JPH02233196A - Material for decoloring and cleaning of water and its preparation - Google Patents
Material for decoloring and cleaning of water and its preparationInfo
- Publication number
- JPH02233196A JPH02233196A JP5375289A JP5375289A JPH02233196A JP H02233196 A JPH02233196 A JP H02233196A JP 5375289 A JP5375289 A JP 5375289A JP 5375289 A JP5375289 A JP 5375289A JP H02233196 A JPH02233196 A JP H02233196A
- Authority
- JP
- Japan
- Prior art keywords
- water
- manganese dioxide
- mno2
- gamma
- decoloring
- 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.)
- Pending
Links
Landscapes
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Removal Of Specific Substances (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野]
本発明は脱色浄水材及びその製造方法に関し、更に詳し
くは井水、河川水、地下水等に含まれる芒色成分等を除
去するγ型二酸化マンガンから成る脱色浄水材及びその
製造方法に関するものである。[Detailed Description of the Invention] [Industrial Field of Application] The present invention relates to a decolorizing water purifying material and a method for producing the same, and more specifically to γ-type dioxide for removing amber components contained in well water, river water, ground water, etc. The present invention relates to a decolorizing water purifying material made of manganese and a method for producing the same.
[従来の技術]
近年、環境汚染とくに廃水による水質汚染は著しく、井
水、河川水、地下水等の天然水がしばしばる色する現象
がみられる。[Prior Art] In recent years, environmental pollution, particularly water pollution caused by wastewater, has become significant, and natural waters such as well water, river water, and groundwater often turn discolored.
これらの青色原因には、鉄,マンガンあるいは硬度成分
などのコロイド状微粒子に起因するもの、フミン酸に起
因するものがあり、これらの除去装置も種々考案されて
いる。These blue colors include those caused by colloidal fine particles such as iron, manganese, or hardness components, and those caused by humic acid, and various removal devices have been devised.
口本全国で、水道法の水質基桑による色度が20度以上
の原水は約340万1・ン/日(水道統計一昭和62年
発行)存t1するとされているが、一般家庭での用水は
、色度5度以下と定められており、この原水をいかに効
率良く上水化することができるかが急務とされている。In Japan, raw water with a chromaticity of 20 degrees or higher according to the water quality standard mulberry under the Water Supply Law is said to exist at approximately 3,400,000 tons/day (Water Supply Statistics I published in 1986), but Commercial water is specified to have a chromaticity of 5 degrees or less, and there is an urgent need to find a way to efficiently convert this raw water into clean water.
従来、原水処理方法として、オゾンや酸化剤を用いた酸
化法、活性炭による方法、接触濾過法、凝集沈殿法等が
一般的である。Conventionally, common raw water treatment methods include an oxidation method using ozone or an oxidizing agent, a method using activated carbon, a contact filtration method, and a coagulation sedimentation method.
しかし、これらの方法には次の様な問題点がある。即ち
、酸化法は、コストが高い上、用いる処理剤1こよって
は大気汚染の危険がある。活性炭による方法は、原水中
に(′7−■するマンガン分,鉄分に対する活性炭の吸
管能が低く、更に着色成分の脱色能力も高いものではな
い。接触濾過法はこの方法で通常用いられる浄化材、例
えば、ゼオライ1・表面に二酸化マンガンを添着させた
もの等は高価である上に、二酸化マンガンの付着力が弱
いため、二酸化マンガンの脱離・流出による損失劣化が
激しい。また、凝集沈殿法では着色成分が多くなる程、
汚染の発生量が多くなるのt1大規模な汚染処理設備が
必要になりコストが高くなる等々である。However, these methods have the following problems. That is, the oxidation method is expensive, and there is a risk of air pollution due to the processing agent used. In the method using activated carbon, activated carbon has a low suction ability for the manganese and iron contents ('7-■) in raw water, and also does not have a high ability to decolorize colored components. For example, zeolite 1, which has manganese dioxide attached to its surface, is expensive, and the adhesion of manganese dioxide is weak, resulting in severe loss and deterioration due to desorption and outflow of manganese dioxide.Also, coagulation-precipitation method So, the more coloring ingredients there are, the more
As the amount of pollution generated increases, large-scale pollution treatment equipment becomes necessary and costs increase.
[発明が解決するための課2l!¥i]本発明は、上記
した問題点が比較的少なく、効率の良い水の脱色浄水材
を提供することを目的とするものである。[Lesson 2l for inventions to solve! ¥i] An object of the present invention is to provide an efficient water decolorizing water purifying material that has relatively few of the above-mentioned problems.
[課題を解決する手段]
本発明者等は、二酸化マンガンを用いた浄水材について
種々検討を重ねた結果、酸性溶液で処理したγ二酸化マ
ンガンを或条件で加熱することによりミγ二酸化マンガ
ンから成る効率の良い浄水材が得られることを見い出し
、本発明を完成した。[Means for Solving the Problems] As a result of various studies on water purification materials using manganese dioxide, the inventors of the present invention discovered that by heating γ-manganese dioxide treated with an acidic solution under certain conditions, a material made of γ-manganese dioxide can be produced. They discovered that an efficient water purifying material could be obtained and completed the present invention.
即ち本発明は、γ型二酸化マンガンを硫酸酸性溶液で混
練し、加湿雰囲気で加熱して得る成形γ型二酸化マンガ
ンから成る脱色浄水材に関するものである。That is, the present invention relates to a decolorizing water purifying material made of shaped γ-type manganese dioxide obtained by kneading γ-type manganese dioxide with an acidic sulfuric acid solution and heating the mixture in a humid atmosphere.
次に本発明を更に説明する。Next, the present invention will be further explained.
二酸化マンガンが岩色水の脱色効果を持つことは従来か
ら一般に認められているが、電解二酸化マンガンのブロ
ックを単に粗砕し整拉したものは、有効な反応表面積が
小さく、またこれを無機質バインダーによって成形した
ものは活性な二酸化マンガン表面がバインダーによって
覆われるため脱色効果が劣るという問題がある。また、
二酸化マンガンには3種の結晶型があり、水の廿色成分
の一つである例えばフミン酸に対しての分解能は次の通
りであることが知られている。It has long been generally accepted that manganese dioxide has the effect of decolorizing rock-colored water, but blocks of electrolytic manganese dioxide that have been simply crushed and processed have a small effective reaction surface area, and they cannot be used as inorganic binders. The problem with molded products is that the active manganese dioxide surface is covered with the binder, resulting in poor decolorizing effect. Also,
It is known that there are three types of crystalline forms of manganese dioxide, and the resolution of humic acid, which is one of the color components of water, is as follows.
7 −MnO > a −MnO ≧β−M n0
2本発明名等は、γ−Mn02粉末をバインダーを用
いることなく、取扱い上好ましい形状で得る方法を検討
した結果、以下の方法を見い出した。7 -MnO > a -MnO ≧β-M n0
2 The present inventors investigated a method for obtaining γ-Mn02 powder in a shape suitable for handling without using a binder, and as a result, discovered the following method.
■)原料のγ−Mn02粉末に酸性溶液を加えて混練し
、?の混練物を加湿状態で加熱する方法、2)原料のγ
−MnO■粉末に所定の酸性溶液を加え混練し、あらか
じめ造粒(例えば20〜42メッシュ)し、この造粒物
を加湿状態で加熱する方法である。■) Add an acidic solution to the raw material γ-Mn02 powder and knead it. A method of heating the kneaded material in a humidified state, 2) γ of the raw material
In this method, a predetermined acidic solution is added to MnO* powder, kneaded, granulated in advance (for example, 20 to 42 mesh), and the granulated product is heated in a humidified state.
このような方法により、マクロ的にボーラスでしかも強
度があり、表面が活性な成形γ−M n0 2が得られ
ることを見い出した。It has been found that by such a method, molded γ-M n0 2 that is macroscopically bolus, strong, and has an active surface can be obtained.
即ち、本発明は、γ−M nO 2を、酸性溶液を用い
て処理したものを加熱処理し、ボーラスな成形γ−M
n 0 2からなる浄水剤とすることが特徴である。That is, the present invention heat-treats γ-M nO 2 using an acidic solution to form a bolus shaped γ-M
It is characterized by being a water purifying agent consisting of n 0 2.
本発明で用いるγ−M n0 2は、好ましくは電解に
より得られるもので、その粒度は200〜400メッシ
ュのものである。又、このγ−MnO。を酸性溶液と混
合して混練するが、この混練時に加える酸性溶液は好ま
しくは金属イオン等の他の陽イオンを含まない(例えば
比抵抗ioxto’Ω・C■以上の純水の)硫酸酸性溶
液で、その使用量は、γ−MnO。γ-M n0 2 used in the present invention is preferably obtained by electrolysis and has a particle size of 200 to 400 mesh. Also, this γ-MnO. is mixed with an acidic solution and kneaded. The acidic solution added during this kneading is preferably a sulfuric acid acidic solution that does not contain other cations such as metal ions (for example, pure water with a specific resistance of ioxto'Ω・C■ or more). The amount used is γ-MnO.
100重量部に対してlO〜30重量部であり、用いる
硫酸酸性溶液の濃度は5〜lOg/ 1のものが好まし
い。本発明では上記混練物のまま又はこれを通常の方法
で粒状、ベレット状に成形したものを加熱するが、この
際、加湿状態で加熱することにより、i゛1られた浄水
材を水と桜触させて用いた際も崩壊することのない成形
体とすることができる。また、上記混練物を単に大気中
で加熱したものは、水分が直ちに蒸発し、粒間固化が進
まず、もろい塊状または粒状物としかならない。It is 10 to 30 parts by weight per 100 parts by weight, and the concentration of the sulfuric acid acidic solution used is preferably 5 to 10 g/1. In the present invention, the above-mentioned kneaded product is heated as it is, or it is formed into granules or pellets using a conventional method. At this time, by heating in a humidified state, the i゛1 water purifying material is mixed with water. A molded article that does not disintegrate even when touched and used can be obtained. Furthermore, if the above-mentioned kneaded product is simply heated in the atmosphere, the moisture will immediately evaporate, intergranular solidification will not proceed, and the product will only become brittle lumps or granules.
又、本発明の浄水材は、前記したようにγ一MnO2か
ら成ることが特徴であるが、本発明の加熱条件を調整す
ることによりこのようなγ一MnO2から成り強固な浄
水材とすることが出来る。Further, the water purifying material of the present invention is characterized by being made of γ-MnO2 as described above, but by adjusting the heating conditions of the present invention, it is possible to make a strong water purifying material made of such γ-MnO2. I can do it.
上記加熱処理の条件は、常圧において温度90〜100
℃、相対湿度90%以上に保ち1時間〜40時間の処理
時間で処理する。また、成形物を加熱する際は若干の加
圧を行うと、一層強固な成形体となる。この際の加圧条
件は30〜l00paである。The conditions for the above heat treatment are a temperature of 90 to 100 at normal pressure.
℃ and relative humidity of 90% or higher, and the treatment time is from 1 hour to 40 hours. Moreover, if a slight amount of pressure is applied when heating the molded product, the molded product will become even stronger. The pressurizing conditions at this time are 30 to 100 pa.
このような方法により、マクロ的にボーラスでしかも強
度があり、表面が活性な成形γ−M n0 2が得られ
る。本発明の浄水材は.、このもののX線回折から略1
00%のγ−Mn02から成ることが確認できる。By such a method, a molded γ-M n0 2 which is macroscopically bolus, strong and surface active is obtained. The water purifying material of the present invention is. , from the X-ray diffraction of this material, approximately 1
00% of γ-Mn02.
[発明の効果]
以上述べたように、本発明はこれを水中でも長時間使用
しても原型を保ち又脱色効果も高い。また比較的簡便な
工程で活性なγ−MnO2からなる成形脱色浄水材が得
られる。[Effects of the Invention] As described above, the present invention maintains its original shape even when used underwater for a long time, and has a high decolorizing effect. Furthermore, a molded decolorizing water purifying material made of active γ-MnO2 can be obtained through a relatively simple process.
[実施例]
以下に実施例を述べるが、本発明はこれに限られるもの
ではない。[Example] Examples will be described below, but the present invention is not limited thereto.
実施例1
320メッシュの電解二酸化マンガン5kgをII2S
O410g#!の酸性溶液1i用いて混練後、この混練
物を相対湿度95%の加湿状態に保ったまま100℃で
50KPaの加圧下で24時間加熱処理を行い、塊状二
酸化マンガンを得た。このものを水洗し、その後苛性ソ
ーダにて中和し20〜40メッシュの浄水祠を得た。i
リられな材のX線回折パターンを図1に示す。Example 1 5 kg of 320 mesh electrolytic manganese dioxide was
O410g#! After kneading using the acidic solution 1i, the kneaded product was heat-treated at 100° C. for 24 hours under a pressure of 50 KPa while keeping it in a humidified state with a relative humidity of 95% to obtain bulk manganese dioxide. This material was washed with water and then neutralized with caustic soda to obtain a 20-40 mesh water purification cage. i
The X-ray diffraction pattern of the recycled wood is shown in Figure 1.
実施例2
320メッシュの電解二酸化マンガン5kgを11。S
O4+og/βの酸性溶液11で混練後、この混練物を
20〜40メッシュの粒状二酸化マンガンとした。この
造粒物を相対湿度95%の加湿状態で100℃でIO時
間加熱処理を行い、原料と同形状の粒状二酸化マンガン
をWjた。さらに、これを水洗し、その後苛性ソーダに
て中和を行い浄水祠を得た。Example 2 5 kg of 320 mesh electrolytic manganese dioxide was added to 11. S
After kneading with an acidic solution 11 of O4+og/β, the kneaded product was made into granular manganese dioxide of 20 to 40 mesh. This granulated product was heat-treated at 100° C. for 10 hours in a humidified state with a relative humidity of 95% to obtain granular manganese dioxide having the same shape as the raw material. Furthermore, this was washed with water, and then neutralized with caustic soda to obtain a purified water shrine.
得られた剤のX線回折パターンを図−2に示す。The X-ray diffraction pattern of the obtained agent is shown in Figure 2.
比較例1
320メッシュの電解二酸化マンガン5kgを、K
SO lOg#!、I+,, SO410g#!の酸
性溶液11’で混練後、造粒し(20〜40メッシュ)
この造粒物を+11対湿度95%の加湿状態に保ったま
ま100℃で72時間加熱処理を行い、粒状二酸化マン
ガンを得た。このものを水洗し、その後苛性ソーダにて
中和し浄水材を得た。得られた材のX線回折パターンか
らこのものはα−M n 0 2を含むものであった。Comparative Example 1 5 kg of 320 mesh electrolytic manganese dioxide was
SO lOg#! , I+,, SO410g#! After kneading with acidic solution 11', granulate (20 to 40 mesh)
This granulated product was heated at 100° C. for 72 hours while being kept in a humidified state of +11 to 95% humidity to obtain granular manganese dioxide. This material was washed with water and then neutralized with caustic soda to obtain a water purifying material. The X-ray diffraction pattern of the obtained material showed that it contained α-M n 0 2 .
比較例2
32ロメッシュの電解二酸化マンガン5kgをK S
O 10g/i、II2SO410g/4の酸性溶液
1flて混練後、造粒し(20〜40メッシュ)この造
粒物をト11対湿度95%の加湿状態に保ち100℃で
100時間加熱処理を行い、粒状二酸化マンガンを得た
。Comparative Example 2 5 kg of electrolytic manganese dioxide of 32 romesh was added to K S
After kneading with 1 fl of an acidic solution containing 10 g/i of O and 10 g/4 of II2SO4, it was granulated (20 to 40 mesh), and the granulated product was kept in a humidified state with a humidity of 95% and heat-treated at 100°C for 100 hours. , granular manganese dioxide was obtained.
さらに、水洗を行い、その後苛性ソーダにて中和を行う
ことにより浄水材を得た。得られた材はX線回折パター
ンからβ−MnO2を含むものであった。Furthermore, water purification material was obtained by washing with water and then neutralizing with caustic soda. The obtained material contained β-MnO2 from the X-ray diffraction pattern.
実施例3
実施例及び比較例.により得られた浄水材を使用しこれ
らの性能比較実験を行った。Example 3 Example and comparative example. We conducted a performance comparison experiment using the water purifying material obtained by the method.
実験は、カラムを川い、S V − 10(*)で、7
日間の通水テストであり、その7日間通水後の処理水で
比較評価を行った。In the experiment, the column was washed with SV-10 (*) at 7.
This was a water flow test for 7 days, and a comparative evaluation was performed using the treated water after water flow for 7 days.
* S V (Space Velocity) [
l/l+r ]:空間速度で、1時間当りに 層を通
過する水量を浄水材の量で除した値。*SV (Space Velocity) [
l/l+r]: Space velocity, the value obtained by dividing the amount of water passing through the layer per hour by the amount of water purifying material.
ただし、塩素添加量はlOmg/ 1である。However, the amount of chlorine added was 10mg/1.
結果を表−1に示す。表一lより、比較例1,2に比べ
、実施例1.2の脱色効果が優れていることがひ判る。The results are shown in Table-1. From Table I, it is clear that the decolorizing effect of Example 1.2 is superior to that of Comparative Examples 1 and 2.
図−1〜4 は順に実施例1、 実施例2、 比較例1、 図面の浄書(内容に変更なし) 比較例2で得られた洗浄剤のX線回折,<ターンを図 示す図である。 Figures 1 to 4 In order, Example 1, Example 2, Comparative example 1, Engraving of drawings (no changes to content) X-ray diffraction of the cleaning agent obtained in Comparative Example 2. FIG.
Claims (1)
成形γ型二酸化マンガンから成る脱色浄水材。 2)γ型二酸化マンガンを硫酸酸性溶液で混練し、加湿
雰囲気で加熱し成形することを特徴とするγ型二酸化マ
ンガンから成る脱色浄水材の製造方法。 3)硫酸酸性溶液で混練し造粒したものを加湿雰囲気で
加熱する特許請求の範囲第2)項記載の製造方法。[Scope of Claims] 1) A decolorizing water purifying material made of molded γ-type manganese dioxide kneaded with an acidic sulfuric acid solution and heated under pressure in a humid atmosphere. 2) A method for producing a decolorizing water purifying material made of γ-type manganese dioxide, which comprises kneading γ-type manganese dioxide with an acidic sulfuric acid solution, heating and molding the mixture in a humidified atmosphere. 3) The manufacturing method according to claim 2), wherein the granulated product is kneaded with an acidic sulfuric acid solution and heated in a humid atmosphere.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5375289A JPH02233196A (en) | 1989-03-08 | 1989-03-08 | Material for decoloring and cleaning of water and its preparation |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5375289A JPH02233196A (en) | 1989-03-08 | 1989-03-08 | Material for decoloring and cleaning of water and its preparation |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH02233196A true JPH02233196A (en) | 1990-09-14 |
Family
ID=12951544
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP5375289A Pending JPH02233196A (en) | 1989-03-08 | 1989-03-08 | Material for decoloring and cleaning of water and its preparation |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH02233196A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4786771B2 (en) * | 2009-03-24 | 2011-10-05 | 株式会社アサカ理研 | Water treatment method and water treatment system |
-
1989
- 1989-03-08 JP JP5375289A patent/JPH02233196A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4786771B2 (en) * | 2009-03-24 | 2011-10-05 | 株式会社アサカ理研 | Water treatment method and water treatment system |
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