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JPS598438B2 - Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou - Google Patents
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JPS598438B2 - Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou - Google Patents

Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou

Info

Publication number
JPS598438B2
JPS598438B2 JP14242575A JP14242575A JPS598438B2 JP S598438 B2 JPS598438 B2 JP S598438B2 JP 14242575 A JP14242575 A JP 14242575A JP 14242575 A JP14242575 A JP 14242575A JP S598438 B2 JPS598438 B2 JP S598438B2
Authority
JP
Japan
Prior art keywords
wastewater
ions
tank
phosphate
yuhaisui
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
JP14242575A
Other languages
Japanese (ja)
Other versions
JPS5267152A (en
Inventor
幸男 高橋
博幸 今村
忠弘 小早川
孝則 矢崎
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.)
Mitsui Toatsu Chemicals Inc
Original Assignee
Mitsui Toatsu Chemicals Inc
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 Mitsui Toatsu Chemicals Inc filed Critical Mitsui Toatsu Chemicals Inc
Priority to JP14242575A priority Critical patent/JPS598438B2/en
Publication of JPS5267152A publication Critical patent/JPS5267152A/en
Publication of JPS598438B2 publication Critical patent/JPS598438B2/en
Expired 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、弗素および燐酸イオンを含有する排水からこ
れらのイオンを連続的に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 continuously removing fluorine and phosphate ions from wastewater containing these ions.

燐鉱石を鉱酸で分解して湿式燐酸を製造する工場や、湿
式燐酸を原料として複合肥料やトリポリ燐酸ソーダのよ
うな燐酸化合物を製造する工場からは、燐酸イオンと共
に弗素イオンを含有する排水が多量に排出される。
Factories that produce wet phosphoric acid by decomposing phosphate rock with mineral acids, and factories that use wet phosphoric acid as a raw material to produce compound fertilizers and phosphate compounds such as sodium tripolyphosphate, produce wastewater that contains both phosphate ions and fluoride ions. Excreted in large quantities.

近年、工場排出物による環境汚染が問題となり、上記排
水中の弗素および燐酸イオンの除去が重要な課題となっ
ている。
In recent years, environmental pollution caused by factory waste has become a problem, and the removal of fluorine and phosphate ions from the wastewater has become an important issue.

燐酸イオンの排出が富栄養化物質の一つとして批難の対
象となっていることは、周知の通りであり、弗素につい
ては、昭和46年6月に公布された「排出基準を定める
総理府令」により、15pplI1以下とされ、特例と
して燐酸肥料製造業においては50ppII1以下とさ
れている。
It is well known that the emission of phosphate ions has been criticized as one of the eutrophication substances, and regarding fluorine, the ``Prime Minister's Office Ordinance Setting Emission Standards'' promulgated in June 1971. Accordingly, it is set at 15 pplI1 or less, and as a special exception, it is set at 50 pplI1 or less in the phosphate fertilizer manufacturing industry.

これらのイオンの除去手段としては、排水を反応性カル
シウム化合物で処理して不溶性のカルシウム化合物を生
成させ、これを分離する方法が知られているが、本発明
者らが種々の排水について検討した結果、排水中にアン
モニウムおよび/またはアルカリ金属イオンが含まれて
いる場合には、排水中の弗素および燐酸イオン、とくに
弗素イオンの除去が十分達成されないことがわかった。
As a means of removing these ions, a method is known in which wastewater is treated with a reactive calcium compound to generate an insoluble calcium compound and this is separated, but the present inventors have investigated various wastewater. As a result, it was found that when the wastewater contained ammonium and/or alkali metal ions, the removal of fluorine and phosphate ions, particularly fluorine ions, from the wastewater was not achieved sufficiently.

たとえば、P含有量約440咽およびF含有量約500
1)p[nと共にアンモニウムイオンおよびアルカリ金
属イオン(代表的な例としてナトリウム)をそれぞれ硫
酸塩として種々の割合で含む水を調製し、10%消石灰
スラリーでpH 7. 5となるまで中和した時の中和
後の炉液のPおよびFの濃度を第1表に示す。
For example, P content is about 440 and F content is about 500
1) Prepare water containing p[n as well as ammonium ions and alkali metal ions (typically sodium) in various proportions as sulfates, and adjust the water to pH 7.0 with 10% slaked lime slurry. Table 1 shows the concentrations of P and F in the furnace solution after neutralization when neutralized to 5.

これは1例に過ぎないが、PおよびFの除去がアンモニ
ウムおよびアルカリ金属イオンの存在によって妨害をう
けているこ吉が明らかである。
Although this is just one example, it is clear that the removal of P and F is hindered by the presence of ammonium and alkali metal ions.

湿式燐酸を使用する工業においてアンモニウムやアルカ
リ金属イオンを含有しない排水が排出される場合はほと
んどなく、このため本発明者らはこのような排水の処理
に苦慮していたが、種々検討した結果、排水をpH約4
〜5まで反応性カルシウム化合物で処理して沈澱固体を
生成せしめ、次に、該沈澱固体を存在せしめたまま、石
灰で処理してpHを約7以上とし、沈澱物を分離するこ
とによって、アンモニウムおよび/またはアルカリ金属
イオンの存在に拘りなく、処理排水中の弗素および燐酸
イオン(p)をそれぞれ20〜30ppl1lおよび1
0〜20ppIIlに低減せしめることができた。
In industries that use wet phosphoric acid, wastewater that does not contain ammonium or alkali metal ions is rarely discharged, and for this reason, the inventors had difficulty treating such wastewater, but after various studies, they found that: pH of wastewater is approximately 4
ammonium by treating with a reactive calcium compound to 5 to 5 to form a precipitated solid, then treating the precipitated solid with lime to bring the pH above about 7 and separating the precipitate. and/or regardless of the presence of alkali metal ions, fluorine and phosphate ions (p) in the treated wastewater should be reduced to 20-30 ppl 1 liter and 1 liter, respectively.
It was possible to reduce the amount to 0 to 20 ppII.

本発明は、このように少なくとも2段階で中和反応を行
なうものであるが、pH約4〜5までの第1段中和では
、弗素および燐酸イオンを含む酸性排水中で弗素および
燐酸イオンと反応して不溶性沈澱を生成する反応性カル
シウム化合物、たとえば生石灰、消石灰、炭酸カルシウ
ム、燐酸カルシウム等が使用される。
In the present invention, the neutralization reaction is carried out in at least two stages as described above, and in the first stage neutralization up to a pH of approximately 4 to 5, fluorine and phosphate ions are reacted in acidic wastewater containing fluorine and phosphate ions. Reactive calcium compounds that react to form insoluble precipitates are used, such as quicklime, slaked lime, calcium carbonate, calcium phosphate, and the like.

第2段中和で使用される石灰は生石灰または消石灰であ
る。
The lime used in the second stage neutralization is quicklime or slaked lime.

したがって、第1段中和および第2段中和共に生石灰ま
たは消石灰を使用することがありうるが、本発明におい
てはpH約4−5までの段階において第1段反応を完結
させ、その間に生成した沈澱固体を分離せず、存在せし
めたまま、第2段の中和反応を行なうことが絶対に必要
である。
Therefore, quicklime or slaked lime may be used in both the first and second stage neutralization, but in the present invention, the first stage reaction is completed at a pH of about 4-5, and the It is absolutely necessary to carry out the second stage neutralization reaction while the precipitated solid remains present without being separated.

第1段反応で生成した沈澱固体をその段階で炉別し、そ
のp液について第2段中和を行なったのでは、燐酸イオ
ン(p)の濃度を40〜soppm以下に低下させるこ
とができない。
If the precipitated solid produced in the first stage reaction is separated in the furnace at that stage and the p liquid is neutralized in the second stage, it is not possible to reduce the concentration of phosphate ions (p) to below 40 to soppm. .

これは、虫゜石灰または消石灰を使用して、1段でpH
約7.5となるまで中和する場合に、弗素イオンの濃度
を50〜100ppIl1以下に低下させることができ
ないのと対照的である。
This method uses insect lime or slaked lime to adjust the pH in one step.
This is in contrast to the inability to reduce the concentration of fluoride ions below 50-100 ppIl1 when neutralizing to about 7.5.

酸性排水の中和反応を少なくとも2段階で行なう本発明
の方法は、それぞれに撹拌機を備えた反応槽を2槽以上
直列に接続し、各槽の中和段階を変え、一約4〜5の段
階で、1旦中和反応を完結する工程を経由する方法によ
って好都合に行なわれる。
The method of the present invention, in which the neutralization reaction of acidic wastewater is carried out in at least two stages, consists of connecting two or more reaction tanks in series, each equipped with a stirrer, and changing the neutralization stage in each tank. This is conveniently carried out by a method that involves a step of once completing the neutralization reaction.

pH4〜5までの中和は1工程あるいは2以上の工程で
行なわれ、また、最終的にpHが約7以上となるまで中
和後、シツクナー等で濃厚化された沈澱物スラリーの1
部を循環使用することによって行なわれてもよい。
Neutralization to pH 4 to 5 is carried out in one step or in two or more steps, and after neutralization until the final pH reaches about 7, 1 of the precipitate slurry thickened with a thickener etc.
This may be done by cyclically using parts.

以下に、本発明の実施例を示す。Examples of the present invention are shown below.

実施例 I P0.09%(以下濃度はすべて重量基準)、FO,0
5%、Na20 0.05%およびNH30.02%を
含む酸性排水を、撹拌装置を有する2基直列の中和槽へ
3.25ll分の割合で導き、第1槽でpH40、第2
槽でpH 7. 2となるように各槽へ10%消石灰ス
ラリーを添加した。
Example I P0.09% (all concentrations below are based on weight), FO, 0
Acidic wastewater containing 5% Na20, 0.05% Na20, and 30.02% NH was introduced at a rate of 3.25 liters into two neutralization tanks equipped with a stirring device in series, with pH 40 in the first tank and pH 40 in the second tank.
pH 7. A 10% slaked lime slurry was added to each tank so that the amount was 2.

処理排液(P液)のP濃度は16p^ F濃度は25p
pmであった。
The P concentration of the treated effluent (P solution) is 16 p^, the F concentration is 25 p
It was pm.

参考までに、第1槽出口で沈澱物を戸別し、炉液につい
てpH 7. 5まで中和した場合はp65ppm,F
23pFであり、また、第1槽のみに消石灰スラリーを
添加して1段でpH 7.5まで中和した場合はP 1
6pIn, F8 0pl)Inであった。
For reference, the precipitate was collected at the outlet of the first tank, and the pH of the furnace liquid was 7. If neutralized to 5, p65ppm, F
23 pF, and if slaked lime slurry was added only to the first tank and neutralized to pH 7.5 in one stage, P 1
6pIn, F8 0pl)In.

実施例 2 実施例1において、第2槽出口スラリーをシツクナーに
導き、スラリー濃度18%の濃厚化された沈澱物スラリ
ーを回収し、爾後の操作では濃厚化スラリーの一部を第
1槽へ循環して中和に使用した。
Example 2 In Example 1, the slurry at the outlet of the second tank was led to a thickener to recover a thickened sediment slurry with a slurry concentration of 18%, and in subsequent operations, part of the thickened slurry was circulated to the first tank. and used for neutralization.

(濃厚化スラリーの残部はフィルターへ送った。(The remainder of the thickened slurry was sent to a filter.

)処理排水のP濃度は、19ppm,F濃度は、28p
pmであった。
) The P concentration of treated wastewater is 19 ppm, the F concentration is 28 ppm.
It was pm.

実施例 3 実施例1において、第1槽では消石灰スラIJ一の代り
に10%炭酸カルシウムスラリーを使用してpH4.2
となるように処理をした。
Example 3 In Example 1, 10% calcium carbonate slurry was used instead of slaked lime slurry IJ in the first tank, and the pH was adjusted to 4.2.
I processed it so that

処理排水のP濃度は、18p鳳F濃度は26I1f)[
11であった。
The P concentration of the treated wastewater is 18p; the F concentration is 26I1f) [
It was 11.

実施例 4 P0.1%、F0.055%、Na200.04%およ
びNH30. 0 1 5%を含む酸性排水を、撹拌装
置を有する3基直列の中和槽へ3.25ll分の割合で
導き、第1槽でpH3.6、第2槽でpH4.5、第3
槽でpi−i 7. 5となるように各槽へ10%消石
灰スラリーを添加した。
Example 4 P0.1%, F0.055%, Na200.04% and NH30. Acidic wastewater containing 0.15% is introduced at a rate of 3.25 liters into three neutralization tanks equipped with a stirring device in series, pH 3.6 in the first tank, pH 4.5 in the second tank, pH 4.5 in the third tank, and pH 4.5 in the second tank.
Pi-i in the tank 7. A 10% slaked lime slurry was added to each tank so that the amount was 5%.

処理排水(P液)のP濃度は12pInn,F濃度は2
2ppII1であった。
The P concentration of the treated wastewater (P liquid) is 12 pInn, and the F concentration is 2.
It was 2ppII1.

Claims (1)

【特許請求の範囲】[Claims] 1 アンモニウムおよび/またはアルカリ金属イオンと
共に弗素および燐酸イオンを含有する酸性排水を連続的
に処理する際、該排水をpH約4〜5まで生石灰、消石
灰、炭酸カルシウム、および燐酸カルシウムからなる群
より選択される反応性カルシウム化合物で処理し沈澱固
体を生成せしめ、次に、該沈澱固体を存在せしめたまま
石灰で処理してpHを約7以上とし、沈澱物を分離する
ことを特徴とする弗素および燐酸イオン含有排水の連続
処理方法。
1. When continuously treating acidic wastewater containing fluorine and phosphate ions together with ammonium and/or alkali metal ions, the wastewater is brought to a pH of about 4 to 5 by a method selected from the group consisting of quicklime, slaked lime, calcium carbonate, and calcium phosphate. a reactive calcium compound to form a precipitated solid, and then treated with lime while the precipitated solid is present to bring the pH to about 7 or higher and to separate the precipitate. Continuous treatment method for wastewater containing phosphate ions.
JP14242575A 1975-12-02 1975-12-02 Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou Expired JPS598438B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14242575A JPS598438B2 (en) 1975-12-02 1975-12-02 Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14242575A JPS598438B2 (en) 1975-12-02 1975-12-02 Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou

Publications (2)

Publication Number Publication Date
JPS5267152A JPS5267152A (en) 1977-06-03
JPS598438B2 true JPS598438B2 (en) 1984-02-24

Family

ID=15315016

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14242575A Expired JPS598438B2 (en) 1975-12-02 1975-12-02 Futsuso Oyobi Rinsan Iongan Yuhaisui no Renzokushiyorihohou

Country Status (1)

Country Link
JP (1) JPS598438B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002035766A (en) * 2000-07-21 2002-02-05 Japan Organo Co Ltd Method for removing fluorine and phosphorus in wastewater
JP2006218354A (en) * 2005-02-08 2006-08-24 Kurita Water Ind Ltd Treatment method for fluorine-containing wastewater

Also Published As

Publication number Publication date
JPS5267152A (en) 1977-06-03

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