JPS6287411A - Method of decomposing chlorate - Google Patents
Method of decomposing chlorateInfo
- Publication number
- JPS6287411A JPS6287411A JP22827585A JP22827585A JPS6287411A JP S6287411 A JPS6287411 A JP S6287411A JP 22827585 A JP22827585 A JP 22827585A JP 22827585 A JP22827585 A JP 22827585A JP S6287411 A JPS6287411 A JP S6287411A
- Authority
- JP
- Japan
- Prior art keywords
- chlorate
- carbon
- salt
- solution
- chlorine
- 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.)
- Granted
Links
Landscapes
- Inorganic Compounds Of Heavy Metals (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は食塩水中に含まれる塩素酸塩の分解方法に関す
る。さらに詳しくは食塩水を電解して苛性ソーダを製造
する際、循環使用する食塩水中に含まれる塩素酸塩を効
率良く分解する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for decomposing chlorate contained in saline water. More specifically, the present invention relates to a method for efficiently decomposing chlorate contained in recycled saline when saline is electrolyzed to produce caustic soda.
現在、苛性ソーダは隔膜法又はイオン交換膜法により食
塩水を電解して製造されているが、陽極室に於いては
0g + 2 NaOH−+ NaC10+Na(j
’ 111g03 Na(JO−→NaCl0.−t
2 Na(7等の副反応により塩素酸塩が副生ずる。そ
の為食塩水を循環使用するイオン交換膜性電解に於いて
は、食塩水中に塩素酸塩が蓄積するために食塩の溶解度
の低下或いはイオン交換膜の劣化促進等の悪影響が生ず
る。Currently, caustic soda is produced by electrolyzing salt water using the diaphragm method or the ion exchange membrane method.
' 111g03 Na(JO-→NaCl0.-t
Chlorate is produced as a by-product due to side reactions such as 2 Na (7).Therefore, in ion-exchange membrane electrolysis where saline water is circulated, chlorate accumulates in the saline water, resulting in a decrease in the solubility of salt. Alternatively, adverse effects such as accelerated deterioration of the ion exchange membrane may occur.
従って、食塩水を循環使用するためには食塩水中の塩素
酸すtリウム澹度を一部レベル以下にするか若しくは完
全に除去する必要がある。Therefore, in order to reuse the saline solution, it is necessary to reduce the concentration of sodium chlorate in the saline solution to a certain level or to remove it completely.
このため食塩水の一部放棄、或いは塩素酸塩の分解のた
めに種々の方法が実施されている。For this reason, various methods have been implemented to partially discard saline water or to decompose chlorate.
従来から行われている分解方法としては(1)還元剤を
添加する方法及び(2)強酸を添加する方法があるが、
いずれも充分な分解方法であるとはいえない。Conventional decomposition methods include (1) adding a reducing agent and (2) adding a strong acid.
None of these methods can be said to be sufficient decomposition methods.
即ち0)の方法は亜硫酸ソーダの様な還元剤を添加する
のであるが、還元剤が比較的高価な上に使用量が多くな
るという欠点があり、さらにNa(JO,+ 3 Na
25Oa −ン3 NazS(14+Na(Jの反応式
で示される通りSO4イオンが生成してしまい、電解槽
の陽極劣化及びイオン交換膜劣化を促進するために、二
次的にSO4イオンの除去操作が必要になる。In other words, method 0) involves adding a reducing agent such as sodium sulfite, but this method has the disadvantage that the reducing agent is relatively expensive and requires a large amount of use.
As shown in the reaction formula of 25Oa - 3 NazS (14+Na It becomes necessary.
また(2)の方法は、例えば
NaCJOa + 611[’J−→3C1g + N
a(J + 31120の反応式で示される通り、強酸
として塩酸を使用し塩素酸塩を分解する方法であるが、
塩水のpuが1程度或いはそれ以下という強酸域でない
と充分な分解速度が得られないため、通常含有されてい
る塩素酸塩に対してモル比で10〜20倍の塩酸を添加
する必要がある。このため塩素酸塩を分解した後、過剰
分の塩酸を中和するべくアルカリを添加する必要がある
」−に、上式の他に次式の反応によって通常数パーセン
トの二酸化塩素が副生ずる。In addition, the method (2) is, for example, NaCJOa + 611['J-→3C1g + N
a(J + As shown in the reaction formula of 31120, it is a method of decomposing chlorate using hydrochloric acid as a strong acid,
Sufficient decomposition rate cannot be obtained unless the salt water is in a strong acid range with a PU of about 1 or less, so it is necessary to add 10 to 20 times the molar ratio of hydrochloric acid to the normally contained chlorate. . Therefore, after decomposing the chlorate, it is necessary to add an alkali to neutralize the excess hydrochloric acid.'' In addition to the above equation, several percent of chlorine dioxide is usually produced as a by-product by the reaction of the following equation.
2NaCJ03+411(’J )2CfOz +C
J!2」2Naf”J +o。2NaCJ03+411('J)2CfOz +C
J! 2”2Naf”J +o.
この二酸化塩素は自己爆発性である]−に、塩素中に混
入することにより塩素使用段hiN側で反応不良を生じ
させる場合がある。This chlorine dioxide is self-explosive, and if mixed into chlorine, it may cause a reaction failure in the chlorine-using stage hiN.
本発明の目的は上記従来法の欠点を解消し、操作が簡単
である上に効率が良く、しかも二次的処理の必要がない
塩素酸塩の分解方法を提供することにある。An object of the present invention is to provide a method for decomposing chlorate, which eliminates the drawbacks of the conventional methods, is simple and efficient in operation, and does not require secondary treatment.
c問題点を解決するだめの手段〕
即ち、本発明は、塩素酸塩を含有する酸性又は中性の食
塩水を炭素と接触させることを特徴とする塩素酸塩の分
解方法であり、
2Naα03 +3G−一〉3CO2+ 2 NaCl
の反応式で示される通り、炭素により塩素酸塩を二酸化
炭素と食塩に分解する方法である。Means for Solving Problem c] That is, the present invention is a method for decomposing chlorate, which is characterized by bringing an acidic or neutral saline solution containing chlorate into contact with carbon. -1〉3CO2+ 2 NaCl
As shown in the reaction formula, this is a method of decomposing chlorate into carbon dioxide and salt using carbon.
発明者等らはさらに、系にわずかの塩素を溶存させる事
に、F、り本反応が容品に開始する事を発見した。すな
わら溶存するα2により生成するNaα0、さらには加
水分解により生成するHCJOが炭素に初回吸着し、さ
らに反応してCO,を生ずる。The inventors further discovered that by dissolving a small amount of chlorine in the system, the F, Rimoto reaction starts in the container. That is, Naα0 produced by dissolved α2 and further HCJO produced by hydrolysis are initially adsorbed on carbon and further react to produce CO.
NaCJO+ II(J−〉H(JO+Na(JCl
t +HtO−一7月1(JO+ Hα2]1αO十G
−〉COz + 211(Jこの際に生成するH(jに
よって、中性液がpH値で3以下になっていると推定さ
れ、塩素酸塩と炭素との反応が促進されて、はとんど副
反応を生ずる事なく二酸化炭素と食塩に分解する事が判
った。NaCJO+ II(J->H(JO+Na(JCl
t +HtO-1 July 1 (JO+ Hα2] 1αO 1 G
-> COz + 211 (J) It is estimated that the pH value of the neutral liquid is 3 or less due to the H (j) generated at this time, and the reaction between chlorate and carbon is promoted, causing a It was found that it decomposed into carbon dioxide and salt without any side reactions.
本発明で使用する炭素としては活性炭、木炭等いずれで
も良いが、特に好ましいのは活性炭であり、例えばキャ
タラ工業■製WA−4/8メソシュが挙げられる。The carbon used in the present invention may be activated carbon, charcoal, or the like, but activated carbon is particularly preferred, such as WA-4/8 Mesosch manufactured by Catara Industries.
食塩水は中性又は酸性であれば良いが、反応速度を考慮
した場合p113以下が好ましく、また塩素を溶存させ
ると反応は一層促進される。さらに食塩水と炭素を接触
させる際の温度は60゜〜130℃、接触時間は5〜1
20分であることが好ましい。接触時間が5分より短い
場合は塩素酸塩の分解が不充分になり、120分より長
い場合は、特に不都合は生しないが、経済性を考慮した
場合120分以下で充分である。The brine may be neutral or acidic, but in consideration of the reaction rate, it is preferably p113 or less, and the reaction will be further promoted if chlorine is dissolved therein. Furthermore, the temperature when bringing the salt solution into contact with carbon is 60° to 130°C, and the contact time is 5 to 1
Preferably it is 20 minutes. If the contact time is shorter than 5 minutes, the decomposition of the chlorate will be insufficient, and if it is longer than 120 minutes, no particular disadvantage will occur, but from economical considerations, 120 minutes or less is sufficient.
また温度を130℃より高くすると反応は更に促進され
るが、高耐圧の反応槽が必要となり、加熱の為に大量の
エネルギーが必要となる等の不都合が生じる。Further, if the temperature is raised above 130° C., the reaction is further promoted, but a reaction tank with high pressure resistance is required, which causes disadvantages such as a large amount of energy being required for heating.
以下実施例及び比較例により本発明の作用、効果をさら
に詳しく説明する。The functions and effects of the present invention will be explained in more detail below using Examples and Comparative Examples.
実施例I
Naα03として21g/Ilの塩素酸塩を含むpH2
,2の食塩水300mZに活性炭(キャタラエ」1^−
478メソシユ)150−を加えて85℃に加熱維持し
、塩素酸塩の濃度変化を測定したところ以下の通りであ
った。Example I pH 2 with 21 g/Il chlorate as Naα03
, Activated carbon (Catarae) 1^- in 300mZ of saline solution of 2.
478 mesohydr) 150- was added and maintained at 85° C., and the change in chlorate concentration was measured, and the results were as follows.
時間 NaαOz(g/N)
1時間後 14.5
2 〃10.5
5〃4
実施例2
N a CI Ozとして45g/#の塩素酸塩を含む
pH2,3の食塩水300 mlに活性炭(キャタラ工
業■製諭−8/32メソシュ)150−を加えて103
℃に加熱維持し、塩素酸塩の濃度変化を測定したところ
以下の通りであった。Time NaαOz (g/N) After 1 hour 14.5 2 〃10.5 5〃4 Example 2 Activated carbon (Catar) was added to 300 ml of a saline solution of pH 2.3 containing 45 g/# of chlorate as Na CI Oz. Industrial ■ Manufacturing - 8/32 mesh) 150 - added to 103
The temperature was maintained at ℃, and the change in chlorate concentration was measured, and the results were as follows.
時間 Naα(h(g/N)
1時間後 26
2 〃16.5
5 〃1.5
実施例3
活性炭(キャタラ工業(IIIIWA−4/8メ・ノシ
ュ)IFMを充填したカラム(内径150 mm、高す
1300鶴)に、Naα03として30g/ Itの塩
素酸塩を含むpH2,3の食塩水を80℃、306 /
hで240時間連続通液した。流出液中の塩素酸塩濃
度はN a (j Ozとして平均27 g / jl
であった。Time Naα (h (g/N) 1 hour later 26 2 〃16.5 5 〃1.5 Example 3 Column (inner diameter 150 mm, A 1,300-inch tall crane) was heated with a saline solution of pH 2.3 containing 30 g/It of chlorate as Naα03 at 80°C.
The solution was continuously passed for 240 hours at h. The chlorate concentration in the effluent is N a (j Oz, with an average of 27 g/jl
Met.
実施例4
N a (J 03として45g/j!の塩素酸塩、及
び(J2として0.20g/nの有効塩素を含むρ11
6.5の食塩水300 mlに活性炭(キャタラL業■
製WA−4/Flメツシュ)150−を加えて110℃
に加熱維持したところ、1時間後の塩素酸塩濃度Cよ2
1g/lであった。Example 4 N a (ρ11 containing 45 g/j! of chlorate as J 03 and 0.20 g/n of available chlorine as (J2)
6.5 300 ml of saline solution and activated charcoal (Catara L Industry ■
WA-4/Fl mesh) 150- was added and heated to 110°C.
When heating was maintained for 1 hour, the chlorate concentration was C2
It was 1 g/l.
実施例5
NaC10xとして37g/eの塩素酸塩を含むpH2
,6の食塩水300 artに、活性炭(キャタラ工業
■製HA−4/8メツシュ)200mfを加え”ζ、耐
圧容器に充填し、加圧下に130℃に加熱維持したとこ
ろ、1時間後の塩素酸塩濃度はN a Q’ 03とし
て0.5 g/lであった。Example 5 pH2 containing 37 g/e chlorate as NaC10x
200 mf of activated carbon (HA-4/8 mesh manufactured by Catara Kogyo ■) was added to 300 art of the saline solution prepared in 6. The acid salt concentration was 0.5 g/l as N a Q'03.
比較例I
N a (J Ozとして45g/lの塩素酸塩を含む
pH2,1の食塩水300 ll11を85℃に加熱維
持したところ、3時間後の塩素酸塩濃度はNa(’JO
iとして44.5g/lであった。Comparative Example I When 300 liters of saline solution with a pH of 2.1 containing 45 g/l of chlorate in Na (JOz) was heated and maintained at 85°C, the chlorate concentration after 3 hours was Na('JO
i was 44.5 g/l.
比較例2
Na(JO,として31g/#の塩素酸塩を含むpl+
8.1の食塩水300−に、活性炭(キャタラ工業■製
HA−4/Rメツシュ)150IIIlを加えて90℃
に加熱維持したところ、3時間後の塩素酸塩濃度はNa
C1’Ozとして31g/71であった。Comparative Example 2 pl+ containing 31 g/# chlorate as Na (JO)
8. Add 150IIIL of activated carbon (HA-4/R mesh manufactured by Catara Kogyo ■) to 300℃ of the saline solution prepared at 90°C.
After 3 hours, the chlorate concentration was Na
It was 31g/71 as C1'Oz.
Claims (1)
接触させることを特徴とする塩素酸塩の分解方法。 2 接触温度が60〜130℃である特許請求の範囲第
1項記載の方法。 3 炭素が活性炭、木炭より選ばれた1種以上である特
許請求の範囲第1項記載の方法。 4 塩素の存在により反応を促進させる特許請求の範囲
第1項記載の方法。[Claims] 1. A method for decomposing chlorate, which comprises bringing acidic or neutral saline containing chlorate into contact with carbon. 2. The method according to claim 1, wherein the contact temperature is 60 to 130°C. 3. The method according to claim 1, wherein the carbon is one or more selected from activated carbon and charcoal. 4. The method according to claim 1, wherein the reaction is accelerated by the presence of chlorine.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22827585A JPS6287411A (en) | 1985-10-14 | 1985-10-14 | Method of decomposing chlorate |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22827585A JPS6287411A (en) | 1985-10-14 | 1985-10-14 | Method of decomposing chlorate |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6287411A true JPS6287411A (en) | 1987-04-21 |
| JPH0529605B2 JPH0529605B2 (en) | 1993-05-06 |
Family
ID=16873924
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP22827585A Granted JPS6287411A (en) | 1985-10-14 | 1985-10-14 | Method of decomposing chlorate |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6287411A (en) |
-
1985
- 1985-10-14 JP JP22827585A patent/JPS6287411A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0529605B2 (en) | 1993-05-06 |
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