama Gumi 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 Hazama Gumi Ltd filed Critical Hazama Gumi Ltd
Priority to JP9615893A priority Critical patent/JPH06304552A/en
Publication of JPH06304552A publication Critical patent/JPH06304552A/en
Pending legal-status Critical Current

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  • Water Treatment By Sorption (AREA)
  • Treatment Of Water By Ion Exchange (AREA)

Abstract

PURPOSE:To effectively and easily remove phosphorus component and ammonia component in sewage water or river water by allowing an aq. solution containing phosphorus ion and ammonia ion to come into contact with zeolite before allowing it to come into contact with an active alumina. CONSTITUTION:In the case of removing phosphorus component and ammonia component from the solution containing phosphorus and ammonia (aq. solution to be treated), at first, the aq. solution to be treated is brought into contact with zeolite. That is, the aq. solution to be treated is passed through a column or the like, in which zeolite is packed. In this case, the flow rate of the aq. solution and the packing quantity of zeolite are adjusted so that the contact time of the aq. solution to be treated with the zeolite is set for >=10 min, particularly preferably 10-20 min. Next, the aq. solution to be treated, which has been brought into contact with zeolite, is brought into contact with the active alumina. As a result, phosphorus component and ammonia component in the aq. solution to be treated is more efficiently removed than in the case of removing phosphorus component by active alumina only.

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、下水、河川水等におい
てリン成分及びアンモニア成分を効率良く除去すること
ができるリン及びアンモニアの除去方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a phosphorus and ammonia removing method capable of efficiently removing phosphorus and ammonia components in sewage, river water and the like.

【0002】[0002]

【従来の技術】従来より、下水、河川水等に含有される
リン成分及びアンモニア成分が、湖沼等の富栄養化及び
公害の原因として知られており、これらの成分を除去す
る方法が種々開発されている。例えばリン酸の除去方法
としては、活性アルミナによる吸着法が一般的に知られ
ており、また該活性アルミナによる処理量を増大させる
ために、カルシウムイオンを共存させることが提案され
ている。一方アンモニアの除去方法としては、ゼオライ
トによるイオン交換方法が一般的に知られている。
2. Description of the Related Art Conventionally, phosphorus and ammonia components contained in sewage, river water, etc. have been known to cause eutrophication and pollution of lakes and marshes, and various methods for removing these components have been developed. Has been done. For example, as a method for removing phosphoric acid, an adsorption method using activated alumina is generally known, and it has been proposed to coexist with calcium ions in order to increase the treatment amount by the activated alumina. On the other hand, as a method for removing ammonia, an ion exchange method using zeolite is generally known.

【0003】しかしながら、前記リン成分を除去する方
法において、活性アルミナとカルシウムイオンを共存さ
せる方法では、従来の活性アルミナのみによる除去法に
比して有効にリン成分を除去することができるが、カル
シウムイオンの添加量及びpH調整等の処理条件を管理
する必要があり、方法自体煩雑化するという問題があ
る。また従来リン成分又はアンモニア成分のどちらか一
方を除去すれば十分であると考えられており、リン成分
及びアンモニア成分を同時に除去する方法としては、唯
一処理条件制御が問題視される微生物による処理方法が
提案されているにすぎないのが現状である。そこでリン
成分及びアンモニア成分を同時に除去するために、前記
活性アルミナ処理とゼオライト処理とを組合せることが
考えられるが、単に組合せたのみでは、これらの成分を
有効に除去することはできず、このように活性アルミナ
処理とゼオライト処理とを組合せること自体行なわれて
いないのが実状である。
However, in the method for removing the phosphorus component, the method in which activated alumina and calcium ions coexist can remove the phosphorus component more effectively than the conventional removal method using activated alumina alone. It is necessary to control the processing conditions such as the amount of added ions and pH adjustment, and there is a problem that the method itself becomes complicated. Further, it has been conventionally considered that it is sufficient to remove either the phosphorus component or the ammonia component, and as a method for simultaneously removing the phosphorus component and the ammonia component, the only treatment condition control method is a treatment method using a microorganism. It is the current situation that is only proposed. Therefore, in order to remove the phosphorus component and the ammonia component at the same time, it is conceivable to combine the activated alumina treatment and the zeolite treatment, but it is not possible to effectively remove these components by simply combining them. The actual situation is that the combination of the activated alumina treatment and the zeolite treatment has not been performed.

【0004】また一般的にリン成分除去に使用される活
性アルミナは、高価であるため、リン成分除去量を低下
させることなく、活性アルミナの使用期間を延長する技
術の開発が望まれている。
Further, since activated alumina generally used for phosphorus component removal is expensive, it is desired to develop a technique for extending the period of use of activated alumina without reducing the phosphorus component removal amount.

【0005】[0005]

【発明が解決しようとする課題】本発明の目的は、下
水、河川水等において有効に、且つ容易にリン成分及び
アンモニア成分を除去することができるリン及びアンモ
ニアの除去方法を提供することにある。
SUMMARY OF THE INVENTION An object of the present invention is to provide a method for removing phosphorus and ammonia which can effectively and easily remove phosphorus components and ammonia components in sewage, river water and the like. .

【0006】本発明の別の目的は、使用する活性アルミ
ナの使用期間を、リン成分の除去量の低下を招くことな
く延長させることができるリン及びアンモニアの除去方
法を提供することにある。
[0006] Another object of the present invention is to provide a method for removing phosphorus and ammonia which can prolong the period of use of the activated alumina used without reducing the removal amount of phosphorus components.

【0007】[0007]

【課題を解決するための手段】本発明によれば、リンイ
オン及びアンモニウムイオンを含む水溶液を、ゼオライ
トに接触させた後、活性アルミナに接触させることを特
徴とするリン及びアンモニアの除去方法が提供される。
According to the present invention, there is provided a method for removing phosphorus and ammonia, which comprises contacting an aqueous solution containing phosphorus ions and ammonium ions with zeolite and then with activated alumina. It

【0008】以下本発明を更に詳細に説明する。The present invention will be described in more detail below.

【0009】本発明のリン及びアンモニアの除去方法
は、下水、河川水、工場廃水、下水処理場エアレーショ
ンタンク中における廃水等のリン及びアンモニアを含む
水溶液を、ゼオライトに接触させた後、活性アルミナに
接触させることにより行なうことができる。
The method for removing phosphorus and ammonia of the present invention is a method in which an aqueous solution containing phosphorus and ammonia such as sewage, river water, industrial wastewater, wastewater in an aeration tank of a sewage treatment plant is brought into contact with zeolite, and then activated alumina is added. It can be carried out by contact.

【0010】本発明の除去方法においては、まずリン及
びアンモニアを含む水溶液をゼオライトに接触させる。
前記ゼオライトとしては、通常アンモニアの除去に使用
されるゼオライト、具体的には例えばクリノプチロライ
ト(clinoptilolite)系ゼオライト、モルデナイト(morde
nite)系ゼオライト等を好ましく挙げることができ、そ
の粒径は、2.3〜4.6mmであるのが好ましい。リ
ン及びアンモニアを含む水溶液をゼオライトに接触させ
るには、例えばゼオライトをカラム等に充填し、該ゼオ
ライトが充填されたカラム等にリン及びアンモニアを含
む水溶液を通過させることにより行なうことができ、こ
の際ゼオライトの充填量は、含有されるアンモニアの量
により異なるが、好ましくはリン及びアンモニアを含む
水溶液とゼオライトとの接触時間が、10分以上、特に
10〜20分となるように、流入速度及びゼオライト充
填量を調整すれば良い。該接触時間が10分未満の場合
には、アンモニアの除去量が低下するので好ましくな
い。このようなゼオライト処理は、好ましくはpH7〜
8.5の条件下行なうのが好ましく、このゼオライト処
理によって、まずアンモニアが有効に除去させるととも
に、ゼオライトのイオン交換作用によって、処理したリ
ン及びアンモニアを含む水溶液中にカルシウムイオンが
含有される。
In the removal method of the present invention, first, an aqueous solution containing phosphorus and ammonia is brought into contact with zeolite.
As the zeolite, a zeolite usually used for removing ammonia, specifically, for example, clinoptilolite-based zeolite, mordenite (morde)
Preferable examples thereof include nite) -based zeolite, and the particle size thereof is preferably 2.3 to 4.6 mm. The aqueous solution containing phosphorus and ammonia can be brought into contact with the zeolite by, for example, packing the zeolite in a column or the like, and passing the aqueous solution containing the phosphorus and ammonia through the column or the like packed with the zeolite. The loading of zeolite varies depending on the amount of ammonia contained, but preferably the inflow rate and the zeolite are such that the contact time between the aqueous solution containing phosphorus and ammonia and the zeolite is 10 minutes or more, particularly 10 to 20 minutes. It is sufficient to adjust the filling amount. If the contact time is less than 10 minutes, the amount of ammonia removed decreases, which is not preferable. Such zeolite treatment preferably has a pH of 7-
It is preferable to carry out under the conditions of 8.5, and by this zeolite treatment, ammonia is first effectively removed, and calcium ion is contained in the treated aqueous solution containing phosphorus and ammonia by the ion exchange action of the zeolite.

【0011】次に本発明の除去方法では、前記ゼオライ
ト処理されたリン及びアンモニアを含む水溶液を、活性
アルミナに接触させる。前記活性アルミナとしては、通
常リン除去に使用される活性アルミナ等を好ましく用い
ることができ、その粒径は、2.0〜4.0mmである
のが好ましい。前記ゼオライト処理されたリン及びアン
モニアを含む水溶液を活性アルミナに接触させるには、
例えば活性アルミナをカラム等に充填し、該活性アルミ
ナが充填されたカラム等に、前記ゼオライト処理された
リン及びアンモニアを含む水溶液を通過させることによ
り行なうことができる。この際、ゼオライト処理された
リン及びアンモニアを含む水溶液の活性アルミナへの接
触は、前記ゼオライト処理後、連続的に活性アルミナ処
理が実施できるように前記活性アルミナが充填されたカ
ラム等を配設するのが好ましい。前記活性アルミナの充
填量は、含有されるリンの量により異なるが、好ましく
は前記ゼオライト処理されたリン及びアンモニアを含む
水溶液と活性アルミナとの接触時間が、10〜30分、
特に10〜20分となるように、流入速度及び活性アル
ミナ充填量を調整すれば良い。該接触時間が10分未満
の場合には、リンの除去量が低下し、また30分を超え
る場合には、リンの除去能の向上が期待できず、しかも
活性アルミナのリン除去能寿命が低下するので好ましく
ない。このような活性アルミナ処理は、好ましくはpH
7〜8.5の条件下行なうのが好ましい。
Next, in the removal method of the present invention, the zeolite-treated aqueous solution containing phosphorus and ammonia is brought into contact with activated alumina. As the activated alumina, activated alumina or the like usually used for phosphorus removal can be preferably used, and the particle size thereof is preferably 2.0 to 4.0 mm. To bring the aqueous solution containing the zeolite-treated phosphorus and ammonia into contact with activated alumina,
For example, it can be carried out by packing activated alumina in a column or the like, and passing the zeolite-treated aqueous solution containing phosphorus and ammonia through the column or the like. At this time, contact of the zeolite-treated aqueous solution containing phosphorus and ammonia with the activated alumina is performed by disposing a column or the like packed with the activated alumina so that the activated alumina treatment can be continuously performed after the zeolite treatment. Is preferred. The filling amount of the activated alumina varies depending on the amount of phosphorus contained, but preferably the contact time between the aqueous solution containing the zeolite-treated phosphorus and ammonia and the activated alumina is 10 to 30 minutes,
In particular, the inflow rate and the activated alumina filling amount may be adjusted so as to be 10 to 20 minutes. When the contact time is less than 10 minutes, the phosphorus removal amount decreases, and when it exceeds 30 minutes, the phosphorus removal ability cannot be expected to be improved, and the phosphorus removal ability life of the activated alumina decreases. Is not preferred. Such activated alumina treatment is preferably pH
It is preferable to carry out under the conditions of 7 to 8.5.

【0012】本発明の除去方法では、前記ゼオライト処
理の後、活性アルミナ処理を行なう必要があり、活性ア
ルミナ処理を行なった後、ゼオライト処理を行なった
り、活性アルミナ処理とゼオライト処理とを同時に行な
う場合には、リン除去能が低下し、更に活性アルミナの
リン除去能寿命が低下する。
In the removal method of the present invention, it is necessary to carry out the active alumina treatment after the above zeolite treatment. When the active alumina treatment is performed and then the zeolite treatment is performed, or when the active alumina treatment and the zeolite treatment are simultaneously performed. In addition, the phosphorus removing ability is lowered, and further the phosphorus removing ability life of the activated alumina is shortened.

【0013】本発明の除去方法において、前記使用され
るゼオライト及び活性アルミナは、リン酸及びアンモニ
ウムの除去量が、それぞれリン酸24000mg/リッ
トル以下、アンモニウム6000mg/リットル以下程
度になった際に交換すれば良く、他に特別な制御等を必
要としない。
In the removal method of the present invention, the zeolite and activated alumina used are replaced when the removal amounts of phosphoric acid and ammonium are about 24000 mg / liter or less of phosphoric acid and 6000 mg / liter or less of ammonium, respectively. It does not need any special control.

【0014】[0014]

【発明の効果】本発明のリン及びアンモニアの除去方法
では、単にリン及びアンモニアを含む水溶液をゼオライ
ト及び活性アルミナに接触させるという簡易な方法で有
効にリン及びアンモニアを除去することができ、しかも
ゼオライト及び活性アルミナへの接触を、ゼオライトに
接触させた後、活性アルミナに接触させるので、活性ア
ルミナ単独によるリン成分除去よりも、活性アルミナの
量を多くすることなく、リン除去量が増大し、しかも活
性アルミナのリン除去能寿命を長くすることができる。
According to the method for removing phosphorus and ammonia of the present invention, phosphorus and ammonia can be effectively removed by a simple method in which an aqueous solution containing phosphorus and ammonia is simply brought into contact with zeolite and activated alumina. And, the contact with the activated alumina, after contacting the zeolite, is contacted with the activated alumina, the phosphorus removal amount is increased without increasing the amount of the activated alumina, as compared with the removal of the phosphorus component by the activated alumina alone, and The life of phosphorus removal ability of activated alumina can be extended.

【0015】[0015]

【実施例】以下本発明を実施例及び比較例により更に詳
細に説明するが、本発明はこれらに限定されるものでは
ない。
EXAMPLES The present invention will be described in more detail with reference to Examples and Comparative Examples, but the present invention is not limited thereto.

【0016】[0016]

【実施例1】内径30mmのポリプロピレン製カラム
に、粒径3.0mmの活性アルミナ(触媒化成工業株式
会社製)20gを25mlとなるように充填した。一方
同様なカラムに粒径4.0mmの天然ゼオライト18g
を25mlとなるように充填した。次いでゼオライトを
充填したカラムと活性アルミナを充填したカラムとを直
列に配列し、ゼオライトを充填したカラム側から試料液
を、SV=5(125ml/時間)の流速で通水した。
試料液としては、リン酸二水素カリウムと塩化アンモニ
ウムを水道水に溶解したリン酸濃度5mg/リットル、
アンモニア濃度30mg/リットル含有水溶液を使用し
た。ゼオライトを充填したカラムと活性アルミナを充填
したカラムとを通過した処理液中のリン酸濃度及びアン
モニア濃度を、試料液通液量に応じて測定した。リン酸
濃度変化の結果を図1に、またアンモニア濃度変化の結
果を図2に示す。
Example 1 A polypropylene column having an inner diameter of 30 mm was filled with 20 g of activated alumina (manufactured by Catalysts & Chemicals Industry Co., Ltd.) having a particle diameter of 3.0 mm so as to be 25 ml. On the other hand, 18 g of natural zeolite with a particle size of 4.0 mm is applied to the same column.
Was charged to 25 ml. Next, the column packed with zeolite and the column packed with activated alumina were arranged in series, and the sample liquid was passed from the column packed with zeolite at a flow rate of SV = 5 (125 ml / hour).
As a sample solution, potassium dihydrogen phosphate and ammonium chloride were dissolved in tap water to have a phosphoric acid concentration of 5 mg / liter,
An aqueous solution containing 30 mg / liter of ammonia was used. The concentration of phosphoric acid and the concentration of ammonia in the treatment liquid that passed through the column filled with zeolite and the column filled with activated alumina were measured according to the amount of sample liquid passed. The results of changes in phosphoric acid concentration are shown in FIG. 1, and the results of changes in ammonia concentration are shown in FIG.

【0017】[0017]

【比較例1】試料液の通水を、ゼオライトを充填したカ
ラム側からではなく、反対に活性アルミナを充填したカ
ラム側から行なった以外は、実施例1と同様に活性アル
ミナを充填したカラムとゼオライトを充填したカラムと
を通過した処理液中のリン酸濃度及びアンモニア濃度
を、試料液通液量に応じて測定した。この際アンモニア
濃度変化は実施例1と変わらなかった。またリン酸濃度
変化の結果を図1に示す。
Comparative Example 1 A column filled with activated alumina was prepared in the same manner as in Example 1 except that water was passed through the sample solution not from the side filled with zeolite but from the side filled with activated alumina. The phosphoric acid concentration and the ammonia concentration in the treatment liquid that passed through the column packed with zeolite were measured according to the amount of the sample liquid passed. At this time, the change in ammonia concentration was the same as in Example 1. The results of changes in phosphoric acid concentration are shown in FIG.

【0018】[0018]

【比較例2】試料液を活性アルミナを充填したカラムの
みを通過させた以外は、実施例1と同様に活性アルミナ
を充填したカラムを通過した処理液中のリン酸濃度及び
アンモニア濃度を、試料液通液量に応じて測定した。こ
の際アンモニアの除去は行なわれていなかった。またリ
ン酸濃度変化の結果を図1に示す。
[Comparative Example 2] The phosphoric acid concentration and the ammonia concentration in the treatment liquid passed through the column filled with activated alumina were the same as in Example 1 except that the sample liquid was passed through only the column filled with activated alumina. The measurement was performed according to the liquid passing amount. At this time, ammonia was not removed. The results of changes in phosphoric acid concentration are shown in FIG.

【0019】図1及び2の結果より、本発明の方法で
は、アンモニアを有効に除去すると共に、リン酸の除去
も、活性アルミナ単独の比較例2及び活性アルミナに接
触させた後、ゼオライトに接触させる比較例1に比し
て、増大させることができ、しかも前記比較例1及び2
のリン除去能の低下に比して、低下速度が遅いため、活
性アルミナのリン除去能寿命が延長させることも可能で
あることが判る。
From the results shown in FIGS. 1 and 2, in the method of the present invention, ammonia is effectively removed, and phosphoric acid is also removed by contacting Comparative Example 2 with activated alumina alone and activated alumina, and then contacting with zeolite. In comparison with Comparative Example 1, the amount can be increased, and Comparative Examples 1 and 2
It is understood that the life of phosphorus removal ability of activated alumina can be extended because the rate of decrease is slower than the reduction of phosphorus removal ability of.

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

【図1】図1は、実施例及び比較例における試料液の通
液量変化に伴うリン酸除去量を示すグラフである。
FIG. 1 is a graph showing the amount of phosphoric acid removed according to changes in the amount of sample liquid passing through in Examples and Comparative Examples.

【図2】図2は、実施例1における試料液の通液量変化
に伴うアンモニア除去量を示すグラフである。
FIG. 2 is a graph showing the amount of ammonia removed according to a change in the amount of sample solution passed in Example 1.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 リンイオン及びアンモニウムイオンを含
む水溶液を、ゼオライトに接触させた後、活性アルミナ
に接触させることを特徴とするリン及びアンモニアの除
去方法。
1. A method for removing phosphorus and ammonia, which comprises bringing an aqueous solution containing phosphorus ions and ammonium ions into contact with zeolite and then contacting with activated alumina.
JP9615893A 1993-04-22 1993-04-22 Removing method of phosphorus and ammonia Pending JPH06304552A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9615893A JPH06304552A (en) 1993-04-22 1993-04-22 Removing method of phosphorus and ammonia

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9615893A JPH06304552A (en) 1993-04-22 1993-04-22 Removing method of phosphorus and ammonia

Publications (1)

Publication Number Publication Date
JPH06304552A true JPH06304552A (en) 1994-11-01

Family

ID=14157554

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9615893A Pending JPH06304552A (en) 1993-04-22 1993-04-22 Removing method of phosphorus and ammonia

Country Status (1)

Country Link
JP (1) JPH06304552A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006016349A (en) * 2004-07-02 2006-01-19 Chiyoda Corp Method for eliminating iodine from organic acid
JP2010051918A (en) * 2008-08-29 2010-03-11 Taisei Corp Water purification method and apparatus therefor
JP2018008180A (en) * 2016-07-11 2018-01-18 太平洋セメント株式会社 Water treatment material and production method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006016349A (en) * 2004-07-02 2006-01-19 Chiyoda Corp Method for eliminating iodine from organic acid
JP2010051918A (en) * 2008-08-29 2010-03-11 Taisei Corp Water purification method and apparatus therefor
JP2018008180A (en) * 2016-07-11 2018-01-18 太平洋セメント株式会社 Water treatment material and production method thereof

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