TW201336788A - Fluorine recovery device, fluorine recovery system, and fluorine recovery method - Google Patents

Fluorine recovery device, fluorine recovery system, and fluorine recovery method Download PDF

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TW201336788A
TW201336788A TW101133795A TW101133795A TW201336788A TW 201336788 A TW201336788 A TW 201336788A TW 101133795 A TW101133795 A TW 101133795A TW 101133795 A TW101133795 A TW 101133795A TW 201336788 A TW201336788 A TW 201336788A
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calcium carbonate
water
filter
fluoride
fluorine
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TW101133795A
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Chinese (zh)
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Kenji Tsutsumi
Atsushi Yamazaki
Taro Fukaya
Ichiro Yamanashi
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Toshiba Kk
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    • 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
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/20Halides
    • C01F11/22Fluorides
    • 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
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • C02F2101/14Fluorine or fluorine-containing compounds

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  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)
  • Filtration Of Liquid (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)

Abstract

A fluorine recovery device as an embodiment of the present invention includes; a precipitation tank in which calcium carbonate is reacted with fluorine ions contained in water being treated, wherein calcium carbonate is introduced in excess relative to the amount of fluorine ions contained in water being treated, thereby precipitating calcium fluoride and obtaining primary treated water; and a solid/liquid separator in which the primary treated water containing calcium fluoride and calcium carbonate is filtered to form, on the filter, a mixed cake layer having accumulated calcium fluoride and calcium carbonate.

Description

氟回收裝置、氟回收系統及氟回收方法 Fluorine recovery unit, fluorine recovery system and fluorine recovery method 〔相關申請之引用〕 [reference to relevant application]

本申請是以日本平成24年3月21日所申請之先行技術日本專利申請第2012-055945號的優先權利益為基礎,並且,追求該優先權之利益,引用其內容全部包括在本申請說明書中。 The present application is based on the priority benefit of the prior art Japanese Patent Application No. 2012-055945, filed on March 21, 2014, and the benefit of the priority, the entire contents of which are incorporated herein by reference. in.

本發明的實施形態是關於氟回收裝置、氟回收系統及氟回收方法。 Embodiments of the present invention relate to a fluorine recovery device, a fluorine recovery system, and a fluorine recovery method.

最近,由於工業發達及人口增加以致水資源有效利用成為一種需求。因此,工業排水等之排水的再利用就變成非常重要。為了要使排水可再利用是需要水的淨化即需要從水中分離其他的物質。要使其他物質從液體分離的方法,例如已知有膜分離、離心分離、活性碳吸附、臭氧處理及利用凝集使浮游物質去除的方法。 Recently, the efficient use of water resources has become a demand due to industrial development and population growth. Therefore, the reuse of drainage such as industrial drainage becomes very important. In order to make the drainage reusable, it is necessary to purify the water, that is, to separate other substances from the water. For the method of separating other substances from the liquid, for example, membrane separation, centrifugation, activated carbon adsorption, ozone treatment, and a method of removing suspended matter by agglutination are known.

利用上述的方法,就能夠去除水中所含有之磷或氮等影響環境較大的化學物質,或能夠去除水中分散的油類、粘土等。上述的方法當中,膜分離是屬於要去除水中之不溶物質時最常用的一種方法。從膜的保護觀點及從要提昇含有難脫水性之物質的水其過水速度的觀點來看,對於膜分離還是屢屢採用所謂預塗助濾劑過濾法及加助劑過濾法 之利用助濾劑的方法。 According to the above method, it is possible to remove chemical substances such as phosphorus or nitrogen which are contained in water, which are environmentally-sensitive, or to remove oils, clays, and the like which are dispersed in water. Among the above methods, membrane separation is one of the most common methods for removing insoluble materials from water. From the viewpoint of membrane protection and from the viewpoint of improving the water passing rate of water containing substances which are difficult to dehydrate, the so-called pre-coating filter filtration method and additive filtration method are often used for membrane separation. A method of using a filter aid.

另一方面,要從水中去除氟離子的方法,是有將氟離子以氟化鈣析出的方法,或以聚氯化鋁吸附氟離子的方法,或利用高分子凝集劑使氟化鈣凝集藉此回收氟化鈣的方法。 On the other hand, a method for removing fluoride ions from water is a method of precipitating fluoride ions with calcium fluoride, or a method of adsorbing fluoride ions by polyaluminum chloride, or agglomerating calcium fluoride by using a polymer aggregating agent. This method of recovering calcium fluoride.

例如專利文獻1中,揭示有使水中的氟以氟化鈣析出,然後添加凝集劑藉此回收氟化鈣的技術。此外,專利文獻2中,揭示有將析晶反應槽所生成之氟化鈣的一部份回送至析晶反應槽藉此對氟化鈣進行再析晶的技術。另外,專利文獻3中,揭示有使鈣和鋁鹽形成反應,然後又添加高分子凝集劑藉此回收氟或/及磷的技術。 For example, Patent Document 1 discloses a technique in which fluorine in water is precipitated as calcium fluoride, and then a flocculating agent is added to recover calcium fluoride. Further, Patent Document 2 discloses a technique in which a part of calcium fluoride produced by a crystallization reaction tank is returned to a crystallization reaction tank to recrystallize calcium fluoride. Further, Patent Document 3 discloses a technique of reacting calcium and an aluminum salt, and then adding a polymer flocculant to recover fluorine or/and phosphorus.

〔先行技術獻〕 [first technical offer] 〔專利文獻〕 [Patent Document]

〔專利文獻1〕日本特開2010-207755號公報 [Patent Document 1] Japanese Patent Laid-Open Publication No. 2010-207755

〔專利文獻2〕日本特開2010-110688號公報 [Patent Document 2] Japanese Patent Laid-Open Publication No. 2010-110688

〔專利文獻3〕日本特開2005-296837號公報 [Patent Document 3] Japanese Patent Laid-Open Publication No. 2005-296837

專利文獻1記載的技術,是藉由高分子凝集劑的混合,使所析出的氟化鈣成為較大的絮凝體,藉此回收氟化鈣。該方法,由於回收之氟化鈣的純度會降低,因此就難以使氟化鈣回收成為有價物。此外,該方法,由於要混入有高分子凝集劑因此污泥量就會增加。 The technique described in Patent Document 1 recovers calcium fluoride by mixing the polymer flocculating agent and causing the precipitated calcium fluoride to become a large floc. In this method, since the purity of the recovered calcium fluoride is lowered, it is difficult to recover calcium fluoride as a valuable substance. Further, in this method, since the polymer aggregating agent is mixed, the amount of sludge increases.

另外,專利文獻2記載的技術,是將所析出之氟化鈣的一部份回送至析出槽做為結晶核利用,將結晶成長後的氟化鈣回收成為大的粒子。該方法雖然也可不使用高分子凝集劑,但需將氟化鈣的一部份回送至析晶反應槽因此處理效率就會降低,並且需要時間讓結晶成長為足夠大。 Further, in the technique described in Patent Document 2, a part of the precipitated calcium fluoride is returned to the precipitation tank as a crystal nucleus, and the calcium fluoride after the crystal growth is recovered into large particles. Although the method does not use a polymer flocculant, it is necessary to return a part of the calcium fluoride to the devitrification reaction tank, so that the treatment efficiency is lowered, and it takes time to allow the crystal to grow sufficiently large.

此外,專利文獻3記載的技術,是揭示著利用鋁鹽(聚氯化鋁等)回收水中之氟離子的方法。但是,鋁鹽是非常不易與水分離,必須併用高分子凝集劑。 Further, the technique described in Patent Document 3 discloses a method of recovering fluoride ions in water using an aluminum salt (polyaluminum chloride or the like). However, the aluminum salt is very difficult to separate from water, and a polymer flocculant must be used in combination.

基於以上所述,水中的氟處理是屬於需要有複數作業之煩雜的處理。其原因在於:生成的氟化鈣粒子徑小以致氟化鈣的分離困難;及添加在水中之鋁鹽的去除困難。 Based on the above, the fluorine treatment in water is a troublesome process requiring a plurality of operations. The reason for this is that the generated calcium fluoride particles have a small diameter so that separation of calcium fluoride is difficult; and removal of the aluminum salt added in water is difficult.

本發明的實施例,是提供一種能夠有效率分離粒子徑小的氟化鈣,並且不必使用添加藥劑就能夠有效率去除氟的氟回收裝置、氟回收系統及氟回收方法。 An embodiment of the present invention provides a fluorine recovery device, a fluorine recovery system, and a fluorine recovery method capable of efficiently separating calcium fluoride having a small particle diameter and efficiently removing fluorine without using a chemical.

本發明實施形態的氟回收裝置,具備有析出槽和固液分離裝置。於析出槽中,是針對被處理水所含有的氟離子量以投入有過剩量之碳酸鈣的狀態使碳酸鈣和氟離子形成反應藉此析出氟化鈣生成初級處理水。此外,固液分離裝置,是構成為對含有氟化鈣及碳酸鈣之初級處理水進行濾餅過濾,藉此在濾器上形成有氟化鈣及碳酸鈣所堆積的混合濾餅層。 The fluorine recovery apparatus according to the embodiment of the present invention includes a precipitation tank and a solid-liquid separation device. In the precipitation tank, calcium fluoride and fluoride ions are reacted in a state in which an excessive amount of calcium carbonate is contained in the water to be treated, thereby precipitating calcium fluoride to form primary treated water. Further, the solid-liquid separation device is configured to filter the cake with the primary treated water containing calcium fluoride and calcium carbonate, thereby forming a mixed cake layer in which calcium fluoride and calcium carbonate are deposited on the filter.

〔發明之實施形態〕 [Embodiment of the Invention]

氟回收裝置,具備有析出槽和固液分離裝置。於析出槽中,是針對含有氟離子的被處理水和被處理水所含有的氟離子量投入過剩量之碳酸鈣,使碳酸鈣和氟離子形成反應藉此析出氟化鈣生成初級處理水。固液分離裝置,具有濾器,該濾器可將含有氟化鈣及碳酸鈣之初級處理水過濾成濾餅藉此在濾器上形成有氟化鈣及碳酸鈣所堆積的混合濾餅層。 The fluorine recovery device includes a precipitation tank and a solid-liquid separation device. In the precipitation tank, calcium carbonate and fluoride ions are reacted with respect to the amount of fluorine ions contained in the water to be treated containing the fluoride ions and the water to be treated, and calcium fluoride and fluoride ions are reacted to precipitate calcium fluoride to form primary treated water. The solid-liquid separation device has a filter that filters a primary treated water containing calcium fluoride and calcium carbonate into a filter cake to form a mixed cake layer in which calcium fluoride and calcium carbonate are deposited on the filter.

其次參照圖面對本發明實施形態進行說明。第1圖為表示本實施形態之氟去除系統的概要構成方塊圖。 Next, an embodiment of the present invention will be described with reference to the drawings. Fig. 1 is a schematic block diagram showing a fluorine removal system of the present embodiment.

氟去除系統10,具備有析出槽11、固液分離裝置15、泥漿回收槽16及脫水槽17。於析出槽11中,是要使含有的氟離子的被處理水INF和碳酸鈣CC形成反應藉此析出氟化鈣(CaF2)生成初級處理水。固液分離裝置15,具有濾器13和洗淨機構14。濾器13,是藉由過濾初級處理水INF1來進行固液分離,以在濾器13上形成濾餅層CK。洗淨機構14,是對濾餅層CK散佈(噴射)洗淨水CW藉此獲得由濾餅層CK和洗淨液CW混合形成濃縮泥漿SL,然後將濃縮泥漿SL取出至固液分離裝置15外。泥漿回收槽16,是回收從固液分離裝置15取出的濃縮泥漿SL。脫水槽17,是對回收在泥漿回收槽16的濃縮泥漿SL進行脫水。 The fluorine removal system 10 includes a precipitation tank 11, a solid-liquid separation device 15, a slurry recovery tank 16, and a dewatering tank 17. In the precipitation tank 11, the treated water INF containing the fluoride ions and the calcium carbonate CC are reacted to precipitate calcium fluoride (CaF 2 ) to form primary treated water. The solid-liquid separation device 15 has a filter 13 and a cleaning mechanism 14. The filter 13 performs solid-liquid separation by filtering the primary treated water INF1 to form a cake layer CK on the filter 13. The cleaning mechanism 14 disperses (sprays) the washing water CW to the cake layer CK, thereby obtaining a concentrated slurry SL by mixing the cake layer CK and the cleaning liquid CW, and then taking the concentrated mud SL to the solid-liquid separation device 15 outer. The mud recovery tank 16 recovers the concentrated mud SL taken out from the solid-liquid separation device 15. The dewatering tank 17 dehydrates the concentrated mud SL recovered in the mud recovery tank 16.

於固液分離裝置15中,通過濾器13後之處理水PW 的一部份,是經由洗淨機構14後做為洗淨水CW使用。其結果,處理水PW所含有之未反應的氟離子,就會和濾餅槽所含有之未反應的碳酸鈣形成反應藉此能夠形成氟化鈣並且能夠抑制實效性之處理水的增加。 In the solid-liquid separation device 15, the treated water PW after passing through the filter 13 A part of it is used as a washing water CW after the washing mechanism 14. As a result, the unreacted fluorine ions contained in the treated water PW react with the unreacted calcium carbonate contained in the filter cake tank, whereby calcium fluoride can be formed and the increase in the effective treated water can be suppressed.

此外,處理水PW之其他的部份,是被供應至泥漿回收槽16做為濃縮泥漿SL的濃度調整用水DW使用。再加上,處理水PW中的氟離子濃度已經非常低,因此處理水PW是能夠直接成為排水排出。 Further, the other portion of the treated water PW is supplied to the mud recovery tank 16 as the concentration adjustment water DW of the concentrated mud SL. Further, since the concentration of fluorine ions in the treated water PW is already very low, the treated water PW can be directly discharged as drainage.

首先,對固液分離裝置15進行說明。 First, the solid-liquid separation device 15 will be described.

於本實施形態中,固液分離裝置15,是使用濾器13成水平配置的過濾器。如此一來,就能夠使濾餅層CK穩定以致處理水的水質穩定。 In the present embodiment, the solid-liquid separation device 15 is a filter that is horizontally arranged using the filter 13. In this way, the cake layer CK can be stabilized so that the water quality of the treated water is stabilized.

固液分離裝置15,如上述具備有洗淨機構14。洗淨機構14,具備有泵浦21和洗淨噴嘴單元22。洗淨噴嘴單元22,是將透過泵浦21供應過來的洗淨水CW散佈在濾餅層CK上使濾餅層CK成為濃縮泥漿SL經由固液分離裝置15的泥漿排出口15A排出至泥漿回收槽16。 The solid-liquid separation device 15 is provided with the cleaning mechanism 14 as described above. The cleaning mechanism 14 is provided with a pump 21 and a washing nozzle unit 22. The washing nozzle unit 22 disperses the washing water CW supplied from the permeate pump 21 on the cake layer CK, and causes the cake layer CK to be the concentrated mud SL to be discharged to the mud through the mud discharge port 15A of the solid-liquid separating device 15. Slot 16.

其次,對濾器13的構成進行說明。 Next, the configuration of the filter 13 will be described.

濾器13具有濾布,濾布可根據處理水的水質要求加以選擇。本實施形態中,是使用透氣度為30~1500cc/cm2‧min的濾布。於此,透氣性是根據弗雷澤式法(譯者備註:弗雷澤式法原文為形法)測定出。具體而言,若濾器以織物構成時,就能夠利用株式會社安田精機製作所的弗雷澤型透氣性測試機(商品名:形 通氣度試驗機)等進行測定。 The filter 13 has a filter cloth which can be selected according to the water quality requirements of the treated water. In the present embodiment, a filter cloth having a gas permeability of 30 to 1500 cc/cm 2 ‧ min is used. Here, the permeability is based on the Frazier method (Translator's Note: Frazier method Shape method) was determined. Specifically, when the filter is made of a woven fabric, the Fraser type gas permeability tester manufactured by Yasuda Seiki Co., Ltd. can be used. The air permeability tester) was measured.

濾器13,例如可利用脫水機用的濾布。即,可使用由聚丙烯系的寶綸(商標登記)、聚酯系的帝特綸(商標登記)、聚醯胺系的尼龍(商標登記)等材質形成的濾布做為濾器13。此外,濾布,又以濾餅層GK之剝離性良好的材質為佳。例如聚丙烯不僅價格便宜,濾餅層CK回收後的差壓也較為穩定,且劣化也較少,因此就容易使用在水處理。基於此,濾布就以採用聚丙烯纖維為佳。 As the filter 13, for example, a filter cloth for a dehydrator can be used. In other words, a filter cloth made of a material such as polypropylene-based stellite (trademark registration), polyester-based texa (trademark registration), or polyamide-based nylon (trademark registration) can be used as the filter 13. Further, the filter cloth is preferably a material having a good peeling property of the filter cake layer GK. For example, polypropylene is not only inexpensive, but the differential pressure after recovery of the cake layer CK is also relatively stable and less deteriorated, so that it is easy to use in water treatment. Based on this, it is preferred to use a polypropylene fiber for the filter cloth.

此外,濾布的織法,是有平紋織法、斜紋織法、緞紋織法等各種的織法。濾布可選用任一織法。即,在選用濾布時,所期望之濾布的透氣性及織法,只要以製造成本等的觀點加以適當選擇即可。 Further, the weaving method of the filter cloth is various weaves such as a plain weave, a twill weave, and a satin weave. Any weave can be used for the filter cloth. In other words, when the filter cloth is selected, the gas permeability and the weaving method of the desired filter cloth may be appropriately selected in view of the production cost and the like.

濾布的材質特別是以聚丙烯為佳,此外濾布的織法以平紋織法為佳。濾布也可視需求施以軋光加工處理。 The material of the filter cloth is particularly preferably polypropylene, and the weave of the filter cloth is preferably a plain weave. The filter cloth can also be subjected to calender processing as required.

本實施形態中,是使投入在析出槽11之過剩量的碳酸鈣以濾餅層CK形成在濾器(濾布)13上,將該濾餅層CK做為一種濾器使用。即,實施形態中,是執行所謂的濾餅過濾。由於初級處理液含有碳酸鈣,因此碳酸鈣就會運作成為助濾劑,能夠提昇過濾流速。 In the present embodiment, the excess amount of calcium carbonate charged in the deposition tank 11 is formed on the filter (filter cloth) 13 by the cake layer CK, and the cake layer CK is used as a filter. That is, in the embodiment, so-called filter cake filtration is performed. Since the primary treatment solution contains calcium carbonate, the calcium carbonate acts as a filter aid and increases the filtration flow rate.

如以上所述,於本實施形態,對於氟離子要和鈣形成反應時的鈣源,是採用碳酸鈣。碳酸鈣,由於不易溶於水,因此反應會產生在其表面,使碳酸鈣的表面生成氟化鈣,以致氟化鈣會在剝落分散在水中。當氟化鈣剝落分散在水中時,氟化鈣是會成為非常細的粒子分散在水中。 As described above, in the present embodiment, calcium carbonate is used for the calcium source when the fluoride ion is reacted with calcium. Calcium carbonate, because it is not easily soluble in water, reacts on the surface to form calcium fluoride on the surface of calcium carbonate, so that calcium fluoride is dispersed in water in the form of flaking. When calcium fluoride is peeled off and dispersed in water, calcium fluoride is a very fine particle dispersed in water.

基於此,所析出的氟化鈣就非常難以固液分離。因此,先前技術是以添加陽離子系聚合物等來形成絮凝體,藉此使所生成之氟化鈣的全量分離。但是,本實施形態中是根據處理水濃度選定濾器13藉此就能夠使析出物直接脫水,因此本實施例就不需要這以外的操作。 Based on this, the precipitated calcium fluoride is very difficult to separate from solid and liquid. Therefore, the prior art has been to form a floc by adding a cationic polymer or the like, thereby separating the entire amount of calcium fluoride formed. However, in the present embodiment, the filter 13 is selected based on the treated water concentration, whereby the precipitate can be directly dehydrated. Therefore, the present embodiment does not require an operation other than this.

為了提昇上述助濾劑的運作,於本實施形態,要投入在析出槽11之碳酸鈣CC的粒子徑為5μm~200μm的範圍。碳酸鈣CC的粒子徑若未滿5μm時,雖然反應性會提昇,但執行性的透氣度(流量)會降低,導致固液分離的效率即過濾效率降低。再加上,濾布產生堵塞的結果恐怕過濾壽命也會降低。此外,碳酸鈣CC的粒子徑若超過200μm時,雖然透氣度(流量)十足,但氟化鈣的析出反應,只有反應在碳酸鈣的表面,因此每單位質量的實效性反應面積就會降低,相對於同量的氟離子就需要使用更多量的碳酸鈣。 In the present embodiment, the particle diameter of the calcium carbonate CC to be introduced into the deposition tank 11 is in the range of 5 μm to 200 μm. When the particle diameter of the calcium carbonate CC is less than 5 μm, the reactivity is improved, but the workability (flow rate) is lowered, and the efficiency of solid-liquid separation, that is, the filtration efficiency is lowered. In addition, as a result of the clogging of the filter cloth, the filtration life may be lowered. Further, when the particle diameter of the calcium carbonate CC exceeds 200 μm, although the gas permeability (flow rate) is sufficient, the precipitation reaction of calcium fluoride is only reacted on the surface of the calcium carbonate, so that the effective reaction area per unit mass is lowered. A larger amount of calcium carbonate is required relative to the same amount of fluoride ion.

另,於本實施形態,主要是使用5μm~200μm之粒子徑範圍篩選後的碳酸鈣,但不排除還包括這以外之粒子徑的碳酸鈣。 Further, in the present embodiment, calcium carbonate after the particle diameter range of 5 μm to 200 μm is mainly used, but calcium carbonate having a particle diameter other than the above is not excluded.

其次對本實施形態的概要動作進行說明。 Next, the outline operation of this embodiment will be described.

首先,對析出槽11供應含有氟離子的被處理水INF,又針對氟離子的量投入過剩量的碳酸鈣CC進行混合。接著經過指定時間之後,使被處理水INF中混濁有碳酸鈣CC的初級處理水INF1(混濁液)在加壓下於濾器13進行水的過濾。藉此使初級處理水INF1中的氟化鈣及 過剩的碳酸鈣CC分別濾出,在濾器13上殘留氟化鈣及碳酸鈣CC藉此形成濾餅層CK。於濾餅層CK,是混合有碳酸鈣及氟化鈣。 First, the water to be treated INF containing fluorine ions is supplied to the deposition tank 11, and an excess amount of calcium carbonate CC is added to the amount of fluorine ions to be mixed. After the lapse of the lapse of a predetermined period of time, the primary treated water INF1 (turbid liquid) in which the calcium carbonate CC is turbid in the water to be treated INF is filtered under pressure in the filter 13 to perform water filtration. Thereby using calcium fluoride in the primary treated water INF1 Excess calcium carbonate CC is separately filtered off, and calcium fluoride and calcium carbonate CC remain on the filter 13 to form a cake layer CK. In the cake layer CK, calcium carbonate and calcium fluoride are mixed.

於此,濾餅層CK,是利用外力的作用使其形成及保持著。例如:將濾器13配置成封住固液分離裝置15構成用之指定容器15B的容器口15C,使碳酸鈣及氟化鈣殘留並堆積在該配置狀下態的濾器13上。於該形態時,利用來自於容器15B之壁面的外力及位於上方之氟化鈣及碳酸鈣的重量造成朝向下方的外力(重力),就能夠使濾餅層CK形成及保持在濾器13上。另,濾餅層CK的厚度會因為要處理的液量而有所改變,但大概是0.1~20mm程度。 Here, the cake layer CK is formed and held by the action of an external force. For example, the filter 13 is disposed so as to seal the container opening 15C of the designated container 15B for constituting the solid-liquid separation device 15, and calcium carbonate and calcium fluoride remain and are deposited on the filter 13 in the down state. In this form, the filter cake layer CK can be formed and held on the filter 13 by an external force (gravity) directed downward from the wall surface of the container 15B and the weight of the calcium fluoride and calcium carbonate located above. In addition, the thickness of the cake layer CK may vary depending on the amount of liquid to be treated, but it is about 0.1 to 20 mm.

經由上述過程從初級處理水INF1分離出來之含有氟化合物的濾餅層CK是利用洗淨機構14進行洗淨。於本實施形態中,是利用洗淨機構14進行設有濾器13之容器15B內的濾餅層CK之洗淨。洗淨也可在其他的容器內進行。當濾餅層CK要在其它的容器內進行洗淨時,是利用另項設置的洗淨機構將濾餅層CK分解成泥漿狀之後,再對分解成泥沙狀的濾餅層CK進行輸出。於本實施形態中,是使用水進行洗淨,但也可使用界面活性劑或有機溶媒進行洗淨。 The filter cake layer CK containing the fluorine compound separated from the primary treated water INF1 by the above process is washed by the cleaning mechanism 14. In the present embodiment, the cleaning of the cake layer CK in the container 15B provided with the filter 13 is performed by the cleaning mechanism 14. Washing can also be carried out in other containers. When the filter cake layer CK is to be washed in another container, the filter cake layer CK is decomposed into a slurry shape by a cleaning mechanism provided separately, and then the filter cake layer CK which is decomposed into a sediment is discharged. . In the present embodiment, the material is washed with water, but it may be washed with a surfactant or an organic solvent.

其次,將洗淨後的濃縮泥漿SL回收至泥漿回收槽16。另,也可將該濃縮泥漿SL通過篩網,對於不能通過篩網的液體是回送至析出槽。該篩選作業的追加是能夠使碳酸鈣做為有效率的利用。 Next, the washed concentrated sludge SL is recovered to the slurry recovery tank 16. Alternatively, the concentrated sludge SL may be passed through a screen and returned to the precipitation tank for liquid that cannot pass through the screen. The addition of this screening operation enables calcium carbonate to be used efficiently.

接著,將回收至泥漿回收槽16的濃縮泥漿SL移送至脫水機17,以脫水機17進行濃縮泥漿SL的脫水。脫水的方法並沒有特別限定。例如有脫水機17是利用壓濾脫水機直接回收碳酸鈣及氟化鈣的方法,或添加少量的高分子助劑回收碳酸鈣及氟化鈣的方法,或脫水機17是利用離心分離機回收碳酸鈣及氟化鈣的方法等。此外,壓濾脫水機由於不使用高分子助劑因此屬於有效的回收方法。 Next, the concentrated sludge SL recovered in the slurry recovery tank 16 is transferred to the dehydrator 17, and the dewatering machine 17 performs dehydration of the concentrated slurry SL. The method of dehydration is not particularly limited. For example, the dehydrator 17 is a method of directly recovering calcium carbonate and calcium fluoride by a filter press dehydrator, or a method of recovering calcium carbonate and calcium fluoride by adding a small amount of a polymer auxiliary agent, or the dehydrator 17 is recovered by a centrifugal separator. Calcium carbonate and calcium fluoride methods. In addition, the filter press dehydrator is an effective recovery method because it does not use a polymer additive.

其次,對比實施形態還為更詳細之實施例進行說明。 Next, the comparative embodiment will be described in more detail.

(針對濾布) (for filter cloth)

首先,為了檢討出最佳的濾布,就準備有以下4種的濾布FA~FD。 First, in order to review the optimum filter cloth, the following four kinds of filter cloths FA to FD are prepared.

濾布FA:寶綸製平紋織法的濾布(平均透氣度40cc/cm2‧min) Filter cloth FA: filter cloth of plain weave fabric (average air permeability 40cc/cm 2 ‧ min)

濾布FB:寶綸製斜紋織法的濾布(平均透氣度500cc/cm2‧min) Filter cloth FB: filter cloth of twill weave fabric (average air permeability 500cc/cm 2 ‧ min)

濾布FC:寶綸製平紋織法的濾布(平均透氣度24cc/cm2‧min) Filter cloth FC: filter cloth of plain weave fabric (average air permeability 24cc/cm 2 ‧min)

濾布FD:寶綸製緞紋織法的濾布(平均透氣度1800cc/cm2‧min) Filter cloth FD: filter cloth made of Baolun satin weave (average air permeability 1800cc/cm 2 ‧min)

(針對碳酸鈣) (for calcium carbonate)

其次,為了檢討出最佳的碳酸鈣粒子徑,就準備有以下5種粒徑的碳酸鈣CC1~CC5。所準備的碳酸鈣是平均粒 子徑2mm之重質碳酸鈣經粉碎及分級後的碳酸鈣。 Next, in order to review the optimum calcium carbonate particle diameter, the following five kinds of calcium carbonates CC1 to CC5 are prepared. The prepared calcium carbonate is the average grain Calcium carbonate after crushing and classification of heavy calcium carbonate having a diameter of 2 mm.

碳酸鈣CC1:碳酸鈣平均粒子徑5.5μm Calcium carbonate CC1: Calcium carbonate average particle diameter 5.5μm

碳酸鈣CC2:碳酸鈣平均粒子徑20μm Calcium carbonate CC2: Calcium carbonate average particle diameter 20μm

碳酸鈣CC3:碳酸鈣平均粒子徑200μm Calcium carbonate CC3: Calcium carbonate average particle diameter 200μm

碳酸鈣CC4:碳酸鈣平均粒子徑3μm Calcium carbonate CC4: Calcium carbonate average particle diameter 3μm

碳酸鈣CC5:碳酸鈣平均粒子徑300μm Calcium carbonate CC5: Calcium carbonate average particle diameter 300μm

〔實施例1〕 [Example 1]

於實施例1中,是使用第1圖所示之氟去除系統10進行氟去除。 In Example 1, fluorine removal was performed using the fluorine removal system 10 shown in Fig. 1.

首先,將含有氟離子的被處理水INF供應至析出槽11。接著,對析出槽11投入要做為鈣源的碳酸鈣CC,使其和被處理水INF混合,藉此生成初級處理水INF1。經過指定時間之後,將初級處理水INF1在加壓下供應至固液分離裝置15,對初級處理水INF1進行固液分離(過濾)。 First, the water to be treated INF containing fluorine ions is supplied to the precipitation tank 11. Next, calcium carbonate CC to be a calcium source is introduced into the precipitation tank 11 to be mixed with the water to be treated INF, whereby primary treated water INF1 is produced. After the lapse of the designated time, the primary treated water INF1 is supplied to the solid-liquid separation device 15 under pressure, and the primary treated water INF1 is subjected to solid-liquid separation (filtration).

於此,通過固液分離裝置15的處理水PW(濾液),是屬於氟離子已經去除之弱鹼性的處理液,能夠直接成為排水。此外如以上所述處理水PW的一部份是可做為固液分離裝置15的洗淨水CW使用,另外處理水PW的其他部份是可做為濃縮泥漿SL的濃度調整用水DW使用。 Here, the treated water PW (filtrate) passing through the solid-liquid separation device 15 is a weakly alkaline treatment liquid from which fluoride ions have been removed, and can be directly drained. Further, as described above, a part of the treated water PW can be used as the washing water CW of the solid-liquid separating device 15, and the other portion of the treated water PW can be used as the concentration adjusting water DW of the concentrated mud SL.

當初級處理水INF1的固液分離(過濾)結束時,在固液分離裝置15內的濾器13會殘留有所析出的氟化合物(主要為氟化鈣)及碳酸鈣的混合濾餅層CK。 When the solid-liquid separation (filtration) of the primary treated water INF1 is completed, the mixed filter cake layer CK of the precipitated fluorine compound (mainly calcium fluoride) and calcium carbonate remains in the filter 13 in the solid-liquid separation device 15.

為了洗淨混合濾餅層CK,是使洗淨機構14構成用之泵浦21及洗淨噴嘴單元22,從濾器13的斜上方散佈(供應)洗淨水SW使濾餅層CK崩潰,將濾餅層CK以濃縮泥漿SL的狀態經由固液分離裝置15的泥漿排出口15A排出(供應)至泥漿回收槽16。 In order to wash the mixed cake layer CK, the pump 21 and the cleaning nozzle unit 22 for constituting the cleaning mechanism 14 are disposed, and the washing water SW is scattered (supplied) from the upper side of the filter 13 to collapse the cake layer CK. The cake layer CK is discharged (supplied) to the mud recovery tank 16 via the slurry discharge port 15A of the solid-liquid separation device 15 in the state of the concentrated slurry SL.

如此一來,洗淨水SW的一部份,就會成為含有高濃度之氟化合物(氟化鈣及碳酸鈣)的濃縮泥漿(氟濃縮水)SL回收在泥漿回收槽16。 As a result, a part of the washing water SW becomes a concentrated mud (fluorine concentrated water) SL containing a high concentration of a fluorine compound (calcium fluoride and calcium carbonate), which is recovered in the slurry recovery tank 16.

回收在泥漿回收槽16的氟化鈣是和碳酸鈣一起供應至壓濾脫水機等的脫水機17內脫水成固形物回收。 The calcium fluoride recovered in the slurry recovery tank 16 is dehydrated into a solid matter recovery by being supplied to a dewatering machine 17 such as a filter press dehydrator together with calcium carbonate.

為了檢討上述構成之氟離子的回收效率,就準備好含有氟離子濃度為500mg/L的氟化氫水溶液做為被處理水INF。此外,成為處理完成之判斷基準的氟去除處理後之初級處理水INF1的氟離子濃度是設定成10mg/L以下。 In order to review the recovery efficiency of the fluorine ion having the above configuration, a hydrogen fluoride aqueous solution having a fluoride ion concentration of 500 mg/L is prepared as the water to be treated INF. In addition, the fluoride ion concentration of the primary treated water INF1 after the fluorine removal treatment which is the criterion for the completion of the treatment is set to 10 mg/L or less.

將碳酸鈣CC1以固形份量成為1000mg/L的狀態在被處理水INF中添加碳酸鈣,於析出槽11中進行10分鐘(=指定時間)攪拌之後就會生成初級處理水INF1。其結果,白色沉澱物析出,初級處理水INF1中的氟離子濃度為基準氟離子濃度(10mg/L)以下的8mg/L。 The calcium carbonate CC1 is added with calcium carbonate in the treated water INF in a state where the solid content is 1000 mg/L, and the primary treated water INF1 is generated after stirring in the precipitation tank 11 for 10 minutes (= designated time). As a result, the white precipitate precipitated, and the fluoride ion concentration in the primary treated water INF1 was 8 mg/L or less of the reference fluoride ion concentration (10 mg/L) or less.

然後,從析出槽11將含有白色沉澱物之混濁液即初級處理水INF1供應至固液分離裝置15,對初級處理水INF1進行了過濾。其結果,可確認處理水PW(過濾水)可回收有初級處理水INF1中98%以上的氟化合物(碳酸鈣和氟離子的反應物)。 Then, the primary treatment water INF1, which is a turbid liquid containing a white precipitate, is supplied from the deposition tank 11 to the solid-liquid separation device 15, and the primary treated water INF1 is filtered. As a result, it was confirmed that the treated water PW (filtered water) can recover 98% or more of the fluorine compound (reactant of calcium carbonate and fluoride ion) in the primary treated water INF1.

過濾處理後,從利用固液分離裝置15的洗淨機構14從濾器13的上部散佈供應洗淨水CW,使形成在濾器13上主要為氟化鈣及碳酸鈣之混合濾餅層即濾餅層CK崩潰,藉此使濾餅層CK以濃縮泥漿SL的狀態排出至泥漿回收槽14。 After the filtration treatment, the washing water CW is supplied from the upper portion of the filter 13 from the washing mechanism 14 using the solid-liquid separating device 15, so that the filter cake layer mainly composed of calcium fluoride and calcium carbonate formed on the filter 13 is a filter cake. The layer CK collapses, whereby the cake layer CK is discharged to the slurry recovery tank 14 in the state of the concentrated slurry SL.

然後,將泥漿回收槽14內的濃縮泥漿SL供應至脫水機17進行了濃縮泥漿SL的脫水處理。其結果,毫無問題可將氟化鈣及碳酸鈣回收成為固形物。 Then, the concentrated mud SL in the slurry recovery tank 14 is supplied to the dehydrator 17 to perform dehydration treatment of the concentrated slurry SL. As a result, calcium fluoride and calcium carbonate can be recovered as a solid matter without any problem.

〔實施例2〕 [Example 2]

使用與實施例1相同的裝置,除了使用濾布FB取代濾布FA以外,其他都和實施例1相同進行了測試。其結果,氟化合物的回收率約80%,處理水PW中的氟濃度為80~100mg/L。於實施例2中,相較於實施例1,該實施例2的固液分離裝置15的過水速度大致為2倍,因此裝置毫無問題能夠運轉。 The same apparatus as in Example 1 was used, and the same test as in Example 1 was carried out except that the filter cloth FB was used instead of the filter cloth FA. As a result, the recovery rate of the fluorine compound was about 80%, and the fluorine concentration in the treated water PW was 80 to 100 mg/L. In the second embodiment, the liquid-water separation speed of the solid-liquid separation device 15 of the second embodiment is substantially twice as high as that of the first embodiment, so that the apparatus can be operated without any problem.

〔實施例3〕 [Example 3]

使用與實施例1相同的裝置,除了使用碳酸鈣CC2取代碳酸鈣CC1以外,其他都和實施例1相同進行了測試。其結果,氟化合物的回收率約90%,處理水PW中的氟濃度為20~50mg/L。於實施例3中,相較於實施例1,該實施例3的固液分離裝置15的過水速度約為1.1倍,因此裝置毫無問題能夠運轉。 The same apparatus as in Example 1 was used, and the same test as in Example 1 was carried out except that calcium carbonate CC2 was used instead of calcium carbonate CC1. As a result, the recovery rate of the fluorine compound was about 90%, and the fluorine concentration in the treated water PW was 20 to 50 mg/L. In the third embodiment, the solid-water separation device 15 of the third embodiment has a water passing speed of about 1.1 times as compared with the first embodiment, so that the device can be operated without any problem.

〔實施例4〕 [Example 4]

使用與實施例1相同的裝置,除了使用碳酸鈣CC3取代碳酸鈣CC1以外,其他都和實施例1相同進行了測試。其結果,氟化合物的回收率約80%,處理水PW中的氟濃度為80~100mg/L。於實施例4中,相較於實施例1,該實施例4的固液分離裝置15的過水速度大致為2倍,因此裝置毫無問題能夠運轉。 The same apparatus as in Example 1 was used, and the same test as in Example 1 was carried out except that calcium carbonate CC3 was used instead of calcium carbonate CC1. As a result, the recovery rate of the fluorine compound was about 80%, and the fluorine concentration in the treated water PW was 80 to 100 mg/L. In the fourth embodiment, the liquid-water separation speed of the solid-liquid separation device 15 of the fourth embodiment is substantially twice as high as that of the first embodiment, so that the apparatus can be operated without any problem.

(比較例1) (Comparative Example 1)

使用與實施例1相同的裝置,除了使用濾布FC取代濾布FA以外,其他都和實施例1相同進行了測試。對氟(氟離子)進行回收的結果,過濾途中就無法進行水的過濾。 The same apparatus as in Example 1 was used, and the test was carried out in the same manner as in Example 1 except that the filter cloth FC was used instead of the filter cloth FA. As a result of recovering fluorine (fluoride ion), water filtration cannot be performed during filtration.

(比較例2) (Comparative Example 2)

使用與實施例1相同的裝置,除了使用濾布FD取代濾布FA以外,其他都和實施例1相同進行了測試。對氟(氟離子)進行回收的結果,氟化合物幾乎全量流出至處理水PW之中。 The same apparatus as in Example 1 was used, and the same test as in Example 1 was carried out except that the filter cloth FD was used instead of the filter cloth FA. As a result of recovery of fluorine (fluorine ion), almost all of the fluorine compound flows out into the treated water PW.

(比較例3) (Comparative Example 3)

使用與實施例1相同的裝置,除了使用碳酸鈣CC4取代碳酸鈣CC1以外,其他都和實施例1相同進行了測試。 對氟(氟離子)進行回收的結果,過濾途中就無法進行水的過濾。 The same apparatus as in Example 1 was used, and the same test as in Example 1 was carried out except that calcium carbonate CC4 was used instead of calcium carbonate CC1. As a result of recovering fluorine (fluoride ion), water filtration cannot be performed during filtration.

(比較例4) (Comparative Example 4)

使用與實施例1相同的裝置,除了使用碳酸鈣CC5取代碳酸鈣CC1以外,其他都和實施例1相同進行了測試。其結果,在析出槽11並沒有形成反應,氟離子幾乎全量流出至處理水PW之中。 The same apparatus as in Example 1 was used, and the same test as in Example 1 was carried out except that calcium carbonate CC5 was used instead of calcium carbonate CC1. As a result, no reaction was formed in the precipitation tank 11, and almost all of the fluorine ions flowed out into the treated water PW.

根據以上的實施例及比較例時,得知:至少形態為使用寶綸製平紋織法或斜紋織法的濾布時,是可構築成為平均透氣度40cc/cm2‧min~平均透氣度500cc/cm2‧min以及碳酸鈣平均粒子徑5~200μm之十分實用的氟去除系統。 According to the above-described examples and comparative examples, it is found that at least the form of the filter cloth using the plain weave or the twill weave of the resin can be constructed to have an average air permeability of 40 cc/cm 2 ‧ min to an average air permeability of 500 cc. /cm 2 ‧ min and a very practical fluorine removal system with an average particle diameter of 5 to 200 μm.

如以上的說明,根據本實施形態之氟去除系統時是能夠以十足的過濾效率去除被處理水INF中的氟離子。 As described above, according to the fluorine removal system of the present embodiment, it is possible to remove fluorine ions in the water to be treated INF with a sufficient filtration efficiency.

以上雖然對本發明的幾種實施例進行了說明,但該等實施例,是以例子為提示,並不表示限定本發明的範圍。該等新的實施例,是能以其他各式各樣的形態加以實施,只要不脫離本發明的主旨範圍,是可進行各種的省略、替換及變更。該等實施例或其變形是包括在本發明的範圍及主旨,並且包括在申請專利範圍所記載之發明和與其均等的範圍。 The embodiments of the present invention have been described above, but are not intended to limit the scope of the present invention. The present invention can be embodied in a variety of other forms, and various omissions, substitutions and changes can be made without departing from the scope of the invention. The invention and its modifications are intended to be included within the scope and spirit of the invention and are intended to

10‧‧‧氟去除系統 10‧‧‧Fluorine removal system

11‧‧‧析出槽 11‧‧‧Precipitation slot

13‧‧‧濾器 13‧‧‧ filter

14‧‧‧洗淨機構 14‧‧‧Cleaning agency

15‧‧‧固液分離裝置 15‧‧‧Solid-liquid separation device

15A‧‧‧泥漿排出口 15A‧‧‧Mud discharge

15B‧‧‧指定容器 15B‧‧‧Specified container

15C‧‧‧容器口 15C‧‧‧ container mouth

16‧‧‧泥漿回收槽 16‧‧‧ mud recovery tank

17‧‧‧脫水機(脫水槽) 17‧‧‧Dehydrator (dewatering tank)

CC‧‧‧碳酸鈣 CC‧‧‧calcium carbonate

CK‧‧‧濾餅層 CK‧‧ filter cake layer

CW‧‧‧洗淨水 CW‧‧·washing water

DW‧‧‧濃度調整用水 DW‧‧‧Concentration water adjustment

EW‧‧‧排水 EW‧‧‧Drainage

PW‧‧‧處理水 PW‧‧‧Processing water

SL‧‧‧濃縮泥漿 SL‧‧‧Concentrated mud

INF‧‧‧被處理水 INF‧‧‧ treated water

INF1‧‧‧初級處理水 INF1‧‧‧ primary treated water

第1圖為表示本發明實施形態的氟去除系統的概要構成方塊圖。 Fig. 1 is a schematic block diagram showing a fluorine removal system according to an embodiment of the present invention.

10‧‧‧氟去除系統 10‧‧‧Fluorine removal system

11‧‧‧析出槽 11‧‧‧Precipitation slot

13‧‧‧濾器 13‧‧‧ filter

14‧‧‧洗淨機構 14‧‧‧Cleaning agency

15‧‧‧固液分離裝置 15‧‧‧Solid-liquid separation device

15A‧‧‧泥漿排出口 15A‧‧‧Mud discharge

15B‧‧‧指定容器 15B‧‧‧Specified container

15C‧‧‧容器口 15C‧‧‧ container mouth

16‧‧‧泥漿回收槽 16‧‧‧ mud recovery tank

17‧‧‧脫水機(脫水槽) 17‧‧‧Dehydrator (dewatering tank)

CC‧‧‧碳酸鈣 CC‧‧‧calcium carbonate

CK‧‧‧濾餅層 CK‧‧ filter cake layer

CW‧‧‧洗淨水 CW‧‧·washing water

DW‧‧‧濃度調整用水 DW‧‧‧Concentration water adjustment

EW‧‧‧排水 EW‧‧‧Drainage

PW‧‧‧處理水 PW‧‧‧ treated water

SL‧‧‧濃縮泥漿 SL‧‧‧Concentrated mud

INF‧‧‧被處理水 INF‧‧‧ treated water

INF1‧‧‧初級處理水 INF1‧‧‧ primary treated water

Claims (6)

一種氟回收裝置,其特徵為,具備有:針對含有氟離子之被處理水和上述被處理水所含有之上述氟離子的量投入過剩量之碳酸鈣,使上述碳酸鈣和上述氟離子形成反應藉此析出氟化鈣生成初級處理水的析出槽;及對含有上述氟化鈣及上述碳酸鈣之上述初級處理水進行濾餅過濾在濾器上形成有上述氟化鈣及上述碳酸鈣堆積的混合濾餅層之具有上述濾器的固液分離裝置。 A fluorine recovery device comprising: an excess amount of calcium carbonate added to the amount of the fluoride ion contained in the water to be treated containing the fluoride ion and the water to be treated, and the calcium carbonate and the fluoride ion are reacted And precipitating the calcium fluoride to form a precipitation tank for the primary treated water; and filtering the filter cake by filtering the primary treated water containing the calcium fluoride and the calcium carbonate to form a mixture of the calcium fluoride and the calcium carbonate deposit on the filter. A solid-liquid separation device of the filter cake layer having the above filter. 如申請專利範圍第1項所記載的氟回收裝置,其中,投入於上述析出槽之上述碳酸鈣的粒子徑為5~200μm。 The fluorine recovery device according to the first aspect of the invention, wherein the calcium carbonate charged in the precipitation tank has a particle diameter of 5 to 200 μm. 如申請專利範圍第1項或第2項所記載的氟回收裝置,其中,具備有利用洗淨水使上述混合濾餅層從上述濾器去除的洗淨裝置。 The fluorine recovery device according to claim 1 or 2, further comprising a cleaning device for removing the mixed cake layer from the filter by using washing water. 一種氟回收系統,其特徵為,具備:針對含有氟離子之被處理水和上述被處理水所含有之上述氟離子的量投入過剩量之碳酸鈣,使上述碳酸鈣和上述氟離子形成反應藉此析出氟化鈣生成初級處理水的析出槽;對含有上述氟化鈣及上述碳酸鈣之上述初級處理水進行濾餅過濾在濾器上形成有上述氟化鈣及上述碳酸鈣堆積的混合濾餅層之具有上述濾器的固液分離裝置;利用洗淨水使上述混合濾餅層從上述濾器去除的洗淨裝置;及 對含有上述所去除之混合濾餅層及上述洗淨水之濃縮漿液進行脫水的脫水機。 A fluorine recovery system comprising: adding an excessive amount of calcium carbonate to the water to be treated containing fluorine ions and the amount of the fluorine ions contained in the water to be treated, and reacting the calcium carbonate with the fluoride ions The precipitated tank for precipitating calcium fluoride to form primary treated water; and the filter cake for filtering the primary treated water containing the calcium fluoride and the calcium carbonate to form a mixed filter cake on which the calcium fluoride and the calcium carbonate are stacked a solid-liquid separation device having the above-mentioned filter; a cleaning device for removing the mixed filter cake layer from the filter by using washing water; and A dehydrator for dehydrating the concentrated slurry containing the above-mentioned mixed cake cake layer and the above-mentioned washing water. 如申請專利範圍第4項所記載的氟回收系統,其中,投入於上述析出槽之上述碳酸鈣的粒子徑為5~200μm。 The fluorine recovery system according to the fourth aspect of the invention, wherein the calcium carbonate charged in the precipitation tank has a particle diameter of 5 to 200 μm. 一種氟回收方法,其特徵為,具備:於析出槽中針對含有氟離子之被處理水和上述被處理水所含有之上述氟離子的量投入過剩量之碳酸鈣,使上述碳酸鈣和上述氟離子形成反應藉此析出氟化鈣生成初級處理水的析出過程;及對上述析出過程所獲得之含有上述氟化鈣及上述碳酸鈣的上述初級處理水進行濾餅過濾在濾器上形成有上述氟化鈣及上述碳酸鈣堆積之混合濾餅層的固液分離過程。 A method of recovering fluorine, wherein the calcium carbonate and the fluorine are added to an amount of the fluoride ion contained in the water to be treated and the fluoride ion contained in the water to be treated in the deposition tank. The ion formation reaction thereby precipitating calcium fluoride to form a precipitation process of the primary treated water; and filtering the cake on the primary treated water containing the calcium fluoride and the calcium carbonate obtained by the precipitation process to form the fluorine on the filter A solid-liquid separation process of a mixed filter cake layer of calcium and the above calcium carbonate.
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