JPS6130838B2 - - Google Patents
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- Publication number
- JPS6130838B2 JPS6130838B2 JP57079887A JP7988782A JPS6130838B2 JP S6130838 B2 JPS6130838 B2 JP S6130838B2 JP 57079887 A JP57079887 A JP 57079887A JP 7988782 A JP7988782 A JP 7988782A JP S6130838 B2 JPS6130838 B2 JP S6130838B2
- Authority
- JP
- Japan
- Prior art keywords
- calcium
- carrier
- seed crystal
- phosphoric acid
- crystal material
- 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.)
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Description
【発明の詳細な説明】
本発明は、液中に溶解して存在するリン酸化合
物を晶析して、該液中から分離するための晶析処
理用種晶材の製造法に係り、特に下水等の用廃水
中に含まれるリン酸化合物を効率よく晶析させる
ために好適な種晶材の製造法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing a seed crystal material for crystallization treatment for crystallizing a phosphoric acid compound dissolved in a liquid and separating it from the liquid. The present invention relates to a method for producing a seed crystal material suitable for efficiently crystallizing phosphoric acid compounds contained in wastewater such as sewage.
自然水系に排出される各種廃水中には、無機性
のオルトリン酸塩、各種の縮合リン酸塩、有機性
リン酸塩などのリン酸化合物がいろいろな形態で
含まれており、これらのリン酸化合物の存在が河
川、湖沼、内湾などの閉鎖性水域の富栄養化の大
きな原因となつている。 Various wastewaters discharged into natural water systems contain various forms of phosphate compounds such as inorganic orthophosphates, various condensed phosphates, and organic phosphates. The presence of compounds is a major cause of eutrophication in closed water bodies such as rivers, lakes, and inner bays.
これらの液中に溶解して存在するリン酸化合物
の除去方法の一つとして晶析処理法がある。この
方法はカルシウムイオンの存在下でPHを7以上に
調整した被処理水を、リン酸カルシウム塩を主成
分とするリン鉱石の充填層に通し、液中のリン酸
塩をリン酸カルシウムとしてリン鉱石の表面に析
出させることを基本としている。この際、リン鉱
石は種晶物質として作用し、リン鉱石の表面には
当初はリン酸カルシウム化合物の中間生成物が形
成されるが、時間の経過とともに安定したヒドロ
キシアパタイトに変化するといわれている。この
晶析処理法は汚泥の発生量が少ないこと、処理操
作が簡便であることなどの長所を有しており、リ
ン酸の濃度が比較的低い下水の3次処理用として
最近採用されつつある。 One of the methods for removing phosphoric acid compounds dissolved in these liquids is a crystallization treatment method. In this method, water to be treated whose pH has been adjusted to 7 or higher in the presence of calcium ions is passed through a packed bed of phosphate rock whose main component is calcium phosphate salt, and the phosphate in the liquid is converted to calcium phosphate and applied to the surface of the phosphate rock. Basically, it is precipitated. At this time, phosphate rock acts as a seed crystal material, and an intermediate product of a calcium phosphate compound is initially formed on the surface of phosphate rock, but it is said to change into stable hydroxyapatite over time. This crystallization treatment method has the advantages of generating little sludge and simple treatment operations, and has recently been adopted as a tertiary treatment for sewage with relatively low phosphoric acid concentrations. .
ところで、この晶析処理法は、種晶材料である
天然産のリン鉱石が、比較的高価であること、不
純物を含むため液中のリン酸塩の処理能力が一定
しないこと、運転途中で処理能力が低下する場合
があることなどの欠点を有していた。また、リン
鉱石自体、産地によつて組成、性状が著しく相違
しており、性能保証の面での不安定要素、充填材
としての物理的性質の適性についても問題があつ
た。 By the way, this crystallization treatment method is difficult because the naturally produced phosphate rock that is the seed crystal material is relatively expensive, contains impurities, so the ability to treat phosphate in the liquid is not constant, and the treatment process is difficult during operation. This method had drawbacks such as a decrease in performance. In addition, the composition and properties of phosphate rock itself vary significantly depending on the production area, and there have been problems with unstable factors in terms of performance guarantee and suitability of physical properties as a filler.
本発明の目的は、上記従来技術の欠点を解消
し、上記リン鉱石に代る安価でかつ処理性能が安
定した液中のリン酸を晶析する種晶材の製造法を
提供することにある。 An object of the present invention is to eliminate the drawbacks of the above-mentioned conventional techniques and to provide a method for producing a seed crystal material for crystallizing phosphoric acid in a liquid that is inexpensive and has stable processing performance, instead of the above-mentioned phosphate rock. .
この目的を達成するため、本発明に係る種晶材
の製造法は、マグネシア系はジルコニア系の担体
にリン酸を吸着させた後、塩化カルシウム、水酸
化カルシウム及び酸化カルシウムから選択された
カルシウム化合物の少なくとも1種を担持させる
ことを特徴とする。 To achieve this objective, the method for producing a seed crystal material according to the present invention involves adsorbing phosphoric acid onto a magnesia-based or zirconia-based carrier, and then adsorbing a calcium compound selected from calcium chloride, calcium hydroxide, and calcium oxide. It is characterized by carrying at least one kind of.
ここに、担体とは種晶材の母体となる粒状体を
意味し、リン酸塩との親和性のある物質が選ばれ
る。粒状体は球状のもの又は破砕状のものの双方
を含む。例えば、マグネシウム又はジルコニウム
の酸化物を主成分とするものが好ましく用いられ
る。これらの担体にリン酸を吸着させるには、例
えばPHを5.5以下に調整した0.01〜5%のリン酸
塩溶液に前記担体を浸漬することによつて実現で
きる。浸漬時間は通常2〜50時間とされる。担体
に吸着させるリン酸の量は担体1g当り2〜20mg
が好ましい。リン酸塩溶液の濃度を低くして、浸
漬時間を長くする方が、その逆の場合よりも吸着
したリン酸の安定度が高い。浸漬後安定化のため
に乾燥加熱することが好ましい。 Here, the term "carrier" refers to a granular material that serves as a matrix for the seed crystal material, and a substance that has an affinity for phosphate is selected. The granules include both spherical and crushed particles. For example, those whose main component is an oxide of magnesium or zirconium are preferably used. Adsorption of phosphoric acid onto these carriers can be achieved, for example, by immersing the carrier in a 0.01-5% phosphate solution whose pH is adjusted to 5.5 or less. The immersion time is usually 2 to 50 hours. The amount of phosphoric acid adsorbed on the carrier is 2 to 20 mg per 1 g of carrier.
is preferred. Lowering the concentration of the phosphate solution and increasing the soaking time results in higher stability of the adsorbed phosphoric acid than vice versa. It is preferable to perform dry heating for stabilization after immersion.
上記に例示した要領でリン酸を吸着させた担体
(以下、吸着担体という。)に対して次に、カルシ
ウム化合物を固着させる。このカルシウム化合物
の固着処理の方法としては、次の方法がある。 Next, a calcium compound is fixed to the carrier (hereinafter referred to as adsorption carrier) on which phosphoric acid has been adsorbed in the manner exemplified above. The following methods can be used to fix the calcium compound.
(1) 吸着担体を、カルシウム化合物溶液に浸漬す
る方法
この方法は、吸着担体を湿潤したまま、若し
くは乾燥加熱後、例えば0.05〜10%のカルシウ
ム化合物溶液に10〜100時間浸漬する。この処
理により、前記の吸着したリン酸とカルシウム
イオンが反応し、担体の表面に多数の活性点が
分布形成される。これらの活性点の化学的組成
は明らかではないが、リン酸カルシウム又はそ
の中間生成物と推定される。前記リン酸の吸着
処理と同様に、この処理は低い濃度のカルシウ
ム化合物溶液に、吸着担体を長時間浸漬するこ
とが好ましい。PHに対する依存性は比較的少な
い。担体に固着させるカルシウムの量は通常担
体1g当り4〜50mgが好ましい。(1) Method of immersing an adsorption carrier in a calcium compound solution In this method, the adsorption carrier is immersed in a 0.05 to 10% calcium compound solution for 10 to 100 hours, either while being wet or after dry heating. Through this treatment, the adsorbed phosphoric acid and calcium ions react, and a large number of active sites are distributed on the surface of the carrier. Although the chemical composition of these active sites is not clear, they are presumed to be calcium phosphate or its intermediate products. As with the phosphoric acid adsorption treatment, this treatment is preferably performed by immersing the adsorption carrier in a low concentration calcium compound solution for a long period of time. There is relatively little dependence on PH. The amount of calcium fixed on the carrier is usually preferably 4 to 50 mg per gram of carrier.
(2) 湿潤状態の吸着担体とカルシウム化合物の微
粉末とを十分に混合したのち、乾燥する方法
この方法は特に乾燥工程において、担体に吸
着したリン酸とカルシウムイオンが徐々に反応
し、担体の表面に活性点を形成する。乾燥後、
さらに120〜200℃で2時間程度加熱することが
好ましい。加熱によりカルシウムの固着がより
強固となる。(2) A method of thoroughly mixing a wet adsorption carrier and fine powder of a calcium compound, and then drying this method. Especially in the drying process, phosphoric acid and calcium ions adsorbed on the carrier gradually react with each other. Forms active points on the surface. After drying,
Further, it is preferable to heat at 120 to 200°C for about 2 hours. Heating makes the calcium fixation stronger.
以上の操作を経た、本発明に係る晶析処理用種
晶材においては、吸着させたリン酸及び固着させ
たカルシウム化合物は母材である担体の重量に対
して、その量がきわめて少なく、担体の表面を覆
うというよりは、むしろ、前記のように多数の活
性点として分布形成されるものであり、種晶材と
して好適な性質を示す。担体はその選択巾が広
く、天然又は人工の性状が均一で安価な担体を利
用でき、均一な処理を実施できるので、本発明の
結果物である種晶材は物理的、化学的に均一で安
定した処理性能を発揮する。また、担体の粒径、
粒度、比重、機械的強度などを任意に選択するこ
とによつて、種晶材を充填し、固定層としても流
動層としても採用できる。 In the seed crystal material for crystallization treatment according to the present invention that has undergone the above operations, the amount of the adsorbed phosphoric acid and the fixed calcium compound is extremely small relative to the weight of the carrier, which is the base material. Rather than covering the surface of the crystal, it is distributed as a large number of active points as described above, and exhibits properties suitable as a seed crystal material. There is a wide selection of carriers, natural or artificial carriers with uniform properties and low cost can be used, and uniform processing can be carried out. Therefore, the seed material resulting from the present invention is physically and chemically uniform. Demonstrates stable processing performance. In addition, the particle size of the carrier,
By arbitrarily selecting the particle size, specific gravity, mechanical strength, etc., the seed crystal material can be filled and used as either a fixed bed or a fluidized bed.
なお、本発明には属さない方法であるリン酸塩
とカルシウム塩が共存する溶液中に、担体を浸漬
する方法によつて、製造した種晶材は十分な処理
性能を発揮しない。この理由は明らかではない
が、本発明においては先づ第一段階として担体に
対して親和性のあるリン酸を吸着させたことが好
結果を生むと推定される。 Note that the seed crystal material produced by the method of immersing the carrier in a solution in which phosphate and calcium salt coexist, which is not a method of the present invention, does not exhibit sufficient treatment performance. Although the reason for this is not clear, it is presumed that in the present invention, adsorption of phosphoric acid with affinity to the carrier as a first step produces good results.
各種担体のリン酸に対する親和性を確認するた
めに、吸着実験を行つた。吸着等温線を第1図に
示す。第1図から水酸化ジルコニウム、酸化マグ
ネシウムのリン吸着量が大きく、次いで酸化アル
ミニウム、活性炭、砂の順にリン吸着量が低下す
ることが判る。 Adsorption experiments were conducted to confirm the affinity of various carriers for phosphoric acid. The adsorption isotherm is shown in Figure 1. It can be seen from FIG. 1 that the amount of phosphorus adsorbed by zirconium hydroxide and magnesium oxide is large, followed by aluminum oxide, activated carbon, and sand, and the amount of phosphorus adsorbed decreases in that order.
実施例 1 下記条件により、4種類の種晶材を調整した。Example 1 Four types of seed crystal materials were prepared according to the following conditions.
試料 A
粒径が0.3〜0.6mmの海水マグネシア・クリンカ
を(i)PH5に調整した0.5%のリン酸ナトリウム溶
液に20時間浸漬した後、(ii)乾燥し、120℃で3時
間加熱した。(iii)この吸着担体を1%の塩化カルシ
ウム溶液に20時間浸漬した後、(iv)乾燥し、120℃
で3時間加熱した。Sample A Seawater magnesia clinker with a particle size of 0.3 to 0.6 mm was (i) immersed in a 0.5% sodium phosphate solution adjusted to pH 5 for 20 hours, and (ii) dried and heated at 120°C for 3 hours. (iii) This adsorption carrier was immersed in a 1% calcium chloride solution for 20 hours, and (iv) dried at 120°C.
It was heated for 3 hours.
試料 B
前記試料Aにおける(iv)の乾燥、加熱処理を省略
した以外は試料Aと同一の方法で調整した。Sample B It was prepared in the same manner as Sample A except that the drying and heat treatment in (iv) in Sample A were omitted.
試料 C
前記試料Aにおける(ii)の乾燥、加熱処理を省略
した以外は試料Aと同一の方法で調整した。Sample C Prepared in the same manner as Sample A except that the drying and heat treatment in (ii) in Sample A were omitted.
試料 D
前記試料Aにおける(ii)及び(iv)の乾燥加熱処理を
省略した以外は試料Aと同一の方法で調整した。Sample D Prepared in the same manner as Sample A except that the drying and heating treatments (ii) and (iv) in Sample A were omitted.
これらの4種類の種晶材をそれぞれ充填したカ
ラムに、リン濃度約3.5mg/、カルシウム濃度
35〜45mg/、PH8.0〜8.5に調整した模擬下水を
SV=5h-1で通水し、リンの除去性能を調べた。
この結果を第2図に示す。いずれの種晶材も処理
水のリン濃度は0.7mg/以下の値を示し、長時
間の運転に対しても安定したリンの除去性能を示
した。試料Aの除去性能が良く、次いで試料B、
試料C、試Dの順に除去性能が若干低下した。 A column packed with each of these four types of seed crystal materials had a phosphorus concentration of approximately 3.5 mg/day and a calcium concentration of approximately 3.5 mg/day.
35~45mg/, simulated sewage adjusted to pH8.0~8.5
The phosphorus removal performance was examined by passing water at SV = 5h -1 .
The results are shown in FIG. The phosphorus concentration in the treated water for all seed crystal materials was less than 0.7 mg/d, demonstrating stable phosphorus removal performance even during long-term operation. Sample A had good removal performance, followed by sample B,
The removal performance decreased slightly in the order of sample C and sample D.
実施例 2
酸化ジルコニウムの水和物を担体として供試し
た以外は、実施例1の試料Aと同一の方法によつ
て、種晶材を調整した。この種晶材について実施
例1と同一の内容で通水実験をした結果、処理水
のリン濃度は、第2図に示した試料Aの場合と同
等の値を示した。Example 2 A seed crystal material was prepared in the same manner as in Sample A of Example 1, except that zirconium oxide hydrate was used as a carrier. A water flow experiment was carried out on this seed crystal material in the same manner as in Example 1, and as a result, the phosphorus concentration of the treated water showed a value equivalent to that of Sample A shown in FIG.
比較例
海水マグネシア・クリンカ(粒径0.3〜0.6mm)
を担体として、リン酸ナトリウム0.5%、塩化カ
ルシウム1.0%、PH8に調整した混合液に担体を
40時間浸漬して種晶材とした。この種晶材につい
て実施例1と同一の内容で通水実験をした結果、
処理水のリン濃度は運転当初は1.6mg/前後で
あり、運転時間の経過とともに漸減傾向を示した
が、1500時間経過後においても1.2mg/前後と
高い値を示した。Comparative example Seawater magnesia clinker (particle size 0.3-0.6mm)
Add the carrier to a mixed solution containing 0.5% sodium phosphate, 1.0% calcium chloride, and adjusted to pH 8.
It was soaked for 40 hours and used as a seed crystal material. As a result of conducting a water flow experiment on this seed crystal material in the same manner as in Example 1,
The phosphorus concentration in the treated water was around 1.6mg/at the beginning of operation, and showed a gradual decreasing trend as the operation time progressed, but even after 1500 hours, it remained high at around 1.2mg/.
第1図は各種担体のリン吸着等温線を示す図、
第2図は本発明に係る種晶材を充填したカラム
に、模擬下水を通水したときの運転結果を示す図
である。
Figure 1 is a diagram showing phosphorus adsorption isotherms of various carriers,
FIG. 2 is a diagram showing the operational results when simulated sewage water was passed through a column filled with the seed crystal material according to the present invention.
Claims (1)
酸を吸着させた後、塩化カルシウム、水酸化カル
シウム及び酸化カルシウムから選択されたカルシ
ウム化合物の少なくとも1種を担持させることを
特徴とする液中のリン酸を晶析する種晶材の製造
法。1. Phosphoric acid in a liquid is characterized by adsorbing phosphoric acid onto a magnesia-based or zirconia-based carrier, and then supporting at least one calcium compound selected from calcium chloride, calcium hydroxide, and calcium oxide. A method for producing seed crystal material for crystallization.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7988782A JPS58199090A (en) | 1982-05-14 | 1982-05-14 | Method for producing seed crystal material for crystallizing phosphoric acid in liquid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7988782A JPS58199090A (en) | 1982-05-14 | 1982-05-14 | Method for producing seed crystal material for crystallizing phosphoric acid in liquid |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58199090A JPS58199090A (en) | 1983-11-19 |
| JPS6130838B2 true JPS6130838B2 (en) | 1986-07-16 |
Family
ID=13702767
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7988782A Granted JPS58199090A (en) | 1982-05-14 | 1982-05-14 | Method for producing seed crystal material for crystallizing phosphoric acid in liquid |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58199090A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6331349U (en) * | 1986-08-14 | 1988-02-29 |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61204086A (en) * | 1985-03-08 | 1986-09-10 | Ataka Kogyo Kk | Crystallizing agent for phosphate ion in waste water and its preparation |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5617122B2 (en) * | 1972-12-18 | 1981-04-21 | ||
| JPS561152A (en) * | 1979-06-15 | 1981-01-08 | Q P Corp | High pressure continuous sterilizer |
| JPS5771693A (en) * | 1980-10-21 | 1982-05-04 | Katayama Chem Works Co Ltd | Method of removing phosphate ion contained in liquid |
-
1982
- 1982-05-14 JP JP7988782A patent/JPS58199090A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6331349U (en) * | 1986-08-14 | 1988-02-29 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58199090A (en) | 1983-11-19 |
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