JPS58199089A - Treatment of waste water containing fluorine together with surfactant - Google Patents

Treatment of waste water containing fluorine together with surfactant

Info

Publication number
JPS58199089A
JPS58199089A JP7988582A JP7988582A JPS58199089A JP S58199089 A JPS58199089 A JP S58199089A JP 7988582 A JP7988582 A JP 7988582A JP 7988582 A JP7988582 A JP 7988582A JP S58199089 A JPS58199089 A JP S58199089A
Authority
JP
Japan
Prior art keywords
water
tank
raw water
activated carbon
surfactant
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
JP7988582A
Other languages
Japanese (ja)
Inventor
Nobuko Sasaki
佐々木 信子
Ichiro Nakajima
一郎 中島
Terutaka Sawara
佐原 輝隆
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.)
Hitachi Plant Construction Co Ltd
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Construction Co Ltd
Hitachi Plant Technologies 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 Hitachi Plant Construction Co Ltd, Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Construction Co Ltd
Priority to JP7988582A priority Critical patent/JPS58199089A/en
Publication of JPS58199089A publication Critical patent/JPS58199089A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To improve removing efficiency while saving the amt. of the chemical to be added, by subjecting waste water to an adsorptive treatment of surfactant with activated carbon at specific pH then adding the chemical thereto and separating and removing fluorine as hardly soluble salt. CONSTITUTION:Raw water is introduced through a raw water introducing pipe 1 into a pH control tank 2, where the water is mixed with the acid or alkali fed through a feed port 3 and is controlled to >=3pH. The raw water is then introduced into an adsorptive treatment tank 4 using activated carbon. The surfactant contained in the raw water is adsorbed by the activated carbon in said tank and removed. The raw water after the adsorptive treatment is introduced into a pH adjusting tank 5, where the pH is properly controlled in the same way and the treated water is introduced into a flocculation tank 7. The water is thoroughly mixed with a calcium compd., a calcium compd. in combination with a phosphoric acid compd. or a metallic salt fed through a feed port 8 in the tank 7, whereafter, the mixed water is transferred into a settling tank 9 and the fluorine compd. is settled and separated.

Description

【発明の詳細な説明】 本発明は界面活性剤が共存するフッ素含有廃水の処理方
法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating fluorine-containing wastewater in which a surfactant coexists.

半導体工場、アルミニウムの電解精練工場、リン酸肥料
の製造工場等から排出される廃水中には。
In wastewater discharged from semiconductor factories, aluminum electrolytic smelting factories, phosphate fertilizer manufacturing factories, etc.

フッ素イオン及び界面活性剤が含まれている。従来、こ
のような廃水中のフッ素イオンを除去する方法としては
、廃水に水溶性カルシウム化合物。
Contains fluorine ions and surfactants. Conventionally, methods for removing fluoride ions from wastewater include adding water-soluble calcium compounds to the wastewater.

例えば水酸化カルシウム、塩化カルシウム等を添加し、
生成する難溶性フッ化カルシウムを沈殿分離する方法が
知られている。
For example, adding calcium hydroxide, calcium chloride, etc.
A method is known in which the poorly soluble calcium fluoride produced is separated by precipitation.

また、中性付近のpHでカルシウムイオンとリン酸イオ
ンを添加してリン酸ア・ξタイトとして沈殿分離する方
法、或いは金属塩を添加して金属とフッ素イオンの難溶
性塩として沈殿分離する方法化する0この対策として、
現存過剰のカルシウム化合物、リン酸カルシウム、金属
塩を添加しており、そのためコスト高になるという欠点
があった。
Alternatively, there is a method in which calcium ions and phosphate ions are added at a pH around neutrality to precipitate and separate as phosphate a-ξtite, or a method in which a metal salt is added to precipitate and separate as a sparingly soluble salt of metal and fluoride ions. As a countermeasure for this,
Existing excess calcium compounds, calcium phosphate, and metal salts are added, which has the disadvantage of increasing costs.

本発明の目的は、前記従来技術の欠点を解消し。The object of the present invention is to overcome the drawbacks of the prior art.

添加する薬品量を節約しながら、効率良くフッ素を除去
しうる廃水の処理方法を提供することにあり、  pH
3以上で活性炭により前処理することによって達成され
る。
Our objective is to provide a wastewater treatment method that can efficiently remove fluorine while reducing the amount of chemicals added.
This is achieved by pretreatment with activated carbon at 3 or more.

本発明による。界面活性剤が共存するフッ素含有廃水の
処理方法は、廃水をpH3以上に調整した後、活性炭で
吸着処理して廃水中の界面活性剤を除去し1次いで必要
に応じてpH調整を行なった後、水溶性カルシウム化合
物または水溶性カルシウム化合物と水溶性リン酸化合物
または金属塩を添加し、難溶性塩としてフッ素を分離除
去することを特徴とする。
According to the present invention. The method for treating fluorine-containing wastewater in which a surfactant coexists is to adjust the pH of the wastewater to 3 or higher, remove the surfactant from the wastewater by adsorption treatment with activated carbon, and then adjust the pH as necessary. , is characterized in that a water-soluble calcium compound or a water-soluble calcium compound and a water-soluble phosphoric acid compound or metal salt are added, and fluorine is separated and removed as a sparingly soluble salt.

対象廃水のpHが3以下である場合には、活性炭はフッ
素イオンを吸着し、界面活性剤の吸着量−6゜ 10に調整する。pHの調整には、塩酸や硫酸のような
鉱酸または水酸化ナトリウムや水酸化カルシウム等のア
ルカリ剤を使用することができる。
When the pH of the target wastewater is 3 or less, activated carbon adsorbs fluorine ions and adjusts the adsorption amount of surfactant to -6°10. To adjust the pH, a mineral acid such as hydrochloric acid or sulfuric acid or an alkaline agent such as sodium hydroxide or calcium hydroxide can be used.

こうして廃水をpH3以上で活性炭で吸着処理すると、
活性炭は界面活性剤を選択的に吸着するので、その後の
フッ素の沈殿除去は阻害されることなく、好適に行なわ
れる。
In this way, when wastewater is adsorbed with activated carbon at a pH of 3 or higher,
Since the activated carbon selectively adsorbs the surfactant, the subsequent precipitation and removal of fluorine is preferably carried out without being inhibited.

本発明に使用するカルシウム化合物としては。Calcium compounds used in the present invention include:

水酸化カルシウム、塩化カルシウム等、常用の水溶性カ
ルシウム化合物を使用することができ、またリン酸化合
物としては、オル) IJン酸またはその塩9例えばす
) IJウム塩等を使用することができる。カルシウム
化合物とリン酸化合物を使用する場合には、フッ素はフ
ルオロアパタイトとして沈殿除去される。
Commonly used water-soluble calcium compounds such as calcium hydroxide and calcium chloride can be used, and as phosphoric acid compounds, phosphoric acid or its salts, eg salts, etc. can be used. . When using calcium and phosphate compounds, fluorine is precipitated and removed as fluoroapatite.

金属塩としては、フッ素と難溶性の塩を形成しうる金属
塩2例えばアルミニウム塩゛、マグネシウム塩等を使用
することができる。
As the metal salt, a metal salt 2 that can form a poorly soluble salt with fluorine, such as an aluminum salt or a magnesium salt, can be used.

次に2図面に基づいて本発明を詳述する。Next, the present invention will be explained in detail based on two drawings.

原水を原水導入管1よりpH調整槽2へ導入し。Raw water is introduced into the pH adjustment tank 2 through the raw water introduction pipe 1.

注入口3より注入された酸またはアルカリと混合し、原
水をpH3以上に調整する。こうしてpHを調整した原
水を次に活性炭吸着処理装置4に導入する。ここで原水
中に含まれていた界面活性剤が活性炭により吸着除去さ
れる。次に、吸着処理された原水をpH調整槽5へ導入
し、注入口6から酸またはアルカリを添加して、pHを
適宜調整した後、凝集槽7へ導入する。凝集槽7内で、
注入口8から注入されたカルシウム化合物、カルシウム
化合物とリン酸化合物、または金属塩と充分混合した後
、沈殿槽9へ送入し、沈殿分離を行なう。
Mix with acid or alkali injected from injection port 3 to adjust raw water to pH 3 or higher. The raw water whose pH has been adjusted in this way is then introduced into the activated carbon adsorption treatment device 4. Here, the surfactant contained in the raw water is adsorbed and removed by activated carbon. Next, the raw water subjected to the adsorption treatment is introduced into the pH adjustment tank 5, and after adding acid or alkali through the inlet 6 to adjust the pH appropriately, the raw water is introduced into the aggregation tank 7. In the flocculation tank 7,
After thoroughly mixing with the calcium compound, calcium compound and phosphoric acid compound, or metal salt injected from the injection port 8, the mixture is fed into the precipitation tank 9 and subjected to precipitation separation.

このようにして9本発明によれば、界面活性剤の妨害を
受けることなく、効率良くフッ素を除去することができ
る。
In this manner, according to the present invention, fluorine can be efficiently removed without being interfered with by surfactants.

次に実施例に基づいて本発明を詳述するが1本発明はこ
れに限定されるものではない。
Next, the present invention will be described in detail based on Examples, but the present invention is not limited thereto.

実施例 瓢界面活性剤及びフッ素を含む廃水(F中3001′注
ソーダでpH5に調整し、活性炭層(内径5.0m、長
さ100cnのカラム)に5V=2で通水した結果、活
性炭処理水のF濃度は280〜7t。
Example: Waste water containing surfactant and fluorine (adjusted to pH 5 with 3001' soda in F, water passed through an activated carbon bed (column with inner diameter of 5.0 m and length of 100 cm) at 5 V = 2, resulting in activated carbon treatment. The F concentration of water is 280-7t.

TOCは150■/lであった。その後、カルシウム化
合物として塩化刃ルシウムを用いて凝集沈殿処理を行な
ったところ、処理水のF濃度を15■/を以下にするの
に、活性炭処理を行なわない従来法ではCQ/Fモル比
は2.5であったが5本発明方法では0072モル比は
1となり、塩化カルシウムの添加量は215に減するこ
とができる。
TOC was 150 μ/l. Afterwards, coagulation-sedimentation treatment was performed using lucium chloride as a calcium compound, and the F concentration in the treated water was reduced to 15/F or less, whereas in the conventional method without activated carbon treatment, the CQ/F molar ratio was 2. However, in the method of the present invention, the molar ratio of 0,072 becomes 1, and the amount of calcium chloride added can be reduced to 215.

【図面の簡単な説明】[Brief explanation of the drawing]

図面は本発明方法の一実施態様を示すフローシートであ
る。 符号の説明 2.5・・・pH調整槽 4・・・活性炭吸着処理装置 7・・・凝集槽 9・・・沈殿槽。
The drawing is a flow sheet showing one embodiment of the method of the present invention. Explanation of symbols 2.5...pH adjustment tank 4...Activated carbon adsorption treatment device 7...Coagulation tank 9...Settling tank.

Claims (1)

【特許請求の範囲】[Claims] fl)  界面活性剤が共存するフッ素含有廃水をPH
3以上に調整した後、活性炭で吸着処理し2次いで必要
に応じて再びpH調整を行なった後、水溶性カルシウム
化合物、水溶性カルシウム化゛合物と水溶性リン酸化合
物または金属塩を添加し、難溶性塩としてフッ素を分離
除去することを特徴とする界面活性剤が共存するフッ素
含有廃水の処理方法。
fl) PH of fluorine-containing wastewater in which surfactants coexist.
After adjusting the pH to 3 or higher, adsorption treatment is performed with activated carbon. After adjusting the pH again as necessary, a water-soluble calcium compound, a water-soluble calcium compound, and a water-soluble phosphoric acid compound or metal salt are added. A method for treating fluorine-containing wastewater in which a surfactant coexists, characterized by separating and removing fluorine as a sparingly soluble salt.
JP7988582A 1982-05-14 1982-05-14 Treatment of waste water containing fluorine together with surfactant Pending JPS58199089A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7988582A JPS58199089A (en) 1982-05-14 1982-05-14 Treatment of waste water containing fluorine together with surfactant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7988582A JPS58199089A (en) 1982-05-14 1982-05-14 Treatment of waste water containing fluorine together with surfactant

Publications (1)

Publication Number Publication Date
JPS58199089A true JPS58199089A (en) 1983-11-19

Family

ID=13702706

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7988582A Pending JPS58199089A (en) 1982-05-14 1982-05-14 Treatment of waste water containing fluorine together with surfactant

Country Status (1)

Country Link
JP (1) JPS58199089A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006272065A (en) * 2005-03-28 2006-10-12 Kurita Water Ind Ltd Treatment method and apparatus of fluorine-containing water containing toc component

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006272065A (en) * 2005-03-28 2006-10-12 Kurita Water Ind Ltd Treatment method and apparatus of fluorine-containing water containing toc component

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