JPS6130639B2 - - Google Patents
Info
- Publication number
- JPS6130639B2 JPS6130639B2 JP7989082A JP7989082A JPS6130639B2 JP S6130639 B2 JPS6130639 B2 JP S6130639B2 JP 7989082 A JP7989082 A JP 7989082A JP 7989082 A JP7989082 A JP 7989082A JP S6130639 B2 JPS6130639 B2 JP S6130639B2
- Authority
- JP
- Japan
- Prior art keywords
- calcium
- carrier
- seed crystal
- crystal material
- phosphorus
- 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
Links
- 239000000463 material Substances 0.000 claims description 24
- 239000013078 crystal Substances 0.000 claims description 22
- 229940043430 calcium compound Drugs 0.000 claims description 21
- 150000001674 calcium compounds Chemical class 0.000 claims description 21
- 239000011574 phosphorus Substances 0.000 claims description 17
- 229910052698 phosphorus Inorganic materials 0.000 claims description 17
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 16
- 239000007788 liquid Substances 0.000 claims description 11
- 238000000034 method Methods 0.000 claims description 11
- 238000004519 manufacturing process Methods 0.000 claims description 7
- 238000010438 heat treatment Methods 0.000 claims description 6
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims description 5
- 239000001110 calcium chloride Substances 0.000 claims description 4
- 229910001628 calcium chloride Inorganic materials 0.000 claims description 4
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 4
- 239000000292 calcium oxide Substances 0.000 claims description 3
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 claims description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 2
- 239000000920 calcium hydroxide Substances 0.000 claims description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 2
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 2
- 150000002681 magnesium compounds Chemical class 0.000 claims description 2
- 150000003755 zirconium compounds Chemical class 0.000 claims description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 13
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 9
- 229910019142 PO4 Inorganic materials 0.000 description 7
- 238000002425 crystallisation Methods 0.000 description 7
- 230000008025 crystallization Effects 0.000 description 7
- 235000021317 phosphate Nutrition 0.000 description 7
- 239000002367 phosphate rock Substances 0.000 description 7
- 239000000969 carrier Substances 0.000 description 6
- 239000000395 magnesium oxide Substances 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 4
- 150000003018 phosphorus compounds Chemical class 0.000 description 4
- 239000001506 calcium phosphate Substances 0.000 description 3
- 229910000389 calcium phosphate Inorganic materials 0.000 description 3
- 235000011010 calcium phosphates Nutrition 0.000 description 3
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 3
- 239000010452 phosphate Substances 0.000 description 3
- 239000013535 sea water Substances 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- QORWJWZARLRLPR-UHFFFAOYSA-H tricalcium bis(phosphate) Chemical group [Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O QORWJWZARLRLPR-UHFFFAOYSA-H 0.000 description 3
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 229910001424 calcium ion Inorganic materials 0.000 description 2
- 235000012255 calcium oxide Nutrition 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000008187 granular material Substances 0.000 description 2
- -1 phosphorus compound Chemical class 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- IVORCBKUUYGUOL-UHFFFAOYSA-N 1-ethynyl-2,4-dimethoxybenzene Chemical compound COC1=CC=C(C#C)C(OC)=C1 IVORCBKUUYGUOL-UHFFFAOYSA-N 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 108010082455 Sebelipase alfa Proteins 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000000151 deposition Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- WMWXXXSCZVGQAR-UHFFFAOYSA-N dialuminum;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3] WMWXXXSCZVGQAR-UHFFFAOYSA-N 0.000 description 1
- 238000004134 energy conservation Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 229910052588 hydroxylapatite Inorganic materials 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000002198 insoluble material Substances 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
- 229940041615 kanuma Drugs 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 description 1
- 239000000347 magnesium hydroxide Substances 0.000 description 1
- 229910001862 magnesium hydroxide Inorganic materials 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- GGROONUBGIWGGS-UHFFFAOYSA-N oxygen(2-);zirconium(4+);hydrate Chemical compound O.[O-2].[O-2].[Zr+4] GGROONUBGIWGGS-UHFFFAOYSA-N 0.000 description 1
- XYJRXVWERLGGKC-UHFFFAOYSA-D pentacalcium;hydroxide;triphosphate Chemical compound [OH-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O XYJRXVWERLGGKC-UHFFFAOYSA-D 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Removal Of Specific Substances (AREA)
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
用種晶材料の製造法に係り、特に下水等の用廃水
中に含まれるリン化合物を効率よく晶析させるた
めに好適な晶析材料の製造法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing a seed crystal material for crystallization treatment for crystallizing and separating a phosphorus compound dissolved in a liquid, and particularly for use in sewage water. The present invention relates to a method for producing a crystallization material suitable for efficiently crystallizing phosphorus compounds contained in industrial wastewater.
自然水係に排出される各種廃水中には、無機性
のオルトリン酸塩、種々の縮合リン酸塩、有機性
リン酸塩などのリン化合物がいろいろの形態で含
まれており、これらのリン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 types of wastewater discharged to natural water systems contain phosphorus compounds in various forms such as inorganic orthophosphates, various condensed phosphates, and organic phosphates. The existence of rivers,
It is a major cause of eutrophication in closed water bodies such as lakes and inner bays.
これらの液中に溶解して存在するリン化合物の
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。 A crystallization treatment method is one of the methods for removing phosphorus compounds dissolved in these liquids. 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. It is basically based on precipitation. 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定でかつ処理性能が安
定した液中のリンの晶析処理用種晶材料の製造法
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 prior art and to provide a method for producing a seed crystal material for crystallizing phosphorus in a liquid that is stable and has stable processing performance in place 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
料の製造法は、担体に塩化カルシウム、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種を付着させた後、
120〜200℃で加熱し、前記担体にカルシウム化合
物を固着させることを特徴とする。 In order to achieve this objective, the method for producing a seed crystal material according to the present invention includes depositing at least one calcium compound selected from calcium chloride, calcium hydroxide, and calcium oxide on a carrier, and then
It is characterized by heating at 120 to 200°C to fix the calcium compound on the carrier.
ここに、担体とは種晶材料の母体となる粒状体
(球状及び破砕状のもの)を意味し、特に、マグ
ネシウム系化合物、アルミニウム系化合物、ジル
コニウム系化合物のうち、水に不溶性のものが選
択される。これらに該当するものとしては、例え
ば海水マグネシア・クリンカ、電融マグネシウ・
クリンカ、活性アルミナ、鹿沼土、ジルコニア、
水酸化マグネシウムなどが挙げられる。すなわ
ち、これらの化合物はリン酸塩との親和性が強
く、これらを担体とした種晶材料を、液中のリン
酸塩の晶析用として用いるときは、液中のリン酸
塩との親和性がよいため、後述の固着させたカル
シウム化合物及び液中に共存するカルシウムイオ
ンと相乗して、担体表面にリン酸カルシウムを効
率よく晶析する。第1図に各種担体のリン酸に関
する吸着等温線を示す。第1図から、本発明に系
る酸化マグネシウム、酸化アルミニウム、水酸化
ジルコニウムのリン吸着量が大きく、これらの担
体がリン酸塩と親和性が強いことが判る。 Here, the term "carrier" refers to a granular material (spherical or crushed) that becomes the base of the seed crystal material, and in particular, a water-insoluble material is selected from among magnesium compounds, aluminum compounds, and zirconium compounds. be done. For example, seawater magnesia/clinker, fused magnesia/clinker, etc.
Clinker, activated alumina, Kanuma soil, zirconia,
Examples include magnesium hydroxide. In other words, these compounds have a strong affinity with phosphates, and when seed crystal materials containing these compounds as carriers are used for crystallizing phosphates in a liquid, it is necessary to Because of its good properties, calcium phosphate is efficiently crystallized on the surface of the carrier by synergistically with the fixed calcium compound described below and calcium ions coexisting in the liquid. Figure 1 shows adsorption isotherms for phosphoric acid on various carriers. From FIG. 1, it can be seen that the amount of phosphorus adsorbed by magnesium oxide, aluminum oxide, and zirconium hydroxide according to the present invention is large, and these carriers have a strong affinity for phosphate.
担体にカルシウム化合物を付着させる方法とし
ては、カルシウム化合物の水溶液に担体を浸漬す
る方法が好ましく用いられる。例えば、0.01〜10
%のカルシウム化合物溶液に10〜100時間浸漬す
る。この処理はなるべく低い濃度のカルシウム化
合物溶液に、なるべく長時間浸漬することによつ
て、担体に対するカルシウム化合物の付着がより
十分となる。付着させるカルシウム化合物の量
は、担体1g当たり2〜50mgが好ましい。すなわ
ち、付着量が少なすぎると種晶材料としての活性
が低下し、多すぎると付着したカルシウム化合物
が担体の表面を覆うことになり、担体のリン化合
物に対する親和性を十分に活かすことができず種
晶材料としての活性が同様に低下する。前記の担
体へのカルシウム化合物の付着処理だけでは、こ
れを液中のリンの晶析処理用として用いたとき、
カルシウム化合物が液中に容易に溶解、離脱し、
種晶材料として不適である。このため、次にカル
シウム化合物の固着処理を行う。すなわち前記浸
漬によつてカルシウム化合物を付着させた担体を
乾燥後加熱する。乾燥は天日乾燥でもよいが、温
度80〜110℃下での強制乾燥より好ましい。加熱
は120〜200℃で2時間程度行う。加熱温度が120
℃未満ではカルシウム化合物の固着が不十分とな
る。200℃を越えて加熱しても、前記120〜200℃
で加熱した場合と同程度の晶析処理性能しか示さ
ない。したがつて、200℃を越える加熱処理は省
エネルギー上不利である。 As a method for attaching the calcium compound to the carrier, a method of immersing the carrier in an aqueous solution of the calcium compound is preferably used. For example, 0.01 to 10
% calcium compound solution for 10-100 hours. In this treatment, by immersing the carrier in a calcium compound solution with a concentration as low as possible for as long as possible, adhesion of the calcium compound to the carrier becomes more sufficient. The amount of calcium compound deposited is preferably 2 to 50 mg per gram of carrier. In other words, if the amount attached is too small, the activity as a seed crystal material will decrease, and if it is too large, the attached calcium compound will cover the surface of the carrier, making it impossible to fully utilize the affinity of the carrier for phosphorus compounds. The activity as seed material is similarly reduced. If the above-mentioned treatment for adhering calcium compounds to the carrier is not enough, when this is used for the crystallization treatment of phosphorus in the liquid,
Calcium compounds easily dissolve and leave the liquid,
Not suitable as seed crystal material. For this reason, a calcium compound fixing treatment is next performed. That is, the carrier to which the calcium compound is attached by the immersion is dried and then heated. Drying may be carried out in the sun, but forced drying at a temperature of 80 to 110°C is preferable. Heating is performed at 120 to 200°C for about 2 hours. Heating temperature is 120
If the temperature is less than 0.degree. C., the fixation of calcium compounds will be insufficient. Even if heated above 200℃, the above 120~200℃
It shows only the same crystallization treatment performance as when heated at . Therefore, heat treatment at temperatures exceeding 200°C is disadvantageous in terms of energy conservation.
カルシウム化合物を固着させる他の方法とし
て、カルシウム化合物の微粉末を担体と十分に混
合し加熱するようにしてもよい。 Another method for fixing the calcium compound may be to thoroughly mix a fine powder of the calcium compound with a carrier and heat the mixture.
上記のようにカルシウム化合物を固着させた担
体は液中のリンの晶析処理用の種晶材料として好
適な性質を示す。 The carrier on which the calcium compound is fixed as described above exhibits properties suitable as a seed crystal material for crystallizing phosphorus in a liquid.
すなわち、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
一なカルシウム化合物の固着処理を実施できるの
で、本発明の結果物である種晶材料は物理的、化
学的に均一で、安定した処理性能を発揮する。ま
た、但体の粒径、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、種晶材料を充填
し、固定層としても流動層として採用できる。 In other words, the seed crystal material resulting from the present invention has a wide selection of carriers, has uniform natural or artificial properties, can be used at low cost, and can uniformly fix calcium compounds. It is chemically uniform and exhibits stable processing performance. Further, by arbitrarily selecting the particle size, particle size, specific gravity, mechanical strength, etc. of the body, it can be filled with seed crystal material and used as a fixed bed or a fluidized bed.
実施例 1
粒径が0.3〜0.6mmの海水マグネシア・クリンカ
を0.1%の塩化カルシウム水溶液に30時間浸漬し
た。次に、この浸漬した担体を、水切り、乾燥
後、恒温槽中で120℃で2時間加熱して種晶材料
とした。この種晶材料を充填したカラムに、リン
濃度約3.0mg/、カルシウム濃度35〜45mg/
、PH8.0〜8.5に調整した下水二次処理水の模擬
水をSV=4h-1で通水し、リンの除去性能を調査
した。この結果、処理水のリン濃度は0.3mg/
前後であり、長時間の運転によつてもリンの除去
性能は安定していた。Example 1 Seawater magnesia clinker having a particle size of 0.3 to 0.6 mm was immersed in a 0.1% calcium chloride aqueous solution for 30 hours. Next, this immersed carrier was drained, dried, and heated in a constant temperature bath at 120° C. for 2 hours to obtain a seed crystal material. A column filled with this seed crystal material has a phosphorus concentration of approximately 3.0 mg/, a calcium concentration of 35 to 45 mg/
The phosphorus removal performance was investigated by passing simulated secondary treated sewage water adjusted to pH 8.0 to 8.5 at SV = 4 h -1 . As a result, the phosphorus concentration in the treated water was 0.3mg/
The phosphorus removal performance was stable even after long-term operation.
実施例 2
酸化アルミニウムの水和物を担体として供試し
た以外は、実施例1と同一の条件で種晶材料を製
造し、同一の条件で通水実験した。この結果、処
理水のリン濃度は、継続的搭に0.4mg/前後の
値を示した。Example 2 A seed crystal material was produced under the same conditions as in Example 1, except that aluminum oxide hydrate was used as a carrier, and a water flow experiment was conducted under the same conditions. As a result, the phosphorus concentration in the treated water showed a value of around 0.4mg/continuously.
実施例 3
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と同一の条件で種晶材料を製
造し、同一の条件で通水実験した。この結果、処
理水のリン濃度は、継続的に0.3mg/前後の値
を示した。Example 3 A seed crystal material was produced under the same conditions as in Example 1, except that zirconium oxide hydrate was used as a carrier, and a water flow experiment was conducted under the same conditions. As a result, the phosphorus concentration in the treated water continuously showed a value of around 0.3mg/.
実施例 4
海水マグネシア・クリンカの粒状物(粒径0.3
〜0.6mm)を担体として、この担体に生石灰の微
粉末(粒径30〜80μm)を、担体の乾重量に対し
て5%の割合で混合し、180℃で2時間加熱して
種晶材料とした。この種晶材料について、実施例
1と同一の条件で通水実験した結果、運転当初は
処理水のリン濃度が1.2mg/前後と高い値を示
したが、72時間運転後には、処理水のリン濃度は
0.5mg/前後となり、以降安定したリンの除去
性能を示した。Example 4 Seawater magnesia clinker granules (particle size 0.3
~0.6mm) as a carrier, mix quicklime fine powder (particle size 30-80μm) at a ratio of 5% based on the dry weight of the carrier, and heat it at 180℃ for 2 hours to obtain seed crystal material. And so. As a result of a water flow experiment using this seed crystal material under the same conditions as in Example 1, the phosphorus concentration in the treated water showed a high value of around 1.2 mg/kg at the beginning of operation, but after 72 hours of operation, The phosphorus concentration is
The amount was around 0.5mg/, and stable phosphorus removal performance was shown thereafter.
比較例
川砂及び活性炭を担体として供試した以外は、
実施例1と同様の条件で種晶材料を製造し、同一
の条件で通水実験した。この結果、処理水のリン
濃度は1.6mg/前後であり、1500時間の運転に
よつても、この値は変化しなかつた。Comparative Example Except for using river sand and activated carbon as carriers,
A seed crystal material was produced under the same conditions as in Example 1, and a water flow experiment was conducted under the same conditions. As a result, the phosphorus concentration in the treated water was around 1.6 mg/d, and this value did not change even after 1500 hours of operation.
第1図は各種担体のリン吸着等温線を示す図で
ある。
FIG. 1 is a diagram showing phosphorus adsorption isotherms of various carriers.
Claims (1)
ム化合物及びジルコニウム化合物から選ばれた粒
状の担体に塩化カルシウム、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種を付着させた後、120〜200℃
で加熱し、前記担体にカルシウム化合物を固着さ
せることを特徴とする液中のリンの晶析処理用種
晶材料の製造法。 2 前記担体を塩化カルシウム溶液中に浸漬し、
加熱して担体に塩化カルシウムを固着させる特許
請求の範囲第1項記載の種晶材料の製造法。[Claims] 1. At least one calcium compound selected from calcium chloride, calcium hydroxide, and calcium oxide is attached to a granular carrier selected from water-insoluble magnesium compounds, aluminum compounds, and zirconium compounds. After, 120~200℃
1. A method for producing a seed crystal material for crystallizing phosphorus in a liquid, the method comprising heating the seed crystal material to fix the calcium compound to the carrier. 2 immersing the carrier in a calcium chloride solution,
2. The method for producing a seed crystal material according to claim 1, wherein calcium chloride is fixed to the carrier by heating.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7989082A JPS58199091A (en) | 1982-05-14 | 1982-05-14 | Production of seed crystal material for crystallization treatment of phosphate in liquid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7989082A JPS58199091A (en) | 1982-05-14 | 1982-05-14 | Production of seed crystal material for crystallization treatment of phosphate in liquid |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58199091A JPS58199091A (en) | 1983-11-19 |
| JPS6130639B2 true JPS6130639B2 (en) | 1986-07-15 |
Family
ID=13702855
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7989082A Granted JPS58199091A (en) | 1982-05-14 | 1982-05-14 | Production of seed crystal material for crystallization treatment of phosphate in liquid |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58199091A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102428038B (en) * | 2009-05-21 | 2015-12-02 | 大金工业株式会社 | Treatment agent and manufacture method thereof and treatment process |
| CN120040173B (en) * | 2025-01-16 | 2025-11-11 | 东莞金太阳研磨股份有限公司 | A novel ceramic abrasive and its dry sandpaper preparation method |
-
1982
- 1982-05-14 JP JP7989082A patent/JPS58199091A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58199091A (en) | 1983-11-19 |
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