JPH0315517B2 - - Google Patents
Info
- Publication number
- JPH0315517B2 JPH0315517B2 JP21890083A JP21890083A JPH0315517B2 JP H0315517 B2 JPH0315517 B2 JP H0315517B2 JP 21890083 A JP21890083 A JP 21890083A JP 21890083 A JP21890083 A JP 21890083A JP H0315517 B2 JPH0315517 B2 JP H0315517B2
- Authority
- JP
- Japan
- Prior art keywords
- liquid
- waste liquid
- calcium carbonate
- calcium
- precipitate
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 239000007788 liquid Substances 0.000 claims description 23
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 claims description 16
- 238000000034 method Methods 0.000 claims description 13
- 229960002050 hydrofluoric acid Drugs 0.000 claims description 11
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 5
- 229910052791 calcium Inorganic materials 0.000 claims description 5
- 239000011575 calcium Substances 0.000 claims description 5
- 239000003795 chemical substances by application Substances 0.000 claims description 4
- 230000003472 neutralizing effect Effects 0.000 claims description 4
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 18
- 239000002699 waste material Substances 0.000 description 11
- 229910000019 calcium carbonate Inorganic materials 0.000 description 9
- 239000002244 precipitate Substances 0.000 description 9
- 238000001035 drying Methods 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 238000006386 neutralization reaction Methods 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 229910004261 CaF 2 Inorganic materials 0.000 description 4
- 238000001914 filtration Methods 0.000 description 4
- 239000002253 acid Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- 239000004568 cement Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000002002 slurry Substances 0.000 description 2
- IRPGOXJVTQTAAN-UHFFFAOYSA-N 2,2,3,3,3-pentafluoropropanal Chemical compound FC(F)(F)C(F)(F)C=O IRPGOXJVTQTAAN-UHFFFAOYSA-N 0.000 description 1
- KLZUFWVZNOTSEM-UHFFFAOYSA-K Aluminum fluoride Inorganic materials F[Al](F)F KLZUFWVZNOTSEM-UHFFFAOYSA-K 0.000 description 1
- JZDMNWBZPLJKBT-UHFFFAOYSA-N F.[Zr] Chemical compound F.[Zr] JZDMNWBZPLJKBT-UHFFFAOYSA-N 0.000 description 1
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 238000007605 air drying Methods 0.000 description 1
- OYLGJCQECKOTOL-UHFFFAOYSA-L barium fluoride Chemical compound [F-].[F-].[Ba+2] OYLGJCQECKOTOL-UHFFFAOYSA-L 0.000 description 1
- 229910001632 barium fluoride Inorganic materials 0.000 description 1
- 238000011437 continuous method Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 229910052731 fluorine Inorganic materials 0.000 description 1
- 239000011737 fluorine Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- -1 hydrofluoric acid Chemical class 0.000 description 1
- 239000008235 industrial water Substances 0.000 description 1
- 238000004898 kneading Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000010907 mechanical stirring Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000004381 surface treatment Methods 0.000 description 1
- BFDQRLXGNLZULX-UHFFFAOYSA-N titanium hydrofluoride Chemical compound F.[Ti] BFDQRLXGNLZULX-UHFFFAOYSA-N 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Removal Of Specific Substances (AREA)
Description
【発明の詳細な説明】
本発明は弗化水素酸製造工程あるいは弗化水素
酸による各種器材(例えばガラス)の表面処理工
程等で発生する各種の高濃度弗素系酸含有液を処
理する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating various highly concentrated fluoric acid-containing liquids generated in the hydrofluoric acid production process or the surface treatment process of various instruments (for example, glass) using hydrofluoric acid. It is something.
弗化水素酸等の弗素系酸含有廃液は一般に濃度
が高く、そのままの濃度では機械撹拌による中和
処理が困難なため、通常他工程からの排水又は工
業用水等で希釈し、炭酸カルシウム等のカルシウ
ム系中和剤をスラリー状にして添加することによ
り中和処理し、その後沈鉱、過等により固液分
離しているが、カルシウム系中和剤により中和生
成するCaF2等の沈殿は微粒子であつて過困難
であり、また上記廃液中に併存することの多い
H2SO4の中和についても、脱水ケーキの水分を
20%以下とするためには、種晶の繰返し、反応時
間の延長、場合によつては加温等を行なわなけれ
ばならない。 Fluoric acid-containing waste liquids such as hydrofluoric acid generally have a high concentration, and it is difficult to neutralize them by mechanical stirring if the concentration is as it is, so it is usually diluted with wastewater from other processes or industrial water, etc. Neutralization is performed by adding a calcium-based neutralizing agent in the form of a slurry, followed by solid-liquid separation by precipitation, filtration, etc. However, the precipitation of CaF 2 etc. that is neutralized by the calcium-based neutralizing agent is They are fine particles that are difficult to detect, and they often coexist in the waste liquid mentioned above.
Regarding the neutralization of H 2 SO 4 , the moisture in the dehydrated cake is also
In order to keep it below 20%, it is necessary to repeat seed crystals, extend the reaction time, and in some cases heat it.
例えば、弗化水素酸含有液の中和生成物は主に
CaF2とCaSO4・2H2Oの混合沈殿であつて過・
脱水が困難なため、プレコートフイルターやオリ
バーフイルター等で過し、場合により加熱乾燥
工程を経てCaF2,CaSO4・2H2O等の混合殿物と
して回収処理されているのが実状である。 For example, the neutralization products of hydrofluoric acid-containing liquids are mainly
It is a mixed precipitate of CaF 2 and CaSO 4 2H 2 O.
Since it is difficult to dehydrate, the actual situation is that it is passed through a pre-coat filter or an Oliver filter, and in some cases is subjected to a heating drying process to be recovered as a mixed precipitate such as CaF 2 , CaSO 4 .2H 2 O, etc.
このように、高濃度弗素系酸含有液を処理する
場合には、従来の方法では上記の如く過及び乾
燥工程、更には液の最終処理といつた工程が必
要となり、工程が複雑でコスト高となる欠点があ
つた。 In this way, when treating a liquid containing a highly concentrated fluoric acid, conventional methods require filtration and drying steps as described above, as well as final treatment of the liquid, making the process complicated and costly. There was a drawback.
本発明は、弗化水素酸、珪弗化水素酸、硼弗化
水素酸、ジルコン弗化水素酸、チタン弗化水素酸
等の弗素系酸を高濃度に含有する液に、炭酸カル
シウム、水酸化カルシウム、酸化カルシウム等の
カルシウム系中和剤を添加し、該液を直接固化さ
せることを特徴とするものである。 In the present invention, calcium carbonate and water are added to a liquid containing a high concentration of fluorine-based acids such as hydrofluoric acid, hydrosilicofluoric acid, borofluoric acid, zirconium hydrofluoric acid, and titanium hydrofluoric acid. This method is characterized by adding a calcium-based neutralizing agent such as calcium oxide or calcium oxide to directly solidify the liquid.
本発明法によれば該廃液を希釈することなく、
しかも過、脱水、乾燥等の工程を経ずに、セメ
ントミキサー型等の混練器で混練するだけでよ
く、固液分離を行なうことなく直接該廃液を固形
の状態で回収することができるのである。 According to the method of the present invention, without diluting the waste liquid,
In addition, it is only necessary to knead the waste liquid in a cement mixer type kneader without going through processes such as filtration, dehydration, and drying, and the waste liquid can be directly recovered in a solid state without performing solid-liquid separation. .
この場合、使用するカルシウム系中和剤は、粉
末等の固形物として添加するとよく、その添加量
は化学当量以上好ましくは1.1〜1.5当量を添加混
合し、生成殿物のPHを3以上好ましくは5以上と
するとよい。 In this case, the calcium-based neutralizer to be used is preferably added as a solid substance such as a powder, and the amount added is at least a chemical equivalent, preferably 1.1 to 1.5 equivalents, and the pH of the produced precipitate is preferably 3 or more. It is better to set it to 5 or more.
また、処理方式としてはバツチ式と連続式が考
えられるが、本発明法ではいずれの方式を採用し
てもよい。 Further, as the processing method, a batch method and a continuous method can be considered, but either method may be adopted in the method of the present invention.
実施例 1
HF19.7%,H2SO416.3%,H2SiF68.1%の廃液
1.26Kgと、炭酸カルシウム1.1Kg(1.05当量)1を
混合混練した。生成殿物を測定したところ、PHは
1.5であつた。さらに、炭酸カルシウム100gを追
加混練した。Example 1 Waste liquid of HF 19.7%, H 2 SO 4 16.3%, H 2 SiF 6 8.1%
1.26 kg and 1.1 kg (1.05 equivalent) of calcium carbonate were mixed and kneaded. When the produced precipitate was measured, the pH was
It was 1.5. Furthermore, 100 g of calcium carbonate was additionally kneaded.
生成殿物のPHは5.5で水分は36%となり、1日
間自然乾燥後の水分は30.5%、2日後は27.5%,
3日後では24.5%となつた。 The pH of the produced precipitate is 5.5 and the moisture content is 36%. After 1 day of natural drying, the moisture content is 30.5%, and after 2 days it is 27.5%.
Three days later, it was 24.5%.
この場合の炭酸カルシウムの使用量は化学当量
の1.15当量であり、殿物の組成はCaF255.3%、
CaSO4・2H2O29.6%,SiO23.5%であつた。 The amount of calcium carbonate used in this case is 1.15 chemical equivalents, and the composition of the precipitate is CaF 2 55.3%,
CaSO 4 .2H 2 O2 was 9.6% and SiO 2 3.5%.
実施例 2
実施例1と同一の廃液25Kgと炭酸カルシウム24
Kgをセメントミキサー型混練器で60分間混練し
た。Example 2 25 kg of waste liquid same as Example 1 and 24 kg of calcium carbonate
Kg was kneaded for 60 minutes in a cement mixer type kneader.
生成殿物のPHは6.0、水分は31%であり、1日
自然乾燥後の水分は26.5%であつた。 The resulting precipitate had a pH of 6.0 and a moisture content of 31%, and the moisture content after one day of natural drying was 26.5%.
なお、反応中の混練器内の温度を測定したら、
50〜70℃でかなりの水の蒸発がみられた。この反
応熱(中和熱)による水の蒸発も殿物水分の低下
に寄与しているものと思われる。 In addition, after measuring the temperature inside the kneader during the reaction,
Significant water evaporation was observed between 50 and 70°C. It is thought that the evaporation of water due to this reaction heat (neutralization heat) also contributes to the decrease in precipitate water content.
実施例 3
HF15%,H2SO49%,H2SiF620%,更に弗化
アルミニウム、弗化バリウム等のスラリーを数%
含有する廃液と炭酸カルシウムを連続的に混練器
に供給して混練した。廃液処理量が4t、炭酸カル
シウムの給鉱量が5tになつた時点(供給時間2時
間)で廃液および炭酸カルシウムの供給を停止
し、引続き30分間混練した。Example 3 15% HF, 9% H 2 SO 4 , 20% H 2 SiF 6 , and several % slurry of aluminum fluoride, barium fluoride, etc.
The waste liquid and calcium carbonate contained therein were continuously supplied to a kneader and kneaded. When the amount of waste liquid treated reached 4 tons and the amount of calcium carbonate fed reached 5 tons (supply time 2 hours), the supply of waste liquid and calcium carbonate was stopped, and kneading was continued for 30 minutes.
なお、この場合の使用炭酸カルシウム量は化学
当量の1.4当量である。 Note that the amount of calcium carbonate used in this case is 1.4 chemical equivalents.
その結果、得られた生成殿物のPHは6.5、水分
25%であり、1日間自然乾燥後の水分は22.5%と
なり、いずれも直ちにトラツクによる輪送が可能
な状態であつた。 As a result, the pH of the resulting precipitate was 6.5, and the water content was
After air drying for one day, the moisture content was 22.5%, and all were in a state where they could be immediately transported by truck.
以上のように、本発明法によれば弗素系酸含有
廃液を中和反応によつて直接水分量の極めて少な
い固形物として回収することができるので、直ち
にトラツク等による輸送が可能であり、従来のよ
うに希釈、過、加熱乾燥、液の最終処理等の
複雑な工程が一切不要となるなど、経済的にも極
めて有利である。 As described above, according to the method of the present invention, fluoric acid-containing waste liquid can be directly recovered as a solid substance with extremely low water content through a neutralization reaction, so it can be immediately transported by truck, etc. It is extremely advantageous economically, as it eliminates the need for complex processes such as dilution, filtration, heat drying, and final treatment of the liquid.
Claims (1)
を添加することにより該液を直接固化させること
を特徴とする弗素系酸含有液の処理法。1. A method for treating a liquid containing a fluoric acid, which comprises directly solidifying the liquid by adding a calcium-based neutralizing agent to the liquid containing a highly concentrated fluoric acid.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP21890083A JPS60110394A (en) | 1983-11-21 | 1983-11-21 | Treatment of fluorine contained acid-containing solution |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP21890083A JPS60110394A (en) | 1983-11-21 | 1983-11-21 | Treatment of fluorine contained acid-containing solution |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS60110394A JPS60110394A (en) | 1985-06-15 |
| JPH0315517B2 true JPH0315517B2 (en) | 1991-03-01 |
Family
ID=16727068
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP21890083A Granted JPS60110394A (en) | 1983-11-21 | 1983-11-21 | Treatment of fluorine contained acid-containing solution |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS60110394A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4368249B2 (en) * | 2004-06-01 | 2009-11-18 | 三洋電機株式会社 | Treatment apparatus and treatment method of water to be treated using the same |
| JP6660812B2 (en) * | 2016-05-31 | 2020-03-11 | オルガノ株式会社 | Waste liquid treatment method and waste liquid treatment device |
-
1983
- 1983-11-21 JP JP21890083A patent/JPS60110394A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS60110394A (en) | 1985-06-15 |
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