TWI438154B - Method for treating hydrofluoric acid wastewater - Google Patents
Method for treating hydrofluoric acid wastewater Download PDFInfo
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- TWI438154B TWI438154B TW101126613A TW101126613A TWI438154B TW I438154 B TWI438154 B TW I438154B TW 101126613 A TW101126613 A TW 101126613A TW 101126613 A TW101126613 A TW 101126613A TW I438154 B TWI438154 B TW I438154B
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- hydrofluoric acid
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- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 title claims description 217
- 238000000034 method Methods 0.000 title claims description 21
- 239000002351 wastewater Substances 0.000 title description 4
- 239000012528 membrane Substances 0.000 claims description 63
- 238000000926 separation method Methods 0.000 claims description 55
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 31
- 238000001704 evaporation Methods 0.000 claims description 28
- 230000008020 evaporation Effects 0.000 claims description 26
- 230000000149 penetrating effect Effects 0.000 claims description 16
- 239000007864 aqueous solution Substances 0.000 claims description 13
- 229910052731 fluorine Inorganic materials 0.000 claims description 12
- 239000011737 fluorine Substances 0.000 claims description 12
- 239000003513 alkali Substances 0.000 claims description 8
- 238000010438 heat treatment Methods 0.000 claims description 3
- 229910052797 bismuth Inorganic materials 0.000 claims description 2
- JCXGWMGPZLAOME-UHFFFAOYSA-N bismuth atom Chemical compound [Bi] JCXGWMGPZLAOME-UHFFFAOYSA-N 0.000 claims description 2
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 claims 1
- 239000007788 liquid Substances 0.000 description 17
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 description 12
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 description 11
- 238000010586 diagram Methods 0.000 description 7
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 6
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 6
- 229910052791 calcium Inorganic materials 0.000 description 6
- 239000011575 calcium Substances 0.000 description 6
- 229910052707 ruthenium Inorganic materials 0.000 description 6
- QPJSUIGXIBEQAC-UHFFFAOYSA-N n-(2,4-dichloro-5-propan-2-yloxyphenyl)acetamide Chemical compound CC(C)OC1=CC(NC(C)=O)=C(Cl)C=C1Cl QPJSUIGXIBEQAC-UHFFFAOYSA-N 0.000 description 5
- WUKWITHWXAAZEY-UHFFFAOYSA-L calcium difluoride Chemical compound [F-].[F-].[Ca+2] WUKWITHWXAAZEY-UHFFFAOYSA-L 0.000 description 4
- 229910001634 calcium fluoride Inorganic materials 0.000 description 4
- 238000011084 recovery Methods 0.000 description 4
- 229910052684 Cerium Inorganic materials 0.000 description 3
- GWXLDORMOJMVQZ-UHFFFAOYSA-N cerium Chemical compound [Ce] GWXLDORMOJMVQZ-UHFFFAOYSA-N 0.000 description 3
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 238000010992 reflux Methods 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 239000004973 liquid crystal related substance Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000004065 semiconductor Substances 0.000 description 2
- 229910017855 NH 4 F Inorganic materials 0.000 description 1
- 239000004809 Teflon Substances 0.000 description 1
- 229920006362 Teflon® Polymers 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- -1 alkali metal salt Chemical class 0.000 description 1
- 229910052787 antimony Inorganic materials 0.000 description 1
- WATWJIUSRGPENY-UHFFFAOYSA-N antimony atom Chemical compound [Sb] WATWJIUSRGPENY-UHFFFAOYSA-N 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 229910052792 caesium Inorganic materials 0.000 description 1
- TVFDJXOCXUVLDH-UHFFFAOYSA-N caesium atom Chemical compound [Cs] TVFDJXOCXUVLDH-UHFFFAOYSA-N 0.000 description 1
- 229910000420 cerium oxide Inorganic materials 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000003657 drainage water Substances 0.000 description 1
- 238000005530 etching Methods 0.000 description 1
- 150000004673 fluoride salts Chemical class 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000001728 nano-filtration Methods 0.000 description 1
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/442—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/025—Reverse osmosis; Hyperfiltration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/027—Nanofiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/583—Treatment of water, waste water, or sewage by removing specified dissolved compounds by removing fluoride or fluorine compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/60—Silicon compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/12—Halogens or halogen-containing compounds
- C02F2101/14—Fluorine or fluorine-containing compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Water Supply & Treatment (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Organic Chemistry (AREA)
- Nanotechnology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
- Removal Of Specific Substances (AREA)
Description
本發明係有關於含矽及氟之氫氟酸排水之處理方法。The present invention relates to a method for treating hydrofluoric acid drainage containing hydrazine and fluorine.
用以將於半導體或液晶等電子零件製造步驟中所產生的氫氟酸排水再利用之處理方法,自習知即檢討迄今。例如,專利文獻1中揭示了一種方法,即藉由將鹼添加至含氟及矽之排水而將pH調整至6以上,使矽酸鹽沉澱後,利用壓濾機等將該矽酸鹽固液分離,並於分離液添加水溶性鈣,藉此而得以氟化鈣形式來回收氟之方法。The treatment method for recycling hydrofluoric acid produced in the manufacturing steps of electronic components such as semiconductors or liquid crystals has been reviewed since the beginning. For example, Patent Document 1 discloses a method in which the pH is adjusted to 6 or more by adding a base to the drainage of fluorine and antimony to precipitate a niobate, and then the niobate is solidified by a filter press or the like. The liquid is separated, and water-soluble calcium is added to the separation liquid, whereby the method of recovering fluorine by the form of calcium fluoride is obtained.
上述專利文獻1中所揭示之排水處理方法,由於係為求除去排水中所含的矽酸而添加鹼使其固液分離,因此分離液中所含的氟係以NaF、NH4 F、KF等鹼金屬鹽存在。如此一來,便無法直接將該分離液再利用作為用於進行蝕刻或洗淨等之氫氟酸,故而必須在藉由水溶性鈣之添加而以氟化鈣回收氟之後,將氟回復成原料來生成氫氟酸,為求再利用之步驟不僅繁瑣且會耗費大量能源。In the wastewater treatment method disclosed in Patent Document 1, since the alkali is added to remove the citric acid contained in the wastewater and the solid-liquid separation is performed, the fluorine contained in the separation liquid is NaF, NH 4 F, KF. An alkali metal salt is present. In this way, the separation liquid cannot be directly reused as hydrofluoric acid for etching or washing, and therefore it is necessary to recover fluorine after recovering fluorine by calcium fluoride by the addition of water-soluble calcium. The raw materials are used to form hydrofluoric acid, and the steps for recycling are not only cumbersome but also consume a lot of energy.
又,專利文獻2揭示有一種氫氟酸回收方法,係以蒸發鍋加熱含二氧化矽及金屬成分之氫氟酸廢液來生成粗氫氟酸蒸氣,而在此粗氫氟酸蒸發步驟中,係藉由將硫酸添加至氫氟酸廢液使金屬成分溶解,來抑制金屬成分沉澱,防止蒸發鍋中積垢之方法。Further, Patent Document 2 discloses a method for recovering hydrofluoric acid by heating a waste liquid of hydrofluoric acid containing cerium oxide and a metal component in an evaporation pot to form a crude hydrofluoric acid vapor, and in the crude hydrofluoric acid evaporation step. A method of suppressing precipitation of a metal component by adding sulfuric acid to a hydrofluoric acid waste liquid to dissolve a metal component to prevent fouling in the evaporation pot.
上述專利文獻2所揭示之氫氟酸回收方法之問題在於,氫氟酸廢液中之矽恐會大量混入粗氫氟酸蒸氣,故而該冷凝水依舊難以作為氫氟酸而再利用。The problem of the hydrofluoric acid recovery method disclosed in the above Patent Document 2 is that a large amount of crude hydrofluoric acid vapor is likely to be mixed in the hydrofluoric acid waste liquid, and thus the condensed water is still difficult to reuse as hydrofluoric acid.
專利文獻1:日本特開2010-207797號公報Patent Document 1: Japanese Laid-Open Patent Publication No. 2010-207797
專利文獻2:日本特許第4635527號公報Patent Document 2: Japanese Patent No. 4635527
於是,本發明目的在於提供一種氫氟酸排水之處理方法,係可有效率地除去氫氟酸排水中所含之矽,而可輕易回收能夠再利用之氫氟酸者。Accordingly, an object of the present invention is to provide a method for treating hydrofluoric acid drainage which is capable of efficiently removing hydrazine contained in a hydrofluoric acid drainage and easily recovering hydrofluoric acid which can be reused.
本發明前述目的可藉由下述來達成,即:一種氫氟酸排水之處理方法,係用以處理含矽及氟之氫氟酸排水者,其具備膜分離步驟,係使前述氫氟酸排水在pH值小於6之狀態下通過膜分離裝置,而分離成氫氟酸水溶液穿透水、與矽業經濃縮之非穿透水。The foregoing object of the present invention can be attained by a method for treating hydrofluoric acid drainage, which is for treating a hydrofluoric acid drainer containing bismuth and fluorine, which comprises a membrane separation step for the hydrofluoric acid The drainage is passed through a membrane separation device at a pH of less than 6, and separated into a hydrofluoric acid aqueous solution penetrating water and a non-penetrating water concentrated by the hydrazine industry.
該氫氟酸排水之處理方法中,前述膜分離步驟係以不添加鹼成分(尤其是鈣成分)至前述氫氟酸排水,便使其通過前述膜分離裝置為佳。前述膜分離裝置係以採用NF膜來進行膜分離為佳,或者是以採用RO膜來進行膜分離為佳。In the method for treating hydrofluoric acid drainage, the membrane separation step is preferably carried out by passing the membrane separation device without adding an alkali component (particularly a calcium component) to the hydrofluoric acid. The membrane separation apparatus preferably performs membrane separation using an NF membrane or membrane separation using an RO membrane.
又,其係以在上述膜分離步驟之外更具備蒸發步驟為 佳,該蒸發步驟係使前述穿透水加熱蒸發而生成含氫氟酸蒸氣。Further, it is further provided with an evaporation step in addition to the above membrane separation step. Preferably, the evaporation step heats the aforementioned penetrating water to form a hydrofluoric acid-containing vapor.
藉由本發明,可提供一種氫氟酸排水之處理方法,係可有效率地除去氫氟酸排水中所含之矽,而可輕易回收能夠再利用之氫氟酸者。According to the present invention, a method for treating hydrofluoric acid drainage can be provided, which can efficiently remove hydrazine contained in hydrofluoric acid drainage, and can easily recover hydrofluoric acid which can be reused.
第1圖係本發明一實施形態中用於氫氟酸排水之處理方法的裝置概略構成圖。Fig. 1 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage according to an embodiment of the present invention.
第2圖係本發明其他實施形態中用於氫氟酸排水之處理方法的裝置之概略構成圖。Fig. 2 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage in another embodiment of the present invention.
第3圖係本發明又一實施形態中用於氫氟酸排水之處理方法的裝置之概略構成圖。Fig. 3 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage in still another embodiment of the present invention.
以下,參照添附圖式針對本發明一實施形態進行說明。第1圖係本發明一實施形態中用於氫氟酸排水之處理方法的裝置之概略構成圖。第1圖所示之氫氟酸排水處理裝置,係構成為:原液槽10與膜分離裝置20係以配管11進行連接,而儲留於原液槽10之氫氟酸排水經供給至膜分離裝置20而進行膜分離。膜分離裝置20係於其殼體21內部藉由分離膜22隔開而形成有一次室23及二次室24。藉由泵(圖式未顯示)之運作而從原液槽10供給至膜分離裝置20之一次室23的氫氟酸排水,會被分離成可通過分離膜22流入二次 室24的穿透水、與不能通過分離膜22之非穿透水,且分別經由配管25、26而排出。分離膜22方面,以可將氫氟酸排水中所含之矽以溶解狀態有效除去為佳,具體而言可採用RO膜(Reverse Osmosis Membrane)或NF膜(Nanofiltration Membrane)。從一次室23排出之非穿透水的一部分,可使其通過回流配管27而與流過配管11之氫氟酸排水合流。Hereinafter, an embodiment of the present invention will be described with reference to the accompanying drawings. Fig. 1 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage according to an embodiment of the present invention. The hydrofluoric acid drainage treatment apparatus shown in Fig. 1 is configured such that the raw liquid tank 10 and the membrane separation device 20 are connected by a pipe 11, and the hydrofluoric acid drainage stored in the raw liquid tank 10 is supplied to the membrane separation device. 20 was subjected to membrane separation. The membrane separation device 20 is formed with a primary chamber 23 and a secondary chamber 24 separated by a separation membrane 22 inside the casing 21. The hydrofluoric acid drainage supplied from the raw liquid tank 10 to the primary chamber 23 of the membrane separation device 20 by the operation of a pump (not shown) is separated into two through the separation membrane 22 The water passing through the chamber 24 and the non-penetrating water that cannot pass through the separation membrane 22 are discharged through the pipes 25 and 26, respectively. In the separation membrane 22, it is preferable to effectively remove the ruthenium contained in the hydrofluoric acid drainage in a dissolved state, and specifically, an RO membrane (Reverse Osmosis Membrane) or an NF membrane (Nanofiltration Membrane) can be used. A part of the non-penetrating water discharged from the primary chamber 23 can be passed through the reflux pipe 27 to merge with the hydrofluoric acid drainage flowing through the pipe 11.
採用上述裝置之本實施形態之氫氟酸排水之處理方法,係將例如於半導體或液晶等電子零件製造步驟中產生的含矽及氟之氫氟酸排水,自原液槽10加壓供給至膜分離裝置20來進行。通過分離膜22之氫氟酸排水,不添加鹼成分而維持在pH值低於6之狀態,其所含之矽成分大多會溶解並以離子狀態存在,而由於離子分子量大故不會通過膜。因此,於膜分離裝置20之一次室23,矽的大部分不會通過分離膜22而是會被濃縮,以非穿透水被排出。另一方面,氫氟酸排水中所含之氟係以氫氟酸水溶液之姿且泰半通過分離膜22,因此,矽經降低之氫氟酸會自膜分離裝置20之二次室24排出。欲使矽濃縮倍率提升並使非穿透水少量化時,以藉由回流配管27使非穿透水之一部分回流為佳,藉由調整閥28之開度,可控制穿透水之回收率。In the method for treating hydrofluoric acid drainage according to the embodiment of the present invention, the hydrofluoric acid-containing hydrofluoric acid-containing wastewater generated in the manufacturing step of an electronic component such as a semiconductor or a liquid crystal is pressurized and supplied from the raw solution tank 10 to the film. The separation device 20 is performed. The hydrofluoric acid drainage of the separation membrane 22 is maintained at a pH lower than 6 without adding an alkali component, and the ruthenium component contained therein is mostly dissolved and exists in an ionic state, and does not pass through the membrane due to the large molecular weight of the ion. . Therefore, in the primary chamber 23 of the membrane separation device 20, most of the crucible does not pass through the separation membrane 22 but is concentrated and discharged without passing through the water. On the other hand, the fluorine contained in the hydrofluoric acid drainage is in the form of an aqueous solution of hydrofluoric acid and the Teflon passes through the separation membrane 22, so that the reduced hydrofluoric acid is discharged from the secondary chamber 24 of the membrane separation device 20. . In order to increase the concentration ratio of the ruthenium and to reduce the amount of non-penetrating water, it is preferable to reflux a part of the non-penetrating water by the reflux pipe 27, and by adjusting the opening degree of the valve 28, the recovery rate of the penetrating water can be controlled. .
如此,本實施形態之氫氟酸排水之處理方法,不於氫氟酸排水中添加鈣等鹼成分便可除去矽,故而可使穿透水呈高純度氫氟酸水溶液而直接再利用。因此,不必像在氫氟酸排水中添加鈣成分來回收氟化鈣之習知技術般自所獲得之氟化鈣製造氟之步驟,而可提高回收效率。再者,本 發明中,不添加鈣等鹼成分係如上述,是為了使氫氟酸排水pH值維持在低於6,以求可直接再利用已通過分離膜22之氫氟酸,而即使氫氟酸排水中略含可達成該目的程度之微量鹼成分亦無妨。As described above, in the method for treating hydrofluoric acid drainage according to the present embodiment, the hydrazine can be removed without adding an alkali component such as calcium to the hydrofluoric acid drainage, so that the permeated water can be directly reused as a high-purity hydrofluoric acid aqueous solution. Therefore, it is not necessary to carry out the step of producing fluorine from the obtained calcium fluoride as in the conventional technique of adding calcium component to hydrofluoric acid drainage to recover calcium fluoride, and the recovery efficiency can be improved. Again, this In the invention, the alkali component such as calcium is not added as described above, in order to maintain the pH value of the hydrofluoric acid drainage below 6, so that the hydrofluoric acid which has passed through the separation membrane 22 can be directly reused, even if hydrofluoric acid is drained. It is also possible to have a trace amount of alkali component which can achieve the purpose.
通過分離膜22之氫氟酸排水的pH值若上升至6以上,例如在有鹼成分存在之情況下,因氟會變成氟化物鹽(例如NaF等)而致使通過之氟離子降低,分離膜22之氫氟酸通過率會減少。所以,氫氟酸排水必須在pH值低於6之狀態下通過分離膜22。該pH值因在5.5以下可使氟離子通過率更加提高故而頗為適宜,又以5以下更佳。氫氟酸排水之pH值的下限並無特別限定,例如在2以上。When the pH of the hydrofluoric acid drainage water passing through the separation membrane 22 is increased to 6 or more, for example, when an alkali component is present, fluorine is reduced to a fluoride salt (for example, NaF or the like), and the fluorine ion which passes therethrough is lowered. The pass rate of hydrofluoric acid in 22 will decrease. Therefore, the hydrofluoric acid drainage must pass through the separation membrane 22 in a state where the pH is lower than 6. Since the pH value is more than 5.5, the fluoride ion passage rate can be further improved, and it is more preferably 5 or less. The lower limit of the pH of the hydrofluoric acid drainage is not particularly limited, and is, for example, 2 or more.
分離膜22可以是RO膜或NF膜任一者,就進一步提高氫氟酸水溶液通過率之觀點而言,以適當採用NF膜為佳,另一方面,就進一步提高矽除去率之觀點而言,以適當採用RO膜為佳。The separation membrane 22 may be either an RO membrane or an NF membrane. From the viewpoint of further increasing the passage rate of the hydrofluoric acid aqueous solution, it is preferable to suitably use the NF membrane, and on the other hand, from the viewpoint of further increasing the ruthenium removal rate. It is better to use RO membrane properly.
本發明之氫氟酸排水之處理方法,亦可採用第2圖所示之裝置來進行。第2圖所示之氫氟酸排水之處理裝置,係在第1圖所示之原液槽10及膜分離裝置20之外,更進而具備蒸發裝置30與冷凝器40,該蒸發裝置30係藉由將已通過膜分離裝置20之氫氟酸水溶液加熱蒸發而使含氫氟酸蒸氣生成者,該冷凝器40係將已生成之含氫氟酸蒸氣冷卻而凝結者。蒸發裝置30之構成並無特別限定,例如可使用公知之瞬間蒸發濃縮裝置,亦即以加熱器加熱氫氟酸水溶液使之呈過飽和狀態後,在減壓下使其於蒸發罐內散佈並蒸發 者。於蒸發裝置30生成之含氫氟酸蒸氣,會經由配管31被導入冷凝器40成為凝結水,並自配管32回收。另一方面,經蒸發裝置30濃縮之濃縮水則會自配管33排出。The method for treating hydrofluoric acid drainage of the present invention can also be carried out by using the apparatus shown in Fig. 2. The hydrofluoric acid drainage treatment apparatus shown in Fig. 2 is further provided with an evaporation device 30 and a condenser 40 in addition to the raw liquid tank 10 and the membrane separation device 20 shown in Fig. 1, and the evaporation device 30 is used. The hydrofluoric acid-containing vapor is generated by heating and evaporating the hydrofluoric acid aqueous solution that has passed through the membrane separation device 20, and the condenser 40 cools the generated hydrofluoric acid-containing vapor to be condensed. The configuration of the evaporation device 30 is not particularly limited. For example, a known instantaneous evaporation concentration device can be used, that is, a hydrofluoric acid aqueous solution is heated by a heater to be supersaturated, and then dispersed and evaporated in an evaporation can under reduced pressure. By. The hydrofluoric acid-containing vapor generated in the evaporation device 30 is introduced into the condenser 40 through the pipe 31 to be condensed water, and is recovered from the pipe 32. On the other hand, the concentrated water concentrated by the evaporation device 30 is discharged from the pipe 33.
藉由第2圖所示之氫氟酸排水之處理裝置,含有矽及氟之氫氟酸排水以膜分離裝置20經膜分離為穿透水與非穿透水之後,穿透水會於蒸發裝置30生成含氫氟酸蒸氣被回收。而氫氟酸排水中所含之矽,其大部分被膜分離裝置20除去之後,可在蒸發裝置30與其他雜質一起進一步降低,獲得更高純度之氫氟酸水溶液。With the hydrofluoric acid drainage treatment device shown in FIG. 2, the hydrofluoric acid drainage containing ruthenium and fluorine is separated by the membrane separation device 20 into a penetrating water and a non-penetrating water, and the permeated water is evaporated. Device 30 produces a hydrofluoric acid containing vapor that is recovered. On the other hand, most of the ruthenium contained in the hydrofluoric acid drainage is removed by the membrane separation device 20, and the evaporation device 30 can be further reduced together with other impurities to obtain a hydrofluoric acid aqueous solution of higher purity.
採用第2圖所示氫氟酸排水之處理裝置之質量守衡之一例,則一如後所述。將含矽(si)及氫氟酸(HF)各為47mg/kg、約1%之氫氟酸排水15092kg/day,自原液槽10供給至膜分離裝置20,即可獲得含矽(Si)及氫氟酸(HF)各為10mg/kg、約1%之穿透水12074kg/day。亦即,可將約8成氫氟酸排水以氫氟酸水溶液進行回收,同時該氫氟酸水溶液之氫氟酸濃度係與氫氟酸排水之氫氟酸濃度同為1wt%左右,而相對於此,將矽濃度自47mg/kg降低至10mg/kg,可充分降低混入氫氟酸水溶液之矽。An example of the mass balance of the treatment apparatus for hydrofluoric acid drainage shown in Fig. 2 is as follows. A hydrofluoric acid-containing wastewater containing 47 mg/kg and about 1% of hydrofluoric acid (HF) is 15092 kg/day, and is supplied from the raw liquid tank 10 to the membrane separation device 20 to obtain cerium (Si). And hydrofluoric acid (HF) is 10 mg/kg each, and about 1% of penetrating water is 12,074 kg/day. That is, about 80% of the hydrofluoric acid drainage can be recovered by the hydrofluoric acid aqueous solution, and the hydrofluoric acid concentration of the hydrofluoric acid aqueous solution is about 1 wt% of the hydrofluoric acid concentration of the hydrofluoric acid drainage, and the relative Here, by reducing the hydrazine concentration from 47 mg/kg to 10 mg/kg, the enthalpy of mixing with the hydrofluoric acid aqueous solution can be sufficiently reduced.
又,該穿透水含有矽(Si)及氫氟酸(HF)各為121g/day、120kg/day,藉由將之供給至蒸發裝置30及冷凝器40,可獲得含矽(Si)及氫氟酸(HF)各為57g/day、108kg/day之凝結水11940kg/day。亦即,可回收與穿透水略等量之凝結水,而氫氟酸(HF)方面可回收約90%。已回收之冷凝水之氫氟酸濃度雖若干偏低為0.91wt%,但可降低其它雜質同時使矽濃度 自10mg/kg進一步降低至5mg/kg,而可回收高純度氫氟酸水溶液。Further, the penetrating water contains cerium (Si) and hydrofluoric acid (HF) of 121 g/day and 120 kg/day, respectively, and is supplied to the evaporation device 30 and the condenser 40 to obtain cerium (Si) and The hydrofluoric acid (HF) was 57 g/day and the condensed water of 108 kg/day was 11,940 kg/day. That is, it is possible to recover a certain amount of condensed water with the penetrating water, and about 90% of the hydrofluoric acid (HF) can be recovered. Although the concentration of hydrofluoric acid in the recovered condensed water is 0.91% by weight, it can reduce other impurities while making the concentration of cesium. It was further reduced from 10 mg/kg to 5 mg/kg, and a high-purity hydrofluoric acid aqueous solution was recovered.
第2圖所示之氫氟酸排水之處理裝置,係構成為將氫氟酸排水以膜分離裝置20進行膜分離之後導入蒸發裝置30,藉此可回收高純度之氫氟酸水溶液,亦可構成為將氫氟酸排水先行導入蒸發裝置30使含氫氟酸蒸氣生成之後,將該冷凝水以膜分離裝置20進行膜分離。The hydrofluoric acid drainage treatment apparatus shown in FIG. 2 is configured to introduce hydrofluoric acid drainage into the evaporation apparatus 30 after the membrane separation apparatus 20 performs membrane separation, thereby recovering a high-purity hydrofluoric acid aqueous solution. After the hydrofluoric acid drainage is first introduced into the evaporation device 30 to generate hydrofluoric acid-containing vapor, the condensed water is subjected to membrane separation by the membrane separation device 20.
本發明氫氟酸排水之處理方法,亦可採用第3圖所示之裝置來進行。第3圖所示之氫氟酸排水之處理裝置,係在第2圖所示之原液槽10、膜分離裝置20、蒸發裝置30及冷凝器40之外,更進而具備附加槽50及附加蒸發裝置60,該附加槽50係用以儲留自蒸發裝置30經由配管33排出之一次濃縮水與自膜分離裝置20經由配管26排出之非穿透水的混合水者,而該附加蒸發裝置60係使藉由配管51自附加槽50供給之混合水加熱並蒸發者。又,第3圖中係將與第2圖相同構成部分賦予同符號。The method for treating hydrofluoric acid drainage of the present invention can also be carried out by using the apparatus shown in Fig. 3. The hydrofluoric acid drainage treatment apparatus shown in Fig. 3 is further provided with an additional tank 50 and additional evaporation in addition to the raw liquid tank 10, the membrane separation device 20, the evaporation device 30, and the condenser 40 shown in Fig. 2 . In the device 60, the additional tank 50 is for storing the primary concentrated water discharged from the evaporation device 30 via the pipe 33 and the non-penetrating water discharged from the membrane separation device 20 via the pipe 26, and the additional evaporation device 60 The mixed water supplied from the additional tank 50 by the piping 51 is heated and evaporated. In the third embodiment, the same components as those in the second embodiment are denoted by the same reference numerals.
於附加蒸發裝置60生成之蒸氣,因含有未通過膜分離裝置20之少量氫氟酸及未於蒸發裝置30蒸發之少量氫氟酸,故藉由使該蒸氣透過配管61返回原液槽10,可更加提高氫氟酸回收率。另一方面,於附加蒸發裝置60經濃縮之二次濃縮水,則自配管62排出。The vapor generated in the additional evaporation device 60 contains a small amount of hydrofluoric acid that has not passed through the membrane separation device 20 and a small amount of hydrofluoric acid that has not been evaporated by the evaporation device 30, so that the vapor can be returned to the raw liquid tank 10 through the pipe 61. Increase the recovery rate of hydrofluoric acid. On the other hand, the secondary concentrated water which has been concentrated by the additional evaporation device 60 is discharged from the pipe 62.
10‧‧‧原液槽10‧‧‧ raw liquid tank
11‧‧‧配管11‧‧‧Pipe
20‧‧‧膜分離裝置20‧‧‧ membrane separation device
21‧‧‧殼體21‧‧‧ housing
22‧‧‧分離膜22‧‧‧Separation membrane
23‧‧‧一次室23‧‧‧First room
24‧‧‧二次室24‧‧‧Second room
25,26‧‧‧配管25,26‧‧‧Pipe
27‧‧‧回流配管27‧‧‧Reflow piping
28‧‧‧閥28‧‧‧Valves
30‧‧‧蒸發裝置30‧‧‧Evaporation unit
31,32,33‧‧‧配管31,32,33‧‧‧Pipe
40‧‧‧冷凝器40‧‧‧Condenser
50‧‧‧附加槽50‧‧‧Additional slot
51‧‧‧配管51‧‧‧Pipe
60‧‧‧附加蒸發裝置60‧‧‧Additional evaporation unit
61,62‧‧‧配管61,62‧‧‧Pipe
第1圖係本發明一實施形態中用於氫氟酸排水之處理方法的裝置概略構成圖。Fig. 1 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage according to an embodiment of the present invention.
第2圖係本發明其他實施形態中用於氫氟酸排水之處理方法的裝置之概略構成圖。Fig. 2 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage in another embodiment of the present invention.
第3圖係本發明又一實施形態中用於氫氟酸排水之處理方法的裝置之概略構成圖。Fig. 3 is a schematic configuration diagram of an apparatus for treating a hydrofluoric acid drainage in still another embodiment of the present invention.
10‧‧‧原液槽10‧‧‧ raw liquid tank
11‧‧‧配管11‧‧‧Pipe
20‧‧‧膜分離裝置20‧‧‧ membrane separation device
21‧‧‧殼體21‧‧‧ housing
22‧‧‧分離膜22‧‧‧Separation membrane
23‧‧‧一次室23‧‧‧First room
24‧‧‧二次室24‧‧‧Second room
25,26‧‧‧配管25,26‧‧‧Pipe
27‧‧‧回流配管27‧‧‧Reflow piping
28‧‧‧閥28‧‧‧Valves
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| JP7422534B2 (en) * | 2019-12-23 | 2024-01-26 | オルガノ株式会社 | Calcium fluoride recovery device and calcium fluoride recovery method |
| CN113105013B (en) * | 2020-01-09 | 2022-10-18 | 湖南中金岭南康盟环保科技有限公司 | Method for removing fluorine and chlorine in zinc smelting electrolyte |
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| JP3671644B2 (en) * | 1998-01-05 | 2005-07-13 | オルガノ株式会社 | Photoresist developing waste liquid recycling method and apparatus |
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