TW201223881A - Method for treating fluorine-containing water - Google Patents

Method for treating fluorine-containing water Download PDF

Info

Publication number
TW201223881A
TW201223881A TW100124977A TW100124977A TW201223881A TW 201223881 A TW201223881 A TW 201223881A TW 100124977 A TW100124977 A TW 100124977A TW 100124977 A TW100124977 A TW 100124977A TW 201223881 A TW201223881 A TW 201223881A
Authority
TW
Taiwan
Prior art keywords
fluorine
water
calcium carbonate
reaction
containing water
Prior art date
Application number
TW100124977A
Other languages
Chinese (zh)
Other versions
TWI568682B (en
Inventor
Shin Sato
Shuhei Izawa
Original Assignee
Kurita Water Ind 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 Kurita Water Ind Ltd filed Critical Kurita Water Ind Ltd
Publication of TW201223881A publication Critical patent/TW201223881A/en
Application granted granted Critical
Publication of TWI568682B publication Critical patent/TWI568682B/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • C02F2101/14Fluorine or fluorine-containing compounds
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

Calcium carbonate particles having a small particle diameter and having excellent reactivity and flowability are used and fluorine-containing water is passed upward through a reaction tower by a once-through operation to thereby effectively remove and recover the fluorine. Disclosed is a method for treating fluorine-containing water which comprises passing the fluorine-containing water upward from a lower part of a reaction tower (1), converting the fluorine contained in the fluorine-containing water into calcium fluoride through reaction with calcium carbonate particles present in the reaction tower (1), thereby removing the fluorine, and taking out the treated water from which the fluorine has been removed, from an upper part of the reaction tower (1), wherein calcium carbonate particles are introduced from an upper part of the reaction tower (1) into the reaction tower (1); through which the fluorine-containing water is being passed. Thus, use is made of not a method in which the fluorine-containing water is passed after calcium carbonate particles having a small particle diameter are packed into the reaction tower (1) to form a packing layer but a method in which calcium carbonate particles having a small particle diameter are introduced from above the reaction tower (1) when the fluorine-containing water is being passed upward through the reaction tower (1). As a result, the calcium carbonate particles can be efficiently reacted with the fluorine contained in the fluorine-containing water.

Description

201223881 六、發明說明: 【發明所屬之技術領域】 本發明係有關含氟之水的處理方法,更詳而言係對反 應塔向上流通入含氟之水,使其在反應塔內與碳酸鈣粒子 接觸點,而可以有效率地將氟做爲氟化鈣除去予以回收之 方法。 【先前技術】 在半導體製造領域或相關領域、太陽電池製造領域、 各種金屬材料、單結晶材料、光學系材料等表面處理領域 中,會有含氟之廢水被掛出。 以往,處理含氟之水的方法係通常提案將含氟之水灌 入碳酸鈣塡充塔,使氟轉換成結晶性佳之氟化鈣予以除去 ,回收之方法。又,此等方法中習知者有直列地連結2塔 以上的碳酸鈣塡充塔,依序將含氟之水通入第一塔內之碳 酸鈣可以使其與含氟之水中的氟反應,而完全成爲氟化鈣 爲止,當第一塔內之碳酸鈣可完全成爲氟化鈣時,抽出第 —塔內之氟化鈣後再塡充新的碳酸鈣,以此塔做爲最後之 塔予以設置通水,以所謂隨輪轉動方式處理含氟之水,予 以回收高純度之氟化鈣的方法係爲人所知者(例如專利文 獻1〜3 )。 以往這種處理含氟之水所用碳酸鈣塡充塔中所塡充之 碳酸鈣粒子係粒徑過度小的碳酸鈣粒子係會溶解於含氟之 水中而無法充分地供予反應,所以通常係使用粒徑爲 -5- 201223881 Ο . 3 mm左右者。 〔先前技術文獻〕 〔專利文獻〕 專利文獻1 :特開平6-2545 7 1號公報 專利文獻2 :特開平7- 1 36667號公報 專利文獻3 :特開平5-253578號公報 【發明內容】 〔發明欲解決之課題〕 惟粒徑0.3mm程度之碳酸鈣粒子係有以下(1 ) 、(2 )缺點。 (1)由於粒子較大所以很難在塡充塔內流動,爲此 極易固黏於塔內。 (2 )與粒子較小者相比,其比表面積小,與氟之反 應速度慢。 爲解決此等問題,以往係在塡充塔內通入向上方流之 含氟之水,將一部份自塔上部取出之處理水循環於塔下部 成爲一種循環方式以提高塔內線速度,使塔內之碳酸鈣粒 子可以流動防止其固黏,又,經由循環通水使其可以充分 地進行反應。惟此循環通水方式必須爲使其循環要有動力 ,爲循環通水其反應塔容積必須較大,工業上不利。 針對此’只要爲粒徑0.05 mm以下之小粒徑碳酸鈣粒子 時,流動性高,很難固黏,又由於比表面積大,所以與氟 之反應速度亦較快,所以不必以循環方式,以一過式即可201223881 VI. Description of the Invention: [Technical Field of the Invention] The present invention relates to a method for treating water containing fluorine, and more specifically, the reaction tower is circulated upward into the water containing fluorine to make it in the reaction tower with calcium carbonate. Particle contact points, and fluorine can be efficiently removed as a method of removing calcium fluoride. [Prior Art] Fluoride-containing wastewater is hanged in the field of semiconductor manufacturing or related fields, solar cell manufacturing, various metal materials, single crystal materials, and optical materials. Conventionally, a method of treating fluorine-containing water has been generally proposed in which fluorine-containing water is poured into a calcium carbonate crucible column, and fluorine is converted into calcium fluoride having good crystallinity to be removed and recovered. Further, in these methods, a calcium carbonate ruthenium tower in which two or more columns are connected in series, and calcium fluoride which is introduced into the first column in sequence can be reacted with fluorine in the fluorine-containing water. When it is completely calcium fluoride, when the calcium carbonate in the first tower can completely become calcium fluoride, the calcium fluoride in the first column is extracted and then the new calcium carbonate is added, and the tower is used as the last The tower is provided with water, and the method of treating the fluorine-containing water in a so-called wheel-rotating manner to recover high-purity calcium fluoride is known (for example, Patent Documents 1 to 3). In the conventional calcium carbonate crucible for the treatment of the fluorine-containing water, the calcium carbonate particles which are filled with the calcium carbonate particles are excessively small in water content, and are dissolved in the fluorine-containing water to be sufficiently supplied for the reaction. Use a particle size of -5 - 201223881 Ο . 3 mm or so. [PRIOR ART DOCUMENT] [Patent Document] Patent Document 1: Japanese Laid-Open Patent Publication No. Hei. No. Hei. No. Hei. No. Hei. The problem to be solved by the invention is that the calcium carbonate particles having a particle diameter of about 0.3 mm have the following disadvantages (1) and (2). (1) It is difficult to flow in the charging tower due to the large particle size, and it is easy to adhere to the inside of the tower. (2) Compared with the smaller particles, the specific surface area is small and the reaction rate with fluorine is slow. In order to solve these problems, in the past, the fluorine-containing water flowing upward was introduced into the charging tower, and a part of the treated water taken out from the upper part of the tower was circulated to the lower part of the tower to become a circulation mode to increase the linear velocity inside the tower, so that the tower was The calcium carbonate particles inside can flow to prevent their adhesion, and the reaction can be sufficiently carried out by circulating water. However, the circulation water supply method must have the power to make it circulate, and the reaction tower volume must be large for circulating water, which is unfavorable in industry. In view of this, as long as it is a small-sized calcium carbonate particle having a particle diameter of 0.05 mm or less, the fluidity is high, it is difficult to fix the viscosity, and since the specific surface area is large, the reaction speed with fluorine is also fast, so it is not necessary to recycle. In one pass

•6- S 201223881 通水。惟小粒徑之碳酸鈣仍有以下(i) 、(ii)之問題。 (i)易溶於水,爲此對於與氟之反應其可貢獻之比 率降低。 (Π )以一過式通水時’塔內線速度小,會引起碳酸 鈣粒子的流動偏一邊,結果在塔底部會形成死水區(dead space),此部份的碳酸鈣粒子無法發揮其反應或固黏。 本發明係以使用反應活性及流動性優之小粒徑碳酸鈣 粒子’以一過式將含氟之水用向上流通水方式至反應塔, 可以有效率地除去氟’並加以回收之方法做爲課題提供者 【實施方式】 本發明人等係經銳意檢討必須解決上述之課題,結果 發現將小粒徑之碳酸鈣粒子塡充於反應塔後並不通入含氟 之水’而在以向上流通水含氟之水予反應塔時,自反應塔 之上方投入小粒徑之碳酸鈣粒子,使其可以與含氟之水中 的氟有效率地反應者^ 本發明係依此發現而終於達成者,其要旨如下。 第1態樣的含氟之水的處理方法係以向上流自反應塔 下部通水入含氟之水,使該反應塔內之碳酸鈣粒子與該含 氟之水中的氟反應,將該氟做爲氟化鈣予以除去,自該反 應塔上部取出除去氟之處理水的含氟之水的處理方法中, 對於被通入該含氟之水的該反應塔,自該反應塔上部投入 碳酸鈣粒子爲特徵者。 201223881 第2態樣的含氟之水的處理方法係第1態樣中上述碳酸 鈣粒子係做爲粉體被投入上述反應塔爲特徵者。 第3態樣的含氟之水的處理方法係第1態樣或第2態樣 中,上述反應塔之碳酸鈣粒子的投入量爲對於被通水入該 反應塔之含氟之水中的氟反應當量而言爲0.9〜1.1倍當量 做爲特徵者。 第4態樣的含氟之水的處理方法係第1至第3態樣之任 一中,上述反應塔之碳酸鈣粒子的投入量爲控制使其成爲 自該反應塔被取出之處理水的pH値6以下做爲特徵者。 第5態樣的含氟之水的處理方法係第4態樣中,使上述 反應塔之碳酸鈣粒子的投入量控制爲自該反應塔被取出之 處理水的pH値可成爲4.5〜5做爲特徵者。 第6態樣的含氟之水的處理方法係第1至第5態樣之任 一中,上述碳酸鈣粒子之粒徑爲0.0 5mm以下做爲特徵者。 第7態樣的含氟之水的處理方法係在第6態樣中,上述 碳酸鈣粒子之平均粒徑爲0.01〜0.0 3 mm做爲特徵者。 第8態樣的含氟之水的處理方法係第1至第7態樣之任 一中’經過上述反應塔內上部所設置之筒狀碳酸鈣粒子投 入構件的筒內投入上述碳酸鈣粒子的方法,該筒狀之碳酸' 鈣粒子之投入構件的上端係比該反應塔之上部水面更向上 方突出,下端係位於較該反應塔之處理水取出部水位更爲 下方30cm以上之位置做爲特徵者。 第9態樣的含氟之水的處理方法係第8態樣中,上述碳 酸鈣粒子投入構件的下端與上述反應塔之處理水取出部水• 6- S 201223881 Water. However, calcium carbonate having a small particle size still has the following problems (i) and (ii). (i) It is easily soluble in water, and for this reason, the ratio of contribution to the reaction with fluorine is lowered. (Π) When the water velocity in the tower is small, the flow rate of the calcium carbonate particles will be shifted to the side. As a result, a dead space will be formed at the bottom of the tower, and the calcium carbonate particles in this part cannot react. Or solid. In the present invention, by using a small-sized calcium carbonate particle having excellent reactivity and fluidity, the fluorine-containing water can be used to efficiently remove the fluorine and recycle it by using an upward flow of water to the reaction column. In order to solve the above problems, the present inventors have found that the small-diameter calcium carbonate particles do not pass into the fluorine-containing water after being immersed in the reaction tower. When the water-containing fluorine-containing water is supplied to the reaction tower, calcium carbonate particles having a small particle diameter are introduced from above the reaction tower to efficiently react with fluorine in the fluorine-containing water. The present invention is finally achieved by the present invention. The gist of the person is as follows. The fluorine-containing water in the first aspect is treated by flowing water from the lower portion of the reaction column into the fluorine-containing water, and reacting the calcium carbonate particles in the reaction column with fluorine in the fluorine-containing water to form the fluorine. In the treatment method of removing the fluorine-containing water from the upper portion of the reaction tower, the fluorine-containing water is removed from the upper portion of the reaction tower, and the reaction tower is introduced with the fluorine-containing water from the upper portion of the reaction tower. Calcium particles are characteristic. 201223881 The second aspect of the method for treating fluorine-containing water is characterized in that in the first aspect, the calcium carbonate particles are introduced into the reaction column as a powder. In the first aspect or the second aspect of the method for treating fluorine-containing water in the third aspect, the amount of calcium carbonate particles in the reaction column is fluorine in the water containing fluorine which is passed into the reaction column. The reaction equivalent is 0.9 to 1.1 equivalents as a characteristic. In the method of treating the fluorine-containing water of the fourth aspect, in any one of the first to third aspects, the amount of the calcium carbonate particles in the reaction column is controlled to be the treated water taken out from the reaction tower. Below pH 値6 is characteristic. In the fourth aspect of the method for treating fluorine-containing water in the fifth aspect, the amount of calcium carbonate particles in the reaction column is controlled so that the pH of the treated water taken out from the reaction column can be 4.5 to 5 For the feature. In the method of treating the fluorine-containing water of the sixth aspect, in any one of the first to fifth aspects, the particle diameter of the calcium carbonate particles is preferably 0.05 mm or less. In the sixth aspect, the method for treating fluorine-containing water in the seventh aspect is characterized in that the average particle diameter of the calcium carbonate particles is 0.01 to 0.0 3 mm. The treatment method of the fluorine-containing water of the eighth aspect is in any one of the first to seventh aspects, wherein the calcium carbonate particles are introduced into the cylinder of the tubular calcium carbonate particle-input member provided in the upper portion of the reaction column. In the method, the upper end of the tubular carbonate-calcium particle input member protrudes upward from the upper surface of the reaction tower, and the lower end is located at a position 30 cm or more lower than the water level of the treated water extraction portion of the reaction tower. Feature. In the eighth aspect of the method for treating fluorine-containing water according to the ninth aspect, the lower end of the calcium carbonate particle-input member and the treated water of the reaction tower are taken out.

-8 - S 201223881 位間的距離Li爲25〜100cm,爲上述反應塔之全有效塔高 L2之1/20〜1/5做爲特徵者。 第10態樣的含氣之水的處理方法係第8或第9態樣中, 對於有底圓筒形狀之上述反應塔,圓筒狀之上述碳酸鈣粒 子投入構件爲被設置爲同心狀,(相對於該反應塔之直徑 (內徑)而言)前述碳酸鈣粒子投入構件之直徑(內徑) 爲1/5〜1/10做爲特徵者》 第1 1態樣的含氟之水的處理方法係第8至第1 0之任一 態樣中,有底圓筒狀形狀之上述反應塔的直徑係爲300〜 150mm,上述含氟之水的向上流速爲150〜5000L/h,上述 碳酸鈣粒子的投入量爲3〜1 00 L/h做爲特徵者。 第1 2態樣的含氟之水的處理方法係第8至第1 0態樣之 任一中,有底圓筒形狀之上述反應塔的直爲1 500〜 3000mm,上述含氟之水的向上流速爲5000〜20000L/h, 上述碳酸鈣粒子的投入量爲1〇〇〜400L/h做爲特徵者。 第13態樣的含氟之水的處理方法係第8至第10態樣之 任一中,有底圓筒形狀之上述反應塔的直徑爲3 000〜 5 0000mm,上述含氟之水的向上流速爲2000〜60000L/h, 上述碳酸鈣粒子的投入量爲400〜1 200L/h做爲特徵者。 第14態樣的含氟之水的處理方法係第1至第13態樣之 任一中,以一過式將上述含氟之水通水入上述反應塔做爲 特徵者。 第1 5態樣的含氟之水的處理方法係第1至第1 4態樣之 任一中,直列地連結2塔以上之反應塔,依順序自第一段 201223881 之反應塔將上述含氟之水通入各反應塔,當該第一段反應 塔之流入水的水質與流出水之水質大約相同之後,中止對 該第一段反應塔的通水,改換成對第二段反應塔的通水, 取出該第一段反應塔內之含氟化鈣之粒子,以該第一段之 反應塔做爲上述二塔以上之反應塔的最後段反應塔,重覆 依序通水之工程,成爲一種隨輪轉動方式的通水方法,對 於該含氟之水被通入水的最後段反應塔投入上述碳酸鈣粒 子做爲特徵者。 第16態樣的含氟之水的處理方法係在第15態樣中,投 入上述碳酸鈣粒子的最後段反應塔係在上述含氟之水通水 之前,在不會預先形成碳酸鈣塡充層,進行上述含氟之水 的通水與投入碳酸鈣粒子做爲特徵者。 第17態樣的含氟之水的處理方法係在第15或第16態樣 中,在上述最後段的反應塔中,會有前段的反應塔之處理 水的氟濃度1 000〜30000mg/L的含氟之水以一過式向著上 方被流通入水做爲特徵》 〔發明之效果〕 依本發明時可以使用反應活性及流動性優異之小粒徑 ,例如粒徑爲〇.〇5mm以下的碳酸鈣粒子,並不是預先將其 塡充於反應塔內以形成塡充層後再通入含氟之水,而是在 上向流通含氟之水時,自反應塔上部做爲粉體投入,而可 以防止因反應塔中之碳酸鈣粒子的流動偏一邊而形成死水 區域。-8 - S The distance between 201223881 is Li 25~100cm, which is characterized by 1/20~1/5 of the total effective tower height L2 of the above reaction tower. In the eighth or ninth aspect, in the eighth or ninth aspect, in the reaction column having a bottomed cylindrical shape, the cylindrical calcium carbonate particle input member is set to be concentric. (relative to the diameter (inner diameter) of the reaction column) The diameter (inner diameter) of the calcium carbonate particle-input member is 1/5 to 1/10 as a feature of the fluorine-containing water of the first aspect In any one of the eighth to tenth aspects, the diameter of the reaction column having a bottomed cylindrical shape is 300 to 150 mm, and the upward flow rate of the fluorine-containing water is 150 to 5000 L/h. The input amount of the above calcium carbonate particles is 3 to 100 L/h. The method for treating fluorine-containing water in the first aspect is a method of any one of the eighth to tenth aspects, wherein the reaction column having a bottomed cylindrical shape is directly 1500 to 3000 mm, and the fluorine-containing water is The upward flow rate is 5000 to 20000 L/h, and the input amount of the above calcium carbonate particles is 1 to 400 L/h. The method for treating fluorine-containing water in the thirteenth aspect is any one of the eighth to tenth aspects, wherein the diameter of the reaction column having a bottomed cylindrical shape is 3,000 to 50,000 mm, and the above-mentioned fluorine-containing water is upward. The flow rate is 2000 to 60000 L/h, and the input amount of the above calcium carbonate particles is 400 to 1 200 L/h. In the method of treating the fluorine-containing water of the fourteenth aspect, in any one of the first to thirteenth aspects, the fluorine-containing water is passed through the reaction column as a feature. The method for treating fluorine-containing water in the first aspect is a reaction column in which two or more columns are connected in series, and the above-mentioned reaction tower is sequentially connected from the first column of 201223881. The water of fluorine is introduced into each reaction tower. When the water quality of the inflow water of the first reaction tower is about the same as the water quality of the effluent water, the water passing through the first reaction tower is stopped, and the reaction is changed to the second stage. The water passing through the tower is taken out, and the particles of the calcium fluoride containing in the first reaction tower are taken out, and the reaction tower of the first stage is used as the last reaction tower of the reaction tower above the two towers, and the water is repeatedly passed through. The project is a water-passing method for the rotation of the wheel, and the calcium carbonate particles are introduced into the last reaction column in which the fluorine-containing water is introduced into the water. The treatment method of the fluorine-containing water of the sixteenth aspect is the 15th aspect, wherein the last-stage reaction tower to which the calcium carbonate particles are charged is not pre-formed with calcium carbonate before the water containing the fluorine-containing water passes through the water. The layer is characterized in that water of the above-mentioned fluorine-containing water is supplied and calcium carbonate particles are introduced. The treatment method of the fluorine-containing water of the 17th aspect is in the 15th or 16th aspect, and in the reaction tower of the last stage, there is a fluorine concentration of the treated water of the reaction tower of the preceding stage of 1 000 to 30000 mg/L. In the present invention, a small particle diameter excellent in reactivity and fluidity, for example, a particle diameter of 〇.〇5 mm or less can be used as the feature of the present invention. The calcium carbonate particles are not preliminarily charged in the reaction tower to form a sputum layer, and then the fluorine-containing water is introduced, but when the fluorine-containing water is circulated upward, the upper portion of the reaction tower is used as a powder. In addition, it is possible to prevent the formation of a dead water region due to the flow of the calcium carbonate particles in the reaction tower.

-10- S 201223881 小粒徑之碳酸鈣粒子係容易溶解者,惟只要依照pH値 控制投入之碳酸鈣粒子,亦可以防止碳酸鈣之溶解。 即,碳酸鈣與氟,例如與氟化氫之反應係如以下反應 式(I)所示,pH酸性條件下,藉由反應生成之碳酸係依 下述式(II),不會立即做爲碳酸氣體溶解於水中而被排 出至系外,所以不會影響及碳酸鈣,但在pH中性以上之條 件下,會依以下式(III)而成爲重碳酸離子。生成之重碳 酸離子會作爲酸進行作用,而會溶解碳酸鈣。-10- S 201223881 The small-sized calcium carbonate particles are easily dissolved. However, it is also possible to prevent the dissolution of calcium carbonate by controlling the calcium carbonate particles charged according to the pH. That is, the reaction between calcium carbonate and fluorine, for example, with hydrogen fluoride is as shown in the following reaction formula (I). Under acidic pH conditions, the carbonic acid formed by the reaction is not immediately used as the carbonic acid gas according to the following formula (II). It is dissolved in water and discharged to the outside of the system, so it does not affect calcium carbonate. However, under conditions of pH neutrality or higher, it becomes a bicarbonate ion according to the following formula (III). The produced heavy carbon acid ions act as an acid and dissolve calcium carbonate.

CaC03+2HF^CaF2+H2C〇3 ··· ( I ) pH 隨:H2CO 广 H20 + C02 (產生氣體) -.-(11) Ρ Η中性以上:h2co3 — h + +hco3- . . · (III) 所以本發明中係對反應塔之碳酸鈣粒子的投入量,最 好控制爲自反應塔所取出之處理水的pH値做爲6以下,藉 此防止碳酸鈣之溶解。 對反應塔之碳酸鈣粒子的投入量係對於被通水於反應 塔之含氟之水中的氟之反應當量爲〇·9〜1.1倍當量時,就 高度地除去回收含氟之水中的氟而言較佳。 又,本發明中,碳酸鈣粒子之投入係自設於反應塔內 上部的筒狀碳酸鈣粒子投入構件,上端會較反應塔上部水 面更上方突出,下端則以經由較反應塔的處理水取出部的 水位低30cm以上之下方位置所設的碳酸#5粒子投入構件的 筒內投入會較佳。 即,直接將小粒徑之碳酸鈣粒子維持於粉體之狀態下 投入時,因此粉體中亦會含有一部份微粉狀者’此微粉狀CaC03+2HF^CaF2+H2C〇3 ··· ( I ) pH with: H2CO H20 + C02 (generating gas) -.-(11) Ρ Η Neutral or above: h2co3 — h + + hco3- . . III) Therefore, in the present invention, the amount of calcium carbonate particles to be injected into the reaction column is preferably controlled so that the pH of the treated water taken out from the reaction column is 6 or less, thereby preventing dissolution of calcium carbonate. When the reaction amount of the calcium carbonate particles in the reaction column is 〇·9 to 1.1 times the equivalent amount of fluorine which is passed through the water in the fluorine-containing water of the reaction column, the fluorine in the fluorine-containing water is highly removed. Better words. Further, in the present invention, the calcium carbonate particles are supplied from the cylindrical calcium carbonate particle input member provided in the upper portion of the reaction column, and the upper end protrudes above the upper surface of the reaction tower, and the lower end is taken out through the treated water of the reaction tower. The in-cylinder injection of the carbonic acid #5 particle input member provided at a position lower than the water level of 30 cm or more is preferable. That is, when the calcium carbonate particles having a small particle diameter are directly maintained in a state of being put into a powder, the powder also contains a part of the fine powder.

之碳酸鈣會投入後直接自反應塔之溢流口,與處理水—起 S -11- 201223881 自反應塔流出,恐無法被使用於反應。要投入這種小粒徑 之碳酸鈣粒子時,若使用如上述之碳酸鈣粒子投入構件時 ,會在碳酸鈣粒子投入構件的筒內部會有微粉狀之碳酸鈣 滯留,與塔內之水充分地接觸,對反應可以有更大之貢獻 〇 本發明係特別將2塔以上之反應塔直列連接,以隨輪 轉動方式進行含氟之水通水時係最好適用於被通水含氟之 水的最後段反應塔,這時在投入碳酸鈣粒子之最後段的反 應塔係通水含氟之水之前係不要預先形成碳酸鈣塡充層, 以進行含氟之水的通水與投入碳酸鈣粒子,以防止塔內之 偏流,並防止形成死水區域爲最佳。 〔實施發明之形態〕 以下參照圖面詳細說明本發明含氟之水的處理方法之 實施形態。 圖1係示被適用於本發明之反應塔1 —例之模式性剖面 圖,此反應塔1係一種上部開放之有底圓筒形狀者,自底 部導入含氟之水,構成爲可自上部之溢流口 2取出處理水 。3係投入碳酸鈣粒子的構件,圖1中碳酸鈣粒子投入構件 3係使其與反應塔1成同心狀地固定於反應塔1之上部,其 上端3A係自反應塔1之水面突出,下端3B係被設置在反應 塔1之水面下,裝設爲可以較反應塔1之溢流口 2的水位更 下方位置之垂直方向。 含氟之水係自反應塔1的底部被導入,再自上述之溢The calcium carbonate will be directly injected from the overflow port of the reaction tower, and the treated water will flow out from the reaction tower from S -11-201223881, and it may not be used in the reaction. When such a calcium carbonate particle having a small particle size is to be used, when the calcium carbonate particle-inputting member is used as described above, calcium carbonate-like calcium carbonate is retained inside the cylinder of the calcium carbonate particle-injecting member, and the water in the tower is retained. In sufficient contact, the reaction can have a greater contribution. The present invention specifically connects the reaction towers of two or more towers in series, and is preferably applied to the water-containing fluorine when the water containing fluorine is passed through in a rotating manner. In the last stage of the water reaction tower, before the reaction tower of the last stage of the injection of the calcium carbonate particles is passed through the water containing fluorine, the calcium carbonate filling layer is not formed in advance to carry out the water supply and the carbonation of the fluorine-containing water. Calcium particles are best used to prevent drift in the tower and to prevent the formation of dead water areas. [Mode for Carrying Out the Invention] Hereinafter, an embodiment of a method for treating water containing fluorine according to the present invention will be described in detail with reference to the drawings. BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 is a schematic cross-sectional view showing an example of a reaction column 1 which is applied to the present invention. The reaction column 1 is an open-bottomed bottomed cylindrical shape, and fluorine-containing water is introduced from the bottom to be constructed from the upper portion. The overflow port 2 takes out the treated water. 3 is a member into which calcium carbonate particles are introduced, and in FIG. 1, the calcium carbonate particle-input member 3 is fixed to the upper portion of the reaction tower 1 concentrically with the reaction tower 1, and the upper end 3A is protruded from the water surface of the reaction tower 1, and the lower end The 3B system is disposed under the water surface of the reaction tower 1, and is installed in a vertical direction which can be lower than the water level of the overflow port 2 of the reaction tower 1. The fluorine-containing water is introduced from the bottom of the reaction column 1, and then overflows from the above

-12- S 201223881 流口 2流出。在此含氟之水上向流通水時,本發明中係自 反應塔1上部,經由碳酸鈣粒子投入構件3的筒內,投入碳 酸鈣粒子。含氟之水內的氟係與被投入之碳酸鈣粒子反應 ,做爲氟化鈣被析出,自含氟之水中被除去。 自反應塔1上部被投入之碳酸鈣粒子係粒徑若過大時 ,與氟之反應速度會慢,無法達成使用粒徑小的碳酸鈣予 以提高反應速度之本發明目的。因此,本發明使用之碳酸 鈣粒子的粒徑係以0.〇5mm以下,較佳爲0.03mm以下,平 均粒徑係以〇.〇1〜0.03mm左右,尤其以0.02〜0.03mm程度 者較適宜。 又,投入之碳酸鈣粒子量過少時無法充分除去含氟之 水中的氟,太多時只會徒增碳酸鈣粒子的使用量而不經濟 ,不但如此,若有未反應之碳酸鈣殘留下來,還會有其無 法轉換爲氟化鈣,而有無法得到高純度之氟化鈣的問題》 因此碳酸鈣粒子之投入量係對通水入反應塔1的含氟之水 中之氟其反應當量之0.9〜1.1當量倍,尤其以0.95〜1.05 當量爲宜。 又,本發明中,碳酸鈣粒子係維持爲粉體之下投入反 應塔。若使碳酸鈣粒子成爲水泥游漿予以投入時,做爲水 泥游漿必須有被添加入之水量份的反應塔容量,更爲了移 送必須有唧筒,又,就碳酸鈣粒子與含氟之水中的氟反應 效率而言,亦以做爲粉體投入較佳。 碳酸鈣粒子之投入係亦可爲連續投入,又,可以例如 每5〜3 00分鐘一次的次數予以間隔地進行。連續地投入時-12- S 201223881 Flow port 2 outflow. In the present invention, when the water is distributed to the water containing fluorine, in the upper portion of the reaction column 1, the calcium carbonate particles are introduced into the cylinder of the member 3 via the calcium carbonate particles. The fluorine in the fluorine-containing water reacts with the calcium carbonate particles to be charged, and calcium fluoride is precipitated and removed from the fluorine-containing water. When the particle size of the calcium carbonate particles introduced from the upper portion of the reaction column 1 is too large, the reaction rate with fluorine is slow, and the object of the present invention in which calcium carbonate having a small particle diameter is used to increase the reaction rate cannot be achieved. Therefore, the particle size of the calcium carbonate particles used in the present invention is 0. 5 mm or less, preferably 0.03 mm or less, and the average particle diameter is about 〜1 to 0.03 mm, especially 0.02 to 0.03 mm. suitable. Further, when the amount of the calcium carbonate particles to be supplied is too small, the fluorine in the fluorine-containing water cannot be sufficiently removed, and when too much, the amount of the calcium carbonate particles used is not increased, and it is not economical, and if unreacted calcium carbonate remains, There is also the problem that it cannot be converted into calcium fluoride, and there is no possibility of obtaining high-purity calcium fluoride. Therefore, the amount of calcium carbonate particles is the reaction equivalent of fluorine in the fluorine-containing water that passes through the reaction tower 1 0.9 to 1.1 equivalent times, particularly preferably 0.95 to 1.05 equivalents. Further, in the present invention, the calcium carbonate particles are maintained in the reaction column under the powder. If the calcium carbonate particles are put into the cement slurry, the capacity of the reaction tower must be added as the amount of water to be added to the cement. The transfer must have a cylinder, and in the case of calcium carbonate particles and fluorine-containing water. In terms of fluorine reaction efficiency, it is also preferable to use it as a powder. The input of the calcium carbonate particles may be continuously input, and may be carried out at intervals, for example, every 5 to 300 minutes. When continuously put in

S -13- 201223881 的每一所定時間的碳酸鈣粒子投入量或分次投入時的每次 碳酸鈣粒子的投入量係依對於上述含氟之水中之氟的反應 當量之比例,或配合以下記載之塔內的合適pH値予以決定 〇 如上述,本發明使用之小粒徑碳酸鈣粒子係有易於溶 解於水的缺點者,惟可以依據pH値進行控制碳酸鈣粒子的 投入,即可以防止碳酸鈣之溶解。 本發明中係爲防止碳酸鈣之溶解,以控制反應塔內之 反應液的pH値爲6以下,尤其以5以下爲較佳。一般而言, 含氟之水中添加碳酸鈣時會提高pH値,而會較易溶解碳酸 鈣粒子。爲此最好在pH値低的狀態下逐以少量投入碳酸鈣 粒子,對於防止碳酸鈣粒子溶解之觀點而言爲較佳。 因此,本發明中係測定自反應塔1流出之處理水或反 應塔上部之水的pH値,控制此pH値爲6以下,尤其5以下 來控制碳酸鈣投入量爲宜。又,此pH値係就防止碳酸鈣粒 子溶解的觀點而言以低爲宜》惟就確保與氟反應之必要量 的碳酸鈣粒子投入量,通常係4.5以上》 又,碳酸鈣粒子之投入若對於含氟之水向上流予以流 動的反應塔直接進行時,所投入之碳酸鈣粒子的一部份會 與處理水一起自反應塔流出,無法供予反應,不但如此逐 會成爲降低處理水水質之原因。 即,如上述,若將小粒徑之碳酸鈣粒子維持在粉體之 下投入時,因粉體中亦會有一部份微粉狀者含於其中,此 微粉狀之碳酸鈣會自溢流口與處理水一起在投入後立即自 -14-The amount of calcium carbonate particles input per time for S-13-201223881 or the amount of calcium carbonate particles charged per fraction of time is based on the ratio of the reaction equivalent of fluorine to the fluorine-containing water, or the following The suitable pH in the column is determined. As described above, the small-sized calcium carbonate particles used in the present invention have the disadvantage of being easily dissolved in water, but the calcium carbonate particles can be controlled according to the pH, that is, the carbonic acid can be prevented. Calcium dissolution. In the present invention, in order to prevent the dissolution of calcium carbonate, the pH of the reaction liquid in the reaction column is controlled to be 6 or less, and particularly preferably 5 or less. In general, the addition of calcium carbonate to the fluorine-containing water increases the pH enthalpy and makes it easier to dissolve the calcium carbonate particles. For this reason, it is preferable to introduce a small amount of calcium carbonate particles in a state where the pH is low, and it is preferable from the viewpoint of preventing dissolution of the calcium carbonate particles. Therefore, in the present invention, the pH of the treated water flowing from the reaction column 1 or the water in the upper portion of the reaction column is measured, and it is preferable to control the pH to be 6 or less, particularly 5 or less to control the amount of calcium carbonate to be supplied. In addition, this pH system is preferably used to prevent the dissolution of calcium carbonate particles, and the amount of calcium carbonate particles required to ensure the reaction with fluorine is usually 4.5 or more. When the reaction column in which the fluorine-containing water flows upward is directly carried out, a part of the calcium carbonate particles to be injected will flow out from the reaction tower together with the treated water, and the reaction cannot be performed, and not only will the water quality of the treated water be reduced. The reason. That is, as described above, when the calcium carbonate particles having a small particle diameter are maintained under the powder, a part of the powdery powder is also contained therein, and the fine powdery calcium carbonate will overflow. The vent and the treated water are immediately after the input from -14-

S 201223881 反應塔流出,深恐無法對於反應有所貢獻。 所以本發明中係如圖1所示,最好在反應塔1中設置筒 狀之碳酸鈣粒子投入構件3,經由此碳酸鈣粒子投入構件3 的筒內’將碳酸鈣粒子投入反應塔1爲最適宜。如上述, 此碳酸鈣粒子投入構件3係與反應塔1成爲同心狀被固定於 反應塔1之上部,此上端3 A係自反應塔1之水面突出,下端 3B係設在反應塔1的水面下,使其在較反應塔1之溢流口 2 之水位更下方位置地被設定爲垂直方向者。使用這種碳酸 鈣粒子投入構件3,在碳酸鈣粒子投入構件3之筒內部使微 粉狀碳酸鈣滯留,使其與塔內之水充分接觸,即可使此等 微粉狀之碳酸鈣粒子更順利地反應。 此碳酸鈣粒子投入部材料3的下端3B與反應塔1之溢流 口 2之水位的距離川係若過度短時無法獲得因設置這種碳 酸鈣粒子投入構件3而可得之充分上述效果,過度長時與 含氟水之向上流的接觸效率會變差。因此此距離Li係以25 〜100cm,例如50cm左右,成爲反應塔之全有效塔高L2之 1/20〜1/5程度爲宜。 又,例如圖1所示對於有底圓筒形狀之反應塔1要設置 圓筒狀的碳酸鈣粒子投入構件3時,係以對反應塔1之直徑 (內徑)使碳酸鈣粒子投入構件3之直徑(內徑)爲1/5〜 1/10程度,而碳酸鈣粒子投入構件3係與反應塔1成同心狀 地設置,這樣對於防止微粉狀碳酸鈣粒子流出’提高含氟 之水之接觸效率而言較佳。 向反應塔1之含氟之水的向上流速係使其與自反應塔1 -15- 201223881 上部被投入之碳酸鈣粒子的接觸效率可充分確保之情況下 ,對於反應塔之直徑或碳酸鈣粒子投入量間的相關而言, 最好適當地調整,例如以下所示條件較佳。 (i)反應塔之直徑:300〜1 500mm時 含氟水之上向流速:150〜500 OL/h 碳酸鈣粒子之投入量:3〜100L/h (Π)反應塔之直徑:1 500〜3000mm時 含氟水之上向流速:5000〜2000L/h 碳酸鈣粒子之投入量:100〜400L/h (iii)反應塔之直徑:3000〜5000mm時 含氟水之上向流速:2000〜60000L/h 碳酸鈣粒子之投入量:400〜120 OL/h 又,適用於本發明之反應塔,雖亦可爲一過式通水含 氟之水或爲循環通水,惟爲了可以不必使用小粒徑之碳酸 鈣粒子循環通水,即可發揮得高反應效率的本發明效果, 亦以一過式通水較爲適宜。 繼續此種處理,反應塔內會因與氟之反應而成爲氟化 鈣的粒子會堆積起來,可以適當地停止通水以取出此氟化 鈣粒子。 本發明中係爲了減少反應塔內的偏流,以防止死水域 在塔底部生成起見,又,就防止碳酸鈣粒子溶解起見,碳 酸鈣粒子係投入預先塡充有碳酸鈣粒子的反應塔,倒不如 逐以少量投入未形成有碳酸鈣粒子塡充層之反應塔爲宜。 因此,本發明係尤其以直列連結2塔以上之反應塔,以隨 -16-S 201223881 The reaction tower flows out, and it is feared that it will not contribute to the reaction. Therefore, in the present invention, as shown in Fig. 1, it is preferable to provide a cylindrical calcium carbonate particle-input member 3 in the reaction column 1, and to introduce calcium carbonate particles into the reaction column 1 through the inside of the calcium carbonate particle-input member 3. Most suitable. As described above, the calcium carbonate particle-input member 3 is fixed to the upper portion of the reaction column 1 concentrically with the reaction column 1, and the upper end 3A protrudes from the water surface of the reaction column 1, and the lower end 3B is provided on the water surface of the reaction column 1. Next, it is set to a vertical direction at a position lower than the water level of the overflow port 2 of the reaction column 1. By using the calcium carbonate particle-input member 3, the fine powdery calcium carbonate is retained in the inside of the cylinder of the calcium carbonate particle-input member 3, and is sufficiently contacted with the water in the column to obtain such fine powdery calcium carbonate particles. React more smoothly. When the distance between the lower end 3B of the calcium carbonate particle input portion material 3 and the water level of the overflow port 2 of the reaction column 1 is too short, the above-described effects which are obtained by providing such a calcium carbonate particle input member 3 cannot be obtained. The contact efficiency with the upward flow of the fluorine-containing water may be deteriorated in an excessively long period of time. Therefore, the distance Li is preferably from 25 to 100 cm, for example, about 50 cm, and is preferably about 1/20 to 1/5 of the total effective column height L2 of the reaction column. Further, for example, when the cylindrical calcium carbonate particle input member 3 is provided in the reaction column 1 having a bottomed cylindrical shape as shown in Fig. 1, the calcium carbonate particles are supplied to the member 3 by the diameter (inner diameter) of the reaction column 1. The diameter (inner diameter) is about 1/5 to 1/10, and the calcium carbonate particle input member 3 is disposed concentrically with the reaction column 1, so as to prevent the flow of the fine powdery calcium carbonate particles. The contact efficiency is preferred. The upward flow rate of the fluorine-containing water to the reaction column 1 is such that the contact efficiency with the calcium carbonate particles charged from the upper portion of the reaction column 1 -15 - 201223881 can be sufficiently ensured, for the diameter of the reaction column or the calcium carbonate particles The correlation between the input amounts is preferably adjusted as appropriate, and for example, the conditions shown below are preferred. (i) The diameter of the reaction tower: 300~1 500mm, the flow rate of the fluorine-containing water: 150~500 OL/h The input amount of the calcium carbonate particles: 3~100L/h (Π) The diameter of the reaction tower: 1 500~ Flow rate of fluorine-containing water at 3000mm: 5000~2000L/h Input of calcium carbonate particles: 100~400L/h (iii) Diameter of reaction tower: Flow rate of fluorine-containing water above 3000~5000mm: 2000~60000L /h Calcium carbonate particles input: 400~120 OL/h Further, it is suitable for the reaction tower of the present invention, although it can also be a water-passing water or a circulating water, but it is not necessary to use small When the calcium carbonate particles having a particle diameter are circulated through the water, the effect of the present invention which exhibits high reaction efficiency can be exhibited, and it is also preferable to pass the water in one pass. By continuing this treatment, particles which become calcium fluoride due to the reaction with fluorine are accumulated in the reaction tower, and the water can be appropriately stopped to take out the calcium fluoride particles. In the present invention, in order to reduce the drift in the reaction tower, to prevent the formation of dead water in the bottom of the tower, and to prevent the dissolution of the calcium carbonate particles, the calcium carbonate particles are put into a reaction tower previously filled with calcium carbonate particles. It is preferable to use a small amount of a reaction column in which a calcium carbonate particle-filled layer is not formed. Therefore, the present invention in particular connects the reaction towers of 2 or more columns in series to follow -16-

S 201223881 輪轉動方式進行含氟之水的通水時’對於 水的最後段反應塔,可以在不形成碳酸釣 下予以應用。 即,一般之依隨輪轉動方式的處理係 ,將其與最前段之反應塔內的含氟之水中 氟化鈣的粒子排出於塔外之後’再添加新 在塔內形成塡充層以做爲最後段之反應塔 則在此反應塔中不形成碳酸鈣粒子的塡充 之反應塔,對於此未形成碳酸鈣塡充層之 將前段之反應塔處理水的氟濃度爲1000〜 的含氟之水以一過式使其成爲向上流通水 入碳酸鈣粒子較爲適宜。 另外,此種隨輪轉動方式之對通水切 常法,例如可依以下實行。即,如專利或 列地連結2塔以上,例如2〜4塔之複數反 塔之入口及出口設置氟濃度計或pH計。又 應塔以外,其他則使其形成爲碳酸鈣粒子 一層之反應塔依序將含氟之水向上流入通 段之反應塔中投入碳酸鈣粒子。一直到第 口前的氟濃度計或pH計,與此第一段反應 濃度計或p Η計的數値可以成爲大約相同之 水處理,待到成爲相同數値後,中止對第 水’改換成對第二段反應塔的通水,同時 應塔內的含氟化鈣粒子取出,不必再添加 被通水該含氟之 粒子的塡充層之 在前次之循環中 之氟反應而成爲 的碳酸鈣粒子, 者,惟本發明中 層而做爲最後段 最後段反應塔, -30000mg/L程度 ,同時自上部投 換本身係可以依 〔獻3所記載,直 應塔,在各反應 ,除最後段之反 的塡充層,自第 水,同時對最後 一段反應塔之入 塔的出口所設氟 數値爲止繼續通 一段反應塔的通 將中止通水之反 新的碳酸鈣粒子 -17- 201223881 ’以此做爲最後段的反應塔予以聯結,自第2段的反應塔 依序通水入含氟之水。以下依同樣之順序,依序進行將第 一段反應塔連結予最後段的隨輪轉動方式的替換。 如上述,對於未形成碳酸鈣粒子塡充層之反應塔適用 本發明時,可以有效地發揮本發明之效果。 實施例 以下舉實施例及比較例,更具體說明本發明。 〔實施例1〕 使用圖1所示反應塔1,以50L/h之流速以一過式以上 向流通水l〇〇〇〇mg/L氟濃度之含氟之水,同時經由反應塔1 上部所設碳酸鈣粒子投入構件3,以10分鐘1次之次數,一 次投入1/3L之量,投入平均粒徑〇.〇3mm的碳酸鈣粒子,使 其使處理水之pH可成爲5以下,具體言可成爲4·5〜5.0。 碳酸鈣粒子之投入量係對通水之含氟之水的氟反應當量而 言爲1.0 2倍當量。 另外,反應塔1係直徑300mm ’高度300cm (即, L2 = 3 00cm )之有底圓筒形狀,可以自塔上端的溢流口 2取 出使處理水可以覆蓋地取出。設置於反應塔1之碳酸鈣粒 子投入構件3係直徑l〇〇mm’長度400mm的圓筒形,設置成 對於反應塔1成爲同心形者。此投入碳酸鈣粒子投入構件3 的下端3B係位於較反應塔之溢流口更爲下方3〇cm (即 1^=300111)之位置。 -18 -S 201223881 When the wheel is rotated to pass the water containing fluorine water, the last reaction tower for water can be applied without carbonation. That is, in general, the processing system according to the wheel rotation mode discharges the particles of calcium fluoride in the fluorine-containing water in the reaction column of the foremost stage, and then adds a new layer in the tower to form a filling layer. In the reaction column of the last stage, a reaction column in which no calcium carbonate particles are formed is formed in the reaction column, and the fluorine having a fluorine concentration of 1000 to 15 in the reaction tower of the reaction column in which the calcium carbonate is not formed is not formed. It is preferable that the water is made into an upward flow of water into the calcium carbonate particles in one pass. In addition, such a method of turning the water in accordance with the rotation mode of the wheel can be carried out, for example, as follows. Namely, a fluorine concentration meter or a pH meter is provided at the inlet and outlet of a plurality of counter towers such as a patent or a column connecting two or more columns, for example, 2 to 4 columns. Further, in addition to the column, the reaction tower which is formed as a layer of calcium carbonate particles sequentially feeds the fluorine-containing water into the reaction column of the passage section to introduce calcium carbonate particles. The fluorine concentration meter or the pH meter up to the first mouth, and the number of the first reaction concentration meter or the p Η meter can be treated as about the same water, and after the same number, the water is changed. The water is exchanged for the second reaction column, and the calcium fluoride particles in the column are taken out, and it is not necessary to add the fluorine reaction in the previous cycle of the fluorinated layer of the fluorine-containing particles. The calcium carbonate particles to be formed, but the middle layer of the present invention is used as the last stage reaction tower of the last stage, -30000 mg/L, and the system itself can be exchanged from the upper part according to [3, the straight column, in each reaction In addition to the reverse layer of the last stage, from the first water, while continuing to pass the reaction column of the last stage of the reaction tower into the tower, the passage of the reaction tower will stop the reversed calcium carbonate particles. -17- 201223881 'This is used as the last stage of the reaction tower to be connected, and the reaction tower from the second stage is sequentially supplied with water into the fluorine-containing water. In the following order, the replacement of the first-stage reaction tower to the last stage of the rotation of the wheel is performed in the same order. As described above, when the present invention is applied to a reaction tower in which a calcium carbonate particle-containing layer is not formed, the effects of the present invention can be effectively exhibited. EXAMPLES Hereinafter, the present invention will be more specifically described by way of examples and comparative examples. [Example 1] Using the reaction column 1 shown in Fig. 1, at a flow rate of 50 L/h, a fluorine-containing water having a fluorine concentration of 1 过 mg/L was passed over at a flow rate of more than one passage, while passing through the upper portion of the reaction column 1 The calcium carbonate particle-input member 3 is placed in an amount of 1/3 L at a time of 10 minutes, and calcium carbonate particles having an average particle diameter of 〇3 mm are introduced so that the pH of the treated water can be 5 or less. Specifically, it can be 4. 5 to 5.0. The amount of calcium carbonate particles charged is 1.02 times the equivalent of the fluorine reaction equivalent of the fluorine-containing water passing through the water. Further, the reaction column 1 has a bottomed cylindrical shape having a diameter of 300 mm' and a height of 300 cm (i.e., L2 = 300 cm), and can be taken out from the overflow port 2 at the upper end of the column so that the treated water can be taken out. The calcium carbonate particle input member 3 provided in the reaction column 1 has a cylindrical shape having a diameter of 10 mm and a length of 400 mm, and is provided so as to be concentric with respect to the reaction column 1. The lower end 3B of the input calcium carbonate particle input member 3 is located 3 sec (i.e., 1^=300111) lower than the overflow port of the reaction tower. -18 -

S 201223881 經過30小時連續通水後,反應塔1內1 (經由反應至少一部份成爲氟化鈣的碳酸 粒子自反應塔底部拔出,完全看不出有粒 又,經此處理過之的處理水之氟濃度 ,氟已被高度地被除去。 〔比較例1〕 於實施例1中,不進行投入碳酸鈣粒 之水前,預先將60L碳酸鈣粒子(粒徑及 施例1中所用者爲相同者)塡充於反應塔 層,除此外,其他則均一樣地進行向上流 〇 連續通水20小時後,反應塔內之粒子 解之關係,減少成爲48L。又,此粒子中 塔底部。 又,此處理所得之處理水的氟濃度$ ,氟之除去效率亦不佳。 如上使用特定態樣,詳細說明了本發 者可以極清楚地獲知,只要不脫離本發明 事實上可以做出各種式樣之變更,就斯業 白之事。 另外,本案之申請係依2010年7月28 專利(特許2010-169378)者,其全部均 列出。S 201223881 After 30 hours of continuous water flow, the reaction column 1 is 1 (the carbonic acid particles which are at least partially converted into calcium fluoride are pulled out from the bottom of the reaction tower, and no particles are observed at all. The fluorine concentration of the treated water was highly removed. [Comparative Example 1] In Example 1, 60 L of calcium carbonate particles (particle size and used in Example 1) were used before the water for the calcium carbonate particles was introduced. The same is the same as the reaction tower layer, except that the others are all flowed upwards continuously for 20 hours, and the relationship between the particles in the reaction tower is reduced to 48 L. Further, the fluorine concentration of the treated water obtained by this treatment is not good for the removal efficiency of fluorine. As described above, the specific use of the specific aspect will be clearly understood by the present applicant, as long as it does not deviate from the present invention. In addition, the application of this case is based on the July 28, 2010 patent (licensed 2010-169378), all of which are listed.

汀以留下60L粒子 鈣粒子)。將此 子固黏等現象。 係 100 〜300mg/L 子,在通入含氟 平均粒徑係與實 ,以形成爲塡充 通水入含氟之水 係因碳酸鈣被溶 5L係固黏於反應 呑 8 00 〜1 500mg/L 明,只要爲斯業 之意圖及範圍, 者而言係極爲明 曰在日本申請之 經引用在本件中 -19- 201223881 【圖式簡單說明】 圖1 :示在本發明被應用之反應塔一例之模式剖面圖 【主要元件符號說明】 1 :反應塔 2 :溢流口 3 :碳酸鈣粒子投入構件 3 A :上端 3B :下端 L!:水位的距離 L2 :全有效塔高Ting to leave 60L particles of calcium particles). This phenomenon is fixed. 100 ~ 300mg / L, in the fluorine-containing average particle size and solid, to form a water-filled water into the fluorine-containing water system due to calcium carbonate is dissolved in the 5L system is fixed in the reaction 呑 8 00 ~ 1 500mg /L Ming, as long as it is the intention and scope of the company, it is very clear that the application in Japan is cited in this article -19- 201223881 [Simple description of the diagram] Figure 1: shows the reaction applied in the present invention Schematic diagram of a tower example [Description of main components] 1 : Reaction tower 2 : Overflow port 3 : Calcium carbonate particle input member 3 A : Upper end 3B : Lower end L!: Distance of water level L2 : Full effective tower height

-20- S-20- S

Claims (1)

201223881 七、申請專利範圍: 1. 一種含氟之水的處理方法,其特徵爲以向上流自 反應塔下部通水入含氟之水,使該反應塔內之碳酸鈣粒子 與該含氟之水中的氟反應,將該氟做爲氟化鈣予以除去, 自該反應塔上部取出除去氟之處理水的含氟之水的處理方 法中,對於被通水入該含氟之水的該反應塔,自該反應塔 上部投入碳酸鈣粒子者。 2. 如申請專利範圍第1項之含氟之水的處理方法,其 中上述碳酸鈣粒子係做爲粉體被投入上述反應塔者。 3. 如申請專利範圍第1項或第2項中之含氟之水的處 理方法,其中,投入上述反應塔之碳酸鈣粒子的量爲對於 被通水入該反應塔之含氟之水中的氟反應當量.而言爲0.9 〜1 .1倍當量者。 4. 如申請專利範圍第1項至第3項中任一項之含氟之 水的處理方法,其中設投入上述反應塔之碳酸鈣粒子的投 入量爲控制使其成爲自該反應塔被取出之處理水的pH値6 以下者。 5. 如申請專利範圍第4項之含氟之水的處理方法,其 使投入上述反應塔之碳酸鈣粒子的投入量控制爲自該反應 塔被取出之處理水的pH値可成爲4.5〜5者。 6. 如申請專利範圍第1項至第5項中任一項的含氟之 水的處理方法,其中上述碳酸鈣粒子之粒徑爲0.05mm以下 者。 7. 如申請專利範圍第6項之含氟之水的處理方法,其 -21 - 201223881 中上述碳酸鈣粒子之平均粒徑爲o.oi 〜0.03mm者。 8-如申請專利範圍第1項至第7項中任一項的含氟之 水的處理方法,其係經過上述反應塔內上部所設置之筒狀 碳酸鈣粒子投入構件的筒內投入上述碳酸鈣粒子的方法, 其中,該筒狀之碳酸鈣粒子之投入構件的上端係比該反應 塔之上部水面更向上方突出,下端係位於較該反應塔之處 理水取出部水位更爲下方30cm以上之位置者》 9. 如申請專利範圍第8項之含氟之水的處理方法,其 中上述碳酸鈣粒子投入構件的下端與上述反應塔之處理水 取出部水位間的距離1^爲25〜100cm,爲上述反應塔之全 有效塔高L2之1/20〜1/5者。 10. 如申請專利範圍第8項或第9項中之含氟之水的處 理方法’其中對於有底圓筒形狀之上述反應塔,圓筒狀之 上述碳酸鈣粒子投入構件爲被設置爲同心狀,對於上述反 應塔之直徑(內徑)而言爲1/5〜1/10者。 1 1 ·如申請專利範圍第8項至第1 0項中任一項之含氟 之水的處理方法’其中有底圓筒形狀之上述反應塔的直徑 係爲300〜l5〇Omm ’上述含氟之水的向上流速爲150〜 5000L/h’上述碳酸鈣粒子的投入量爲3〜l〇〇L/h者。 12·如申請專利範圍第8項至第10項中任一項之含氟 之水的處理方法,其中有底圓筒形狀之上述反應塔的直徑 爲1500〜3000mm ’上述含氟之水的向上流速爲5〇〇〇〜 20000L/h,上述碳酸鈣粒子的投入量爲1〇〇〜400L/h者。 13.如申請專利範圍第8項至第10項中任一項之含氟 -22- S 201223881 之水的處理方法,其中有底圓筒形狀之上述反應塔的直徑 爲3000〜50000mm,上述含氟之水的向上流速爲2000〜 60000L/h,上述碳酸鈣粒子的投入量爲400〜l 200L/h者。 14. 如申請專利範圍第1項至第13項中任一項之含氟 之水的處理方法,其中以一過式將上述含氟之水通水入上 述反應塔者。 15. 如申請專利範圍第1項至第14項中任一項之含氟 之水的處理方法,其中直列地連結2塔以上之反應塔,依 順序自第一段之反應塔將上述含氟之水通入各反應塔,當 該第一段反應塔之流入水的水質與流出水之水質大約相同 之後,中止對該第一段反應塔的通水,改換成對第二段反 應塔的通水取出該第一段反應塔內之含氟化鈣之粒子,以 該第一段之反應塔做爲上述二塔以上之反應塔的最後段反 應塔,重覆依序通水之工程,成爲一種隨輪轉動方式的通 水方法,對於該含氟之水被通入水的最後段反應塔投入上 述碳酸鈣粒子者。 16. 如申請專利範圍第15項之含氟之水的處理方法, 其中投入上述碳酸鈣粒子的最後段反應塔係在上述含氟之 水通水之前,在不會預先形成碳酸鈣塡充層,進行上述含 氟之水的通水與投入碳酸鈣粒子者。 17. 如申請專利範圍第15項或第16項中之含氟之水 的處理方法,其中在上述最後段的反應塔中,含有前段反 應塔之處理水的氟濃度1〇〇〇〜30000m g/L的含氟之水,以 一過式向著上方被流通入水者。 -23-201223881 VII. Patent application scope: 1. A method for treating fluorine-containing water, characterized in that water is introduced into the lower part of the reaction tower to pass water into the fluorine-containing water, so that the calcium carbonate particles in the reaction tower and the fluorine-containing one The fluorine reaction in the water is carried out by removing the fluorine as calcium fluoride, and in the treatment method of removing the fluorine-containing water from the fluorine-treated water from the upper portion of the reaction tower, the reaction is carried out by the water passing through the fluorine-containing water. The tower is a person who inputs calcium carbonate particles from the upper part of the reaction tower. 2. The method for treating a fluorine-containing water according to the first aspect of the invention, wherein the calcium carbonate particles are introduced into the reaction column as a powder. 3. The method for treating water containing fluorine in the first or second aspect of the patent application, wherein the amount of calcium carbonate particles charged into the reaction column is for the water to be passed into the fluorine-containing water of the reaction column. The fluorine reaction equivalent is 0.9 to 1.1 times the equivalent. 4. The method for treating fluorine-containing water according to any one of claims 1 to 3, wherein the amount of calcium carbonate particles charged into the reaction column is controlled to be taken out from the reaction column. The pH of the treated water is below 値6. 5. The method for treating fluorine-containing water according to claim 4, wherein the amount of calcium carbonate particles charged into the reaction column is controlled so that the pH of the treated water taken out from the reaction column can be 4.5 to 5 By. 6. The method for treating fluorine-containing water according to any one of claims 1 to 5, wherein the calcium carbonate particles have a particle diameter of 0.05 mm or less. 7. The method for treating fluorine-containing water according to item 6 of the patent application, wherein the average particle diameter of the calcium carbonate particles in -21 - 201223881 is o. oi to 0.03 mm. The method for treating fluorine-containing water according to any one of the first to seventh aspects of the present invention, wherein the carbonic acid is introduced into a cylinder of a tubular calcium carbonate particle-receiving member provided in an upper portion of the reaction column The method of the calcium particles, wherein the upper end of the cylindrical calcium carbonate particle input member protrudes upward from the upper surface of the reaction tower, and the lower end is located more than 30 cm below the water level of the treated water extraction portion of the reaction tower. 9. The method of treating fluorine-containing water according to claim 8 wherein the distance between the lower end of the calcium carbonate particle input member and the water level of the treated water extraction portion of the reaction tower is 25 to 100 cm. It is 1/20~1/5 of the total effective tower height L2 of the above reaction tower. 10. The method for treating a fluorine-containing water in the eighth or ninth aspect of the patent application, wherein the cylindrical calcium carbonate particle-input member is set to be concentric for the reaction column having a bottomed cylindrical shape. The shape is 1/5 to 1/10 of the diameter (inner diameter) of the above reaction column. 1 1 The method for treating a fluorine-containing water according to any one of the items 8 to 10 of the patent application, wherein the diameter of the reaction column having a bottomed cylindrical shape is 300 to 15 〇 Omm. The upward flow rate of the fluorine water is 150 to 5000 L/h. The input amount of the above calcium carbonate particles is 3 to 1 〇〇L/h. The method for treating fluorine-containing water according to any one of claims 8 to 10, wherein the reaction column having a bottomed cylindrical shape has a diameter of 1500 to 3000 mm. The flow rate is 5 〇〇〇 to 20000 L/h, and the input amount of the above calcium carbonate particles is 1 〇〇 to 400 L/h. The method for treating water containing fluorine-22-S 201223881 according to any one of claims 8 to 10, wherein the reaction column having a bottomed cylindrical shape has a diameter of 3000 to 50000 mm, and the above-mentioned The upward flow rate of the fluorine water is 2000 to 60000 L/h, and the input amount of the calcium carbonate particles is 400 to 1 200 L/h. 14. The method for treating fluorine-containing water according to any one of claims 1 to 13, wherein the fluorine-containing water is passed through the reaction column in a one-pass manner. [15] The method for treating fluorine-containing water according to any one of claims 1 to 14, wherein the reaction column of two or more columns is connected in series, and the fluorine is sequentially supplied from the reaction column of the first stage. The water is passed into each reaction tower. When the water quality of the inflow water of the first reaction tower is about the same as the water quality of the effluent water, the water flowing to the first reaction tower is suspended, and the second reaction tower is replaced. The water passing through the first stage of the reaction tower removes the particles of calcium fluoride, and the reaction tower of the first stage is used as the last reaction tower of the reaction tower above the two towers, and the engineering of repeating the water sequentially It is a water-passing method for the rotation of the wheel, and the calcium carbonate particles are put into the last reaction column in which the fluorine-containing water is introduced into the water. 16. The method for treating fluorine-containing water according to claim 15 wherein the last stage of the reaction of the calcium carbonate particles is before the water of the fluorine-containing water is passed, and the calcium carbonate filling layer is not formed in advance. , the water passing through the fluorine-containing water and the calcium carbonate particles are introduced. 17. The method for treating fluorine-containing water according to claim 15 or 16, wherein in the reaction column of the last stage, the fluorine concentration of the treated water containing the preceding reaction column is from 1 300 to 30000 m g /L of the fluorine-containing water, which is circulated into the water in one pass. -twenty three-
TW100124977A 2010-07-28 2011-07-14 Treatment of fluorine - containing water TWI568682B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2010169378A JP5644236B2 (en) 2010-07-28 2010-07-28 Fluorine-containing water treatment method

Publications (2)

Publication Number Publication Date
TW201223881A true TW201223881A (en) 2012-06-16
TWI568682B TWI568682B (en) 2017-02-01

Family

ID=45529803

Family Applications (1)

Application Number Title Priority Date Filing Date
TW100124977A TWI568682B (en) 2010-07-28 2011-07-14 Treatment of fluorine - containing water

Country Status (5)

Country Link
JP (1) JP5644236B2 (en)
KR (1) KR20130119843A (en)
CN (1) CN102917987A (en)
TW (1) TWI568682B (en)
WO (1) WO2012014582A1 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103011453B (en) * 2012-12-08 2014-01-22 北京国环清华环境工程设计研究院有限公司 Processing method for fluoride waste water in production of solar cells

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0651185B2 (en) * 1984-04-25 1994-07-06 三菱重工業株式会社 Flue gas desulfurization wastewater treatment equipment
JP3550713B2 (en) * 1994-03-07 2004-08-04 栗田工業株式会社 Calcium fluoride recovery device
TW310313B (en) * 1995-06-30 1997-07-11 Ind Tech Res Inst Apparatus provided with a fluidized bed crystallizer for treating wastewater
JPH11157834A (en) * 1997-12-01 1999-06-15 Ultla Clean Technology Kaihatsu Kenkyusho:Kk Resource recovering device
JP3483482B2 (en) * 1998-04-22 2004-01-06 富士通株式会社 Fluorine-containing water treatment method
JP2000070962A (en) * 1998-08-27 2000-03-07 Japan Organo Co Ltd Treatment of waste water containing fluorine
CN1185171C (en) * 2001-12-20 2005-01-19 南化集团研究院 Treating method for high fluorice acid waste water
JP4880656B2 (en) * 2008-09-30 2012-02-22 オルガノ株式会社 Water treatment apparatus and water treatment method

Also Published As

Publication number Publication date
WO2012014582A1 (en) 2012-02-02
JP2012030143A (en) 2012-02-16
KR20130119843A (en) 2013-11-01
CN102917987A (en) 2013-02-06
TWI568682B (en) 2017-02-01
JP5644236B2 (en) 2014-12-24

Similar Documents

Publication Publication Date Title
CN108128961A (en) Brine waste zero emission method and system
JP5440095B2 (en) Method and apparatus for treating fluorine-containing water
CN106630084A (en) Method and system for treating high-fluorine high-hardness wastewater by two-stage two-phase fluidized bed through self crystallization
CN106746113A (en) A kind of photovoltaic industry fluoride waste resource and the technique and system of reuse
US9995121B2 (en) Selective removal of silica from silica containing brines
JP4880656B2 (en) Water treatment apparatus and water treatment method
CN208008627U (en) Brine waste zero emission system
CN109928563A (en) A kind of shale gas well-drilling waste water processing method
CN105129832B (en) The method that liquid calcium chloride is continuously produced using fluorine-containing by-product waste hydrochloric acid
TW201223881A (en) Method for treating fluorine-containing water
CN107162279A (en) A kind of cleaning system and purification method for handling high-concentration fluorine-contained waste liquid
CN103723861B (en) Filter device
JP7206061B2 (en) Method for treating liquid to be treated
CN207108677U (en) A kind of cleaning system for handling high-concentration fluorine-contained waste liquid
CN206580692U (en) A kind of photovoltaic industry fluoride waste recycling and the system of reuse
CN204958619U (en) Adopt tubular micro -filtration membrane's fluoride waste processing system
JP2010221115A (en) Method and apparatus for treating fluorine-containing waste water
CN114604980A (en) Raw water heating and hard water removing treatment device
JP3559789B2 (en) Calcium fluoride recovery method
JP2013081886A (en) Treatment method and treatment apparatus of wastewater containing high-concentration calcium and alkali
US20200131038A1 (en) Method for extracting iodine from an aqueous solution
CN108545888A (en) A kind of recycling of uns-dimethylhydrazine industrial wastewater and processing combination process
CN208829414U (en) Reverse osmosis concentrated water removes hardness system
EA045859B1 (en) METHOD FOR PRODUCING SALT WATER IN AN UNDERGROUND SALT CAVERN
TWI642631B (en) Fluorine-containing water treatment method and treatment device

Legal Events

Date Code Title Description
MM4A Annulment or lapse of patent due to non-payment of fees