JPS6071081A - Removal of organic compound in water - Google Patents

Removal of organic compound in water

Info

Publication number
JPS6071081A
JPS6071081A JP17959983A JP17959983A JPS6071081A JP S6071081 A JPS6071081 A JP S6071081A JP 17959983 A JP17959983 A JP 17959983A JP 17959983 A JP17959983 A JP 17959983A JP S6071081 A JPS6071081 A JP S6071081A
Authority
JP
Japan
Prior art keywords
filter bed
activated carbon
water
compounds
activated carbons
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
Application number
JP17959983A
Other languages
Japanese (ja)
Inventor
Hiromoto Uejima
植嶋 宏元
Tomonari Kakishita
垣下 智成
Koichiro Nakai
中井 浩一郎
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Unitika Ltd
Original Assignee
Unitika Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Unitika Ltd filed Critical Unitika Ltd
Priority to JP17959983A priority Critical patent/JPS6071081A/en
Publication of JPS6071081A publication Critical patent/JPS6071081A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To remove various kinds of org. compounds mixed in water with good efficiency, by passing water containing org. compounds through a filter bed, which is formed by packing activated carbons different in specific gravity in a laminar form, so as to traversely cross said filter bed. CONSTITUTION:Two kinds of activated carbons, of which the specific gravity is set to a range of 0.2-0.6g/ml by the baking or activating condition of a generally used petroleum pitch type activated carbon stock material are prepared from said stock material and these activated carbons different in the specific gravity are packed in a laminar form to form a filter bed. Water containing org. compounds is passed through this filter bed in an upward or downward stream. 1-80wt% of oxide or hydroxide of Na, K, Mg or Ca can be mixed in the aforementioned activated carbons. In addition, as the aforementioned activated carbons, ones receiving acid washing using an acid such as hydrochloric acid are suitably used. The height of the activated carbon packing layer in forming the filter bed is suitably selected in a range of 0.5-4m.

Description

【発明の詳細な説明】 本発明は、水中の有機化合物の除去方法に関するもので
あり、さらに詳しくは比重の異なる活性炭を層状に充填
して濾床を形成し、該濾床を縦断して有機化合物を含有
する水を通水することを特徴とする水中の有機化合物の
除去方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing organic compounds from water. More specifically, the present invention relates to a method for removing organic compounds from water. The present invention relates to a method for removing organic compounds in water, which is characterized by passing water containing the compounds through the water.

従来、活性炭は水中の有機化合物の吸着除去剤として広
範囲に利用され、実用に供せられている。
Activated carbon has been widely used and put to practical use as an adsorbent and remover for organic compounds in water.

なかでも水の高次処理に汎用化のある吸着剤とされてい
る。然るに、近年1分析技術が進歩し、水処理技術が一
層高度化してきたために、従来のように単に活性炭で処
理するのみでは水中の全ての有機化合物を吸着除去する
ことが不可能であることが明らかになってきた。さらに
詳述すれば有機化合物の分子量の差異、立体構造差異等
の物理的な観点ならびにイオン性、親水性、疎水性、或
いは金属との化合性等の化学的な観点より考察すると、
単に活性炭で処理することにより、上記特性が種々異な
る各種化合物、たとえば、多価アルコール頬、ベンゼン
等の芳香族化合物、ハロゲン化アルキル類、脂肪族化合
物類等夫々を十分満足に除去することは不可能といって
も過言ではない。
Among these, it is said to be a versatile adsorbent for high-level water treatment. However, in recent years, as analysis technology has advanced and water treatment technology has become more sophisticated, it has become impossible to adsorb and remove all organic compounds in water simply by treating it with activated carbon as in the past. It's becoming clear. More specifically, when considered from a physical perspective such as differences in molecular weight and steric structure of organic compounds, and from a chemical perspective such as ionicity, hydrophilicity, hydrophobicity, or compatibility with metals,
It is not possible to completely and satisfactorily remove various compounds with different properties such as polyhydric alcohols, aromatic compounds such as benzene, alkyl halides, and aliphatic compounds by simply treating with activated carbon. It is no exaggeration to say that it is possible.

そこで1本発明者らは、鋭意研究の結果、比重を異にし
た活性炭を層状に充填した濾床を形成させることにより
、水中に広範囲にわたる種類の有機化合物が混在してい
てもそれらの除去が可能となることを見出し1本発明に
到達したものである。
As a result of intensive research, the inventors of the present invention discovered that by forming a filter bed filled with layers of activated carbon with different specific gravity, it was possible to remove a wide range of organic compounds even if they were mixed in water. The present invention was achieved by discovering that this is possible.

従来の単一の活性炭層を利用する吸着法によれば、活性
炭層への有機化合物含有水の通水によって、粗大な夾雑
物による濾床閉塞を生じて逆洗等を行なわざるを得な(
なった場合、有機化合物の吸着により形成された。いわ
ゆる吸着帯が破壊されるのに対し9本発明のごとく吸着
剤層が比重差を有する活性炭で形成されている場合ば逆
洗前とほとんど同一の吸着帯の状態にもどすことが容易
であり、続く通水工程でも効果的な吸着除去特性を持続
し、吸着剤の長寿命化を図ることができる。
According to the conventional adsorption method that uses a single activated carbon layer, when water containing organic compounds is passed through the activated carbon layer, the filter bed is clogged with coarse impurities, making it necessary to perform backwashing, etc.
If so, it was formed by adsorption of organic compounds. Whereas the so-called adsorption zone is destroyed, if the adsorbent layer is made of activated carbon with a difference in specific gravity as in the present invention, it is easy to restore the adsorption zone to almost the same state as before backwashing. Effective adsorption and removal properties can be maintained even during the subsequent water passage process, and the life of the adsorbent can be extended.

また、単一の活性炭層による吸着では、いったん活性炭
に吸着した有機化合物が他の有機化合物により置換され
、追い出される減少がしばしば起きるのに対し3本発明
方法によれば、比重の異なる各層の活性炭層々が異なる
有機化合物を吸着し。
In addition, in adsorption using a single activated carbon layer, organic compounds that have been adsorbed on the activated carbon are replaced by other organic compounds and are often driven out. The layers adsorb different organic compounds.

効率良く有機化合物を除去することができる。比重差を
持った層の形成による本発明の他の利点として、吸着破
過した吸着剤の再生利用に際して。
Organic compounds can be removed efficiently. Another advantage of the present invention due to the formation of layers with different specific gravity is in the recycling of adsorbent that has passed through adsorption.

夫々の活性炭を分別して取り出すことができ、夫々に適
した再生賦活を実施することができることである。
It is possible to separate and take out each type of activated carbon, and to carry out regeneration and activation suitable for each type of activated carbon.

本発明の方法に用いる比重の異なる活性炭は。Activated carbons with different specific gravities are used in the method of the present invention.

通常の活性炭製造における賦活条件を変えることにより
製造しうろことはよく知られている。
It is well known that scales can be produced by changing the activation conditions in conventional activated carbon production.

本発明においては、さらに他の成分を混合して比重を異
なるようにした活性炭も使用することができる。すなわ
ち、活性炭は一般に用いられる原料がヤシ核系2石炭系
1石油ピンチ系、木質系であるが、その焼成条件あるい
は賦活条件により見掛比重(充填密度表示)を0.2乃
至0.6g/lI+7!の範囲で任意に設定できる。他
成分の混合においては充填密度を0.5乃至]、、5 
g/ mj!の範囲で任意調整できる。混合しうる成分
としては、Na+ K +Mgl Ca、Ba、Sr、
TI+ Mn、Fe+ Zr+、八l、S+、 Sh+
pb等の単独又は複数の酸化化合物1水酸化化合物。
In the present invention, activated carbon having different specific gravity by mixing other components can also be used. In other words, the raw materials generally used for activated carbon are coconut kernel, coal, petroleum, and wood, but depending on the firing or activation conditions, the apparent specific gravity (indication of packing density) may range from 0.2 to 0.6 g/ lI+7! Can be set arbitrarily within the range. When mixing other components, the packing density should be 0.5 to 5.
g/mj! It can be adjusted arbitrarily within the range. Mixable components include Na + K + Mgl Ca, Ba, Sr,
TI+ Mn, Fe+ Zr+, 8l, S+, Sh+
Single or multiple oxidized compounds monohydroxide compounds such as pb.

炭酸化合物の単独又は混合物等があげられる。好ましい
具体例を示すと+ MgO+ CaO+ 7’+O* 
+Fea 03 + Fe3O4+ 八I2 03 +
 SiO21MgCO31CaCOa + Nag O
・Alx 03 5t0211x O系化合物+ Mg
6 ・Ah (Oll) 16・Co、・41h O系
化合物等があげられる。混合物の種類及びその混合割合
は被吸着有機化合物の種類及び要求比重によって異なる
が、混合物の混合量は通常、活性炭に対して1乃至80
重量%でよい。さらに上記混合物以外に、必要に応じて
それらの結合剤として、ポリビニルアルコール、糖蜜、
タールピッチ等を混入し強度を与える他、細孔を多く有
する吸着剤とすることもできる。
Examples include carbonate compounds alone or in mixtures. A preferred specific example is + MgO+ CaO+ 7'+O*
+Fea 03 + Fe3O4+ 8I2 03 +
SiO21MgCO31CaCOa + Nag O
・Alx 03 5t0211x O-based compound + Mg
Examples include 6.Ah (Oll) 16.Co, .41h O-based compounds, and the like. The type of mixture and its mixing ratio vary depending on the type of organic compound to be adsorbed and the required specific gravity, but the amount of the mixture is usually 1 to 80% based on activated carbon.
Weight % is sufficient. In addition to the above mixtures, polyvinyl alcohol, molasses,
In addition to adding tar pitch or the like to give strength, it can also be made into an adsorbent with many pores.

本発明に用いられる活性炭は前述のように製造に際して
焼成または賦活が行われるが、それらを還元状態で行う
ことにより、有機化合物の吸着性能を向上させるととも
に、従来の活性炭では除去しにくかった有機化合物をも
除去しうるようになしうる。還元雰囲気ガスの1例とし
て、水素および/または一酸化炭素を含むガスがあげら
れる。
The activated carbon used in the present invention is fired or activated during production as described above, but by performing these processes in a reduced state, it improves the adsorption performance of organic compounds and also removes organic compounds that are difficult to remove with conventional activated carbon. It can be made so that it can also be removed. An example of the reducing atmosphere gas is a gas containing hydrogen and/or carbon monoxide.

さらには活性炭を還元処理しても同様の効果かえられる
。たとえば活性炭を0.1wt%水溶液を用いて20℃
で6時間処理してもよい。
Furthermore, similar effects can be obtained by reducing activated carbon. For example, using activated carbon in a 0.1 wt% aqueous solution at 20°C.
It may be treated for 6 hours.

本発明に用いられる活性炭は、また、酸洗浄されたもの
であるこが好ましい。酸としては、塩酸。
The activated carbon used in the present invention is also preferably acid-washed. The acid is hydrochloric acid.

弗酸が好ましく用いられる。洗浄法としては、塩酸の場
合、たとえば5wt%水溶液中20℃で、3時間浸漬す
ればよい。必要に応じて、同様の洗浄を繰り返すと一層
良好な吸着特性が得られる。弗5− 酸の場合には、たとえば、20wt%水溶液中2゜°C
で3時間浸漬すればよく、塩酸洗浄後同様の浸漬をすれ
ば吸着性能が格段に向上する。いずれの場合にも浸漬後
、十分に水洗を行うことが好ましい。
Hydrofluoric acid is preferably used. In the case of hydrochloric acid, the cleaning method may be, for example, immersion in a 5 wt % aqueous solution at 20° C. for 3 hours. Even better adsorption properties can be obtained by repeating similar washing as necessary. In the case of fluoro5-acid, for example, at 2°C in a 20 wt% aqueous solution.
It is sufficient to immerse the material in water for 3 hours, and if the same immersion is performed after washing with hydrochloric acid, the adsorption performance will be significantly improved. In either case, it is preferable to thoroughly wash with water after immersion.

本発明は、比重の異なる活性炭を塔或いは濾過池に充填
して形成した濾床を用いるものであるが。
The present invention uses a filter bed formed by filling a column or a filter basin with activated carbon having different specific gravity.

充填層の高さは、0.5乃至4mの範囲で処理水の目標
水質及び損失水頭等を考慮し任意に選ぶことが好ましい
。比重の異なる活性炭の種類は2種乃至4種で十分であ
るが、必要に応じてそれ以上であってもい。なお、各層
の活性炭の層の高さは用途に応じて同一であってもよく
、また夫々異なった高さとすることもできる。
It is preferable that the height of the packed bed is arbitrarily selected within the range of 0.5 to 4 m in consideration of the target water quality of the treated water, head loss, etc. Two to four types of activated carbon having different specific gravities are sufficient, but more than that may be used if necessary. Note that the height of each activated carbon layer may be the same or different depending on the purpose.

濾床への通水は上向流、下向流いずれでもよいが、下向
流が好ましい。上向流においては比重の小さい上層部の
みを流動床として通水することも可能である。通水によ
り損失水頭が増大した場合は、逆洗を行なえばよい。長
期間の使用により。
Water may be passed through the filter bed either upwardly or downwardly, but preferably downwardly. In the case of upward flow, it is also possible to pass water through only the upper layer, which has a lower specific gravity, as a fluidized bed. If head loss increases due to water flow, backwashing can be performed. Due to long-term use.

活性炭の吸着性能が低下した場合は比重差による6一 分別により活性炭を取り出し、夫々に適した再生条件に
て再生ずるのが最も好ましいが、場合によっては混合状
態で行ってもよい。
When the adsorption performance of activated carbon has deteriorated, it is most preferable to take out the activated carbon by fractionation based on the difference in specific gravity and regenerate it under regeneration conditions suitable for each, but depending on the case, it may be carried out in a mixed state.

本発明の方法は飲料用水中の有機化合物(臭気を含む)
の除去、醗酵用水の精製1食品用水の精製、電気部品!
V造造塊洗浄水精製等多分野に利用可能である。
The method of the present invention reduces organic compounds (including odors) in drinking water.
Removal, purification of water for fermentation 1 Purification of water for food use, electrical parts!
It can be used in many fields such as V-shaped agglomeration, washing water purification, etc.

以下、具体例をあげて本発明をさらに詳細に説明する。Hereinafter, the present invention will be explained in more detail by giving specific examples.

実施例I 石炭系活1jL炭(タラレコールG1、C;クラレケミ
カル製、8〜32メソシュ、充填密度o、25g、/m
7りとヤシガラ系活性炭(白鷺Wlh C:武田薬品製
、8〜32メソシュ、充填密度0.45g/ mj! 
) 。
Example I Coal-based activated 1jL charcoal (Tararecol G1, C; manufactured by Kuraray Chemical Co., Ltd., 8 to 32 meshes, packing density o, 25 g, /m
7rito coconut shell activated carbon (Shirasagi Wlh C: Takeda Pharmaceutical Co., Ltd., 8 to 32 meshes, packing density 0.45 g/mj!
).

の各々を管径50 mm、 長さ1mのガラス管に40
0mmづつ2層、計800mmの高さに充填した。この
活性炭充填ガラス管の上部よりクロロホルム100μg
/Jとフミン酸2 mg/ Rを含有する水溶液を線速
度(1,ν) 15m/llr、で通水した。クロロホ
ルム及びフミン酸とも通水初期ではほとんど除去され。
40 each in a glass tube with a tube diameter of 50 mm and a length of 1 m.
Two layers of 0 mm each were filled to a total height of 800 mm. 100μg of chloroform from the top of this glass tube filled with activated carbon.
An aqueous solution containing 2 mg/R of humic acid and 2 mg/R of humic acid was passed through the tube at a linear velocity (1, ν) of 15 m/llr. Both chloroform and humic acid are almost completely removed at the initial stage of water flow.

1力月後でも90%以上、2力月後でも70%以上の除
去率が保持された。
The removal rate was maintained at over 90% after one month and over 70% after two months.

一方、上記活性炭の単独使用では、タラレコールGLC
の場合2力月後にはクロロホルムの除去率は50%以下
に低下し、白鷺wnzcではフミン酸の除去率が50%
以下に低下した。
On the other hand, when the above activated carbon is used alone, Tararecol GLC
In the case of Shirasagi WNZC, the removal rate of chloroform decreased to less than 50% after 2 months, and in Shirasagi WNZC, the removal rate of humic acid was 50%.
It decreased to below.

特許出願人 ユニ亭力株式会社Patent applicant: Uni-Tei Riki Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] +11比重の異なる活性炭を層状に充填して濾床を形成
し、該濾床を縦断して有機化合物を含有する水を通水す
ることを特徴とする水中の有機化合物の除去方法。
A method for removing organic compounds in water, comprising: forming a filter bed by filling layers of activated carbon with different specific gravities, and passing water containing organic compounds vertically through the filter bed.
JP17959983A 1983-09-26 1983-09-26 Removal of organic compound in water Pending JPS6071081A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17959983A JPS6071081A (en) 1983-09-26 1983-09-26 Removal of organic compound in water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17959983A JPS6071081A (en) 1983-09-26 1983-09-26 Removal of organic compound in water

Publications (1)

Publication Number Publication Date
JPS6071081A true JPS6071081A (en) 1985-04-22

Family

ID=16068550

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17959983A Pending JPS6071081A (en) 1983-09-26 1983-09-26 Removal of organic compound in water

Country Status (1)

Country Link
JP (1) JPS6071081A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02229595A (en) * 1989-03-03 1990-09-12 Ebara Infilco Co Ltd Water treatment by biological active carbon
CN106241903A (en) * 2016-08-11 2016-12-21 李宝全 A kind of environmental protection water purification agent

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4846148A (en) * 1971-10-16 1973-07-02
JPS504847A (en) * 1973-05-16 1975-01-18

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4846148A (en) * 1971-10-16 1973-07-02
JPS504847A (en) * 1973-05-16 1975-01-18

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02229595A (en) * 1989-03-03 1990-09-12 Ebara Infilco Co Ltd Water treatment by biological active carbon
JPH0474076B2 (en) * 1989-03-03 1992-11-25
CN106241903A (en) * 2016-08-11 2016-12-21 李宝全 A kind of environmental protection water purification agent

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