JPS5944919B2 - How to remove heavy metals - Google Patents
How to remove heavy metalsInfo
- Publication number
- JPS5944919B2 JPS5944919B2 JP5943877A JP5943877A JPS5944919B2 JP S5944919 B2 JPS5944919 B2 JP S5944919B2 JP 5943877 A JP5943877 A JP 5943877A JP 5943877 A JP5943877 A JP 5943877A JP S5944919 B2 JPS5944919 B2 JP S5944919B2
- Authority
- JP
- Japan
- Prior art keywords
- iron
- heavy metals
- resin
- chelate
- type
- 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
Landscapes
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Water Treatment By Sorption (AREA)
Description
【発明の詳細な説明】
本発明は、廃水中にアニオンとして存在するクロム、バ
ナジン、ヒ素、モリブデン、タングステンなどの重金属
を吸着除去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 adsorbing and removing heavy metals such as chromium, vanadine, arsenic, molybdenum, and tungsten that exist as anions in wastewater.
さらに詳しく述べると、キレート形成基としてイミノプ
ロピオン酸鉄塩基および/もしくはイミノジプロピオン
酸鉄塩基を有する鉄盤キレート樹脂を用いて廃水中のア
ニオン性重金属を吸着させることを特徴とする廃水中の
重金属除去方法に関するものである。More specifically, heavy metals in wastewater are characterized in that anionic heavy metals in wastewater are adsorbed using an iron plate chelate resin having an iron base of iminopropionate and/or iron base of iminodipropionate as a chelate-forming group. This relates to a removal method.
通常、水銀、銅、カドミウム、亜鉛、鉛、銀、ニッケル
、コバルトなど多くの重金属は溶液中ではカチオンとし
て存在している場合が多く、中和凝集沈殿法、硫化物沈
殿法、イオン浮選法、イオン交換樹脂法、活性炭吸着法
などにより除去することが可能である。Normally, many heavy metals such as mercury, copper, cadmium, zinc, lead, silver, nickel, and cobalt often exist as cations in solution, and are processed using neutralization coagulation precipitation method, sulfide precipitation method, and ion flotation method. , ion exchange resin method, activated carbon adsorption method, etc.
しかしながら、クロム、バナジン、ヒ素、モリブデン、
タングステンなどの重金属は溶液中ではアニオンとして
存在し易く、前記の処理方法では除去することが極めて
困難である。However, chromium, vanadine, arsenic, molybdenum,
Heavy metals such as tungsten tend to exist as anions in solutions and are extremely difficult to remove using the treatment methods described above.
このような状況に鑑みて、本発明者らは、廃水中にアニ
オンの形で存在するクロム、バナジン、ヒ素、モリブデ
ン、タングステンなどの重金属を、装置が簡単で、操作
も容易であり、しかも有効かつ確実にこれらの重金属を
除去できる方法を見出すべく鋭意研究の結果、キレート
形成基としてイミノプロピオン酸鉄塩基および/もしく
はイミノジプロピオン酸鉄塩基を有する鉄型キレート樹
脂を用いて廃水中のアニオン性重金属を処理すると、著
しい除去効果を発揮し、はぼ完全にこれらの重金属を吸
着除去できることを発明した。In view of this situation, the present inventors have developed a method for removing heavy metals such as chromium, vanadine, arsenic, molybdenum, and tungsten, which are present in the form of anions in wastewater, using a simple device, easy to operate, and effective. As a result of intensive research to find a method that can reliably remove these heavy metals, we have found that anionic properties in wastewater can be reduced by using iron-type chelate resins containing iron iminopropionate and/or iron iminodipropionate as chelate-forming groups. The inventors have discovered that treatment of heavy metals has a remarkable removal effect and can almost completely adsorb and remove these heavy metals.
本発明をさらに詳細に説明すると、本発明で使用するキ
レート形成基としてイミノプロピオン酸鉄塩基および/
もしくはイミノジプロピオン酸鉄塩基を有するキレート
樹脂は、キレート形成基として下記に示すイミノプロピ
オン酸基(CII))および/もしくはイミノジプロピ
オン酸基(CID)を有するH型、Li型、Na型、K
型、Ca型、Mg型などのキレート樹脂に鉄イオン溶液
を反応させることにより容易に得ることができる。To explain the present invention in more detail, the chelate-forming groups used in the present invention include iminopropionate iron base and/or
Alternatively, the chelate resin having an iminodipropionic acid iron base is an H type, Li type, Na type, which has an iminopropionic acid group (CII) and/or an iminodipropionic acid group (CID) shown below as a chelate forming group. K
It can be easily obtained by reacting a chelate resin such as type, Ca type, or Mg type with an iron ion solution.
鉄イオン溶液としては、塩化第一鉄、塩化第二鉄、硫酸
第一鉄、硫酸第二鉄、硝酸第一鉄、硝酸第二鉄、臭化第
一鉄および臭化第二鉄などの溶液が使用できる。Examples of iron ion solutions include ferrous chloride, ferric chloride, ferrous sulfate, ferric sulfate, ferrous nitrate, ferric nitrate, ferrous bromide, and ferric bromide. can be used.
また、これらキレート樹脂の母体樹脂としては、フェノ
ール樹脂、エポキシ樹脂、ウレタン樹脂、メラミン樹脂
、塩化ビニル樹脂、スチレン−ジビニルベンゼン共重合
樹脂などが使用できる。Further, as the base resin for these chelate resins, phenol resin, epoxy resin, urethane resin, melamine resin, vinyl chloride resin, styrene-divinylbenzene copolymer resin, etc. can be used.
(ただし、RはH,Li 、Na 、に、Ca/2゜M
g/2を示す)
また、前記した鉄盤キレート樹脂に吸着除去されたアニ
オン性の重金属は、苛性ソーダ、食塩、塩酸、硝酸、硫
酸などの再生剤を使用することにより、容易に溶離(回
収)することができ、さらに再生された樹脂は繰り返し
使用することができることも大きな特徴である。(However, R is H, Li, Na, Ca/2゜M
In addition, the anionic heavy metals adsorbed and removed by the iron plate chelate resin described above can be easily eluted (recovered) by using a regenerating agent such as caustic soda, common salt, hydrochloric acid, nitric acid, or sulfuric acid. Another major feature is that the recycled resin can be used repeatedly.
以下実施例により詳細に説明するが、本発明はこれらの
実施例に限定されるものではない。The present invention will be described in detail below with reference to Examples, but the present invention is not limited to these Examples.
実施例 1
ミヨシ油脂■製のイミノプロピオン酸型キレート樹脂(
商品名[エポラスMX−8J樹脂母体がエポキシ樹脂と
してイミノプロピオン酸およびイミノジプロピオン酸基
を有するNa塩型)100麻を0.1%塩化第二鉄水溶
液500rrLl中に添加し、5時間攪拌後樹脂を良く
水洗して鉄(III)型キレート樹脂を得た。Example 1 Iminopropionic acid type chelate resin manufactured by Miyoshi Oil (
Product name: [Eporus MX-8J resin base is Na salt type having iminopropionic acid and iminodipropionic acid groups as epoxy resin] 100 hemp was added to 500 rrLl of 0.1% ferric chloride aqueous solution, and after stirring for 5 hours. The resin was thoroughly washed with water to obtain an iron (III) type chelate resin.
このNa型および鉄(III)型キレート樹脂それぞれ
10Inlをカラム(径15朋φ)に充填し、六価クロ
ムとして100p−のクロム酸水溶液(PH3)SV3
0、ダウンフローにて通液した。A column (diameter 15 mm) was filled with 10 Inl each of the Na type and iron (III) type chelate resin, and 100 p- of chromic acid aqueous solution (PH3) SV3 was used as hexavalent chromium.
0, the liquid was passed in a down flow manner.
流出液をフラクションコレクターにて20属ごとに分散
し、流出液中の残存六価クロムイオン濃度を原子吸光光
度法で測定した。The effluent was dispersed into 20 groups using a fraction collector, and the concentration of residual hexavalent chromium ions in the effluent was measured by atomic absorption spectrophotometry.
なお比較例として市販の強塩基性イオン交換樹脂の通液
も同様に行なった。As a comparative example, a commercially available strongly basic ion exchange resin was also passed through in the same manner.
第1図にこれらの通液結果を示す。第1図により明らか
なように、鉄イオン溶液と反応させる以前のNa型キレ
ート樹脂は六価クロムをほとんど吸着しないのに対し、
鉄([1)型キレート樹脂は市販の強塩基性イオン交換
樹脂にくらべて吸着量も大きく、除去下限も0.11]
In以下まテ六価クロムを除去でき、o、 i ppm
までの六価クロムの吸着量は47g/l−Rで、63p
pHlリークするまでの吸着量は51.0 g/ l−
R,wetであった。Figure 1 shows the results of these liquid passages. As is clear from Figure 1, the Na-type chelate resin before reacting with the iron ion solution hardly adsorbs hexavalent chromium.
Iron ([1) type chelate resin has a larger adsorption amount than commercially available strong basic ion exchange resins, and the lower limit of removal is 0.11]
Can remove hexavalent chromium below In, o, i ppm
The amount of hexavalent chromium adsorbed up to 47g/l-R is 63p.
The amount of adsorption until pHL leaks is 51.0 g/l-
It was R, wet.
実施例 2
実施例1で得られた鉄(III)型キレート樹脂にヒ素
(III)およびヒ素(V)の通液結果を示す。Example 2 The results of passing arsenic (III) and arsenic (V) through the iron (III) type chelate resin obtained in Example 1 are shown.
通液条件は実施例1と同様に行なった。The liquid passing conditions were the same as in Example 1.
なおヒ素(III)およびヒ素(V)の濃度はそれぞれ
1100ppで、pH8,0の水溶液を通液した。Note that the concentrations of arsenic (III) and arsenic (V) were each 1100 pp, and aqueous solutions with a pH of 8.0 were passed through the tube.
第2図にその結果を示す
実施例 3
実施例1で六価クロムを吸着した鉄(III)型キレー
ト樹脂に再生剤として5%苛性ソーダ水溶液を充填した
樹脂の6倍量使用して、SV2、ダウンフローで通液し
、六価クロムを溶離した。The results are shown in Figure 2. Example 3 Using 6 times the amount of the iron (III) type chelate resin that adsorbed hexavalent chromium in Example 1 and filling it with 5% caustic soda aqueous solution as a regenerant, SV2, The hexavalent chromium was eluted by passing the solution in a down flow manner.
溶離液中に回収された六価クロムの量は50.29/1
− R、we tで、回収率は98,4%以上であった
。The amount of hexavalent chromium recovered in the eluent was 50.29/1
-R, wet, the recovery rate was over 98.4%.
実施例 4
エチレンジアミン2プロピオン酸ナトリウム25&、レ
ヅルシン15gおよび37%ホルマリン40g、並びに
水300gを500m1ビーカーに仕込み、50℃で3
0分間攪拌し、プレポリマー水溶液をフィルム状に成形
し、130〜150℃にて10時間加熱して硬化樹脂を
得た。Example 4 A 500ml beaker was charged with 25% sodium ethylenediamine dipropionate, 15g of redulucin, 40g of 37% formalin, and 300g of water, and heated at 50°C for 30 minutes.
After stirring for 0 minutes, the aqueous prepolymer solution was formed into a film, and heated at 130 to 150°C for 10 hours to obtain a cured resin.
得られた硬化樹脂は10〜48メツシユに粉砕した。The obtained cured resin was pulverized into 10 to 48 meshes.
このようにして得られたlO〜48メ゛ンシュのイミノ
プロピオン酸ナトリウム塩型キレート樹脂50gをo、
i%硝酸第二鉄水溶液500rnl中に添加し、30分
間反応させ、得られた鉄(III)型キレート樹脂を良
く水洗し、通液試験に供した。50 g of the thus obtained lO~48 mesh iminopropionate sodium salt type chelate resin was
It was added to 500 rnl of an i% ferric nitrate aqueous solution and reacted for 30 minutes, and the obtained iron (III) type chelate resin was thoroughly washed with water and subjected to a liquid passage test.
実施例1と同様の通液条件では0.1ppl[lまでの
六価クロムがリークするまでの通液倍率(l/l−R,
wet )は520倍であった。Under the same liquid passing conditions as in Example 1, the liquid passing rate (l/l-R,
wet) was 520 times.
第1図および第2図は重金属の吸着性能を示す説明図で
ある。FIG. 1 and FIG. 2 are explanatory diagrams showing the adsorption performance of heavy metals.
Claims (1)
))および/もしくはイミノジプロピオン酸基((II
))を有するキレート樹脂に、鉄イオン溶液を反応させ
て得られるキレート形成基としてイミノプロピオン酸鉄
塩基および/もしくはイミノジプロピオン酸鉄塩基を有
する鉄盤キレート樹脂を用いて溶液中にアニオンとして
存在する重金属を吸着除去することを特徴とする重金属
の除去方法。 (ただし、RはH,Li 、Na 、に、Ca/2゜M
g/2を示す)[Claims] 1 Iminopropionic acid group ((1
)) and/or iminodipropionic acid groups ((II
)) is present as an anion in the solution using an iron plate chelate resin having iminopropionate iron base and/or iminodipropionate iron base as a chelate forming group obtained by reacting an iron ion solution with a chelate resin having iron ion solution. A method for removing heavy metals, characterized by adsorbing and removing heavy metals. (However, R is H, Li, Na, Ca/2゜M
g/2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5943877A JPS5944919B2 (en) | 1977-05-24 | 1977-05-24 | How to remove heavy metals |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5943877A JPS5944919B2 (en) | 1977-05-24 | 1977-05-24 | How to remove heavy metals |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS53145351A JPS53145351A (en) | 1978-12-18 |
| JPS5944919B2 true JPS5944919B2 (en) | 1984-11-01 |
Family
ID=13113272
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP5943877A Expired JPS5944919B2 (en) | 1977-05-24 | 1977-05-24 | How to remove heavy metals |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5944919B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP3999596B2 (en) * | 2002-08-02 | 2007-10-31 | 中部キレスト株式会社 | Arsenic-trapping fiber and arsenic-containing water treatment method using the same |
| JP5030129B2 (en) * | 2005-06-23 | 2012-09-19 | 株式会社ジー・ピー・ワン | High speed arsenic adsorbing material and method for producing the same |
-
1977
- 1977-05-24 JP JP5943877A patent/JPS5944919B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS53145351A (en) | 1978-12-18 |
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