JPH11333290A - Adsorption molded body - Google Patents

Adsorption molded body

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Publication number
JPH11333290A
JPH11333290A JP14777698A JP14777698A JPH11333290A JP H11333290 A JPH11333290 A JP H11333290A JP 14777698 A JP14777698 A JP 14777698A JP 14777698 A JP14777698 A JP 14777698A JP H11333290 A JPH11333290 A JP H11333290A
Authority
JP
Japan
Prior art keywords
activated carbon
water
molded article
weight
active carbon
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.)
Withdrawn
Application number
JP14777698A
Other languages
Japanese (ja)
Inventor
Masayuki Imagawa
真之 今川
Yasuhiro Iizuka
康広 飯塚
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.)
Toyobo Co Ltd
Original Assignee
Toyobo Co 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 Toyobo Co Ltd filed Critical Toyobo Co Ltd
Priority to JP14777698A priority Critical patent/JPH11333290A/en
Publication of JPH11333290A publication Critical patent/JPH11333290A/en
Withdrawn legal-status Critical Current

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  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a high water cleaning capacity without deteriorating flow rate for a long period of time while water is made to pass through by constituting active carbons of a fibrous active carbon, a powdery active carbon and a granular active carbon and providing an adsorption molded body with a particular packing density, in the adsorption molded body made by integrally molding the active carbons and a fibril aggregate. SOLUTION: An adsorption molded body is made by integrally molding active carbons and a fibril aggregate and the active carbons comprises a fibrous active carbon, a powdery active carbon and a granular active carbon. The adsorption molded body has a packing density of 0.15-0.30 g/cc and a specific surface area of 850-2000 m<2> /g. The fibrous active carbon has a mean fiber diameter of 5-50 μm and its content is approximately 20-75 wt.%. The granular active carbon has a mean granule diameter of about 150 μm and its content is 2-40 wt.%. The powdery active carbon has a mean particle diameter of about 5-80 μm and its content is about 10-40 wt.%.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、一定の形状に成形
した吸着成形体に関するもので、更に詳しくは、液相、
特に浄水用途に適しており、通水時に長期に渡って流量
の低下を起こさず、遊離残留塩素の分解除去が可能な吸
着成形体に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an adsorption molded article formed into a fixed shape, and more specifically, to a liquid phase,
Particularly, the present invention relates to an adsorption molded article which is suitable for water purification use, does not cause a decrease in flow rate for a long time when water is passed, and is capable of decomposing and removing free residual chlorine.

【0002】[0002]

【従来の技術】吸着成形体の主な用途に飲料水中のカル
キ臭の除去を目的とした浄水器がある。近年、蛇口直結
型浄水器に代表されるように浄水器の小型化が進み、限
られたスペースに充填してなおかつ従来以上の浄水性能
が得られるよう、活性炭の性能の向上が望まれている。
2. Description of the Related Art A main use of an adsorption molded article is a water purifier for removing a odor in drinking water. In recent years, the miniaturization of water purifiers, as typified by faucet direct connection type water purifiers, has been progressing, and the performance of activated carbon has been desired to be improved so that it can be filled in a limited space and still have a higher water purification performance than before. .

【0003】現在、一般にカルキ臭の原因物質である遊
離残留塩素の除去には粒子径が150μmより大きい粒
状活性炭が使用されており、該粒状活性炭はプラスチッ
ク製ケース等の容器に充填して使用されることが多い。
しかし、該粒状活性炭のみでは遊離残留塩素分解除去性
能、いわゆる浄水性能の向上はあまり望めない。
At present, granular activated carbon having a particle diameter of more than 150 μm is generally used for removing free residual chlorine, which is a substance causing the odor of chalky, and the granular activated carbon is used after being filled in a container such as a plastic case. Often.
However, the granular activated carbon alone cannot provide much improvement in the performance of removing and removing free residual chlorine, that is, the so-called water purification performance.

【0004】なぜならば、水中からの遊離残留塩素の分
解除去は活性炭と水との接触効率、即ち活性炭の外表面
積が大きいほど向上するのであるが、粒状活性炭ではそ
の粒子径の大きさから外表面積を大きく取れないため、
遊離残留塩素分解除去性能、いわゆる浄水性能の向上に
は限界があるからである。そのため、粒状活性炭に替わ
るものとして、繊維状活性炭や粉末活性炭が検討されて
いる。
[0004] The reason is that the efficiency of decomposing and removing free residual chlorine from water is improved as the contact efficiency between activated carbon and water, that is, as the outer surface area of activated carbon is increased, but in the case of granular activated carbon, the outer surface area is reduced due to its particle size. Because we can not get large
This is because there is a limit in improving the performance of decomposing and removing free residual chlorine, that is, the so-called water purification performance. For this reason, fibrous activated carbon and powdered activated carbon have been studied as alternatives to granular activated carbon.

【0005】繊維状活性炭は、単位重量あたりの浄水性
能は粒状活性炭に比べ優れている特徴を持つが、通常嵩
密度が粒状活性炭の1/5〜1/10程度であり、単位
体積あたりの浄水性能は、結果的に粒状活性炭程度のも
のしか得られないという問題があった。また、繊維状活
性炭の価格は粒状活性炭や粉末活性炭の約10倍と高価
であった。
[0005] Fibrous activated carbon has a characteristic that the water purification performance per unit weight is superior to that of granular activated carbon. However, the bulk density is usually about 1/5 to 1/10 that of granular activated carbon, and the water purification capacity per unit volume is high. As a result, there was a problem that the performance was only about the same as the granular activated carbon. Moreover, the price of fibrous activated carbon was about ten times as expensive as granular activated carbon or powdered activated carbon.

【0006】粉末状活性炭は、単位重量あたりの浄水性
能は粒状活性炭に比べ優れており、嵩密度が粒状活性炭
より大きく、単位体積当たりの浄水性能は一般的に粒状
活性炭及び繊維状活性炭より高いという特徴を持つ。し
かし、該粉末活性炭のみを一体成形して使用する事は、
吸着成形体の嵩密度が大きいため通水抵抗が大きく流量
が低下する点や、粉塵が発生し操作性が悪い等の問題点
を有する。
[0006] Powdered activated carbon has better water purification performance per unit weight than granular activated carbon, has a higher bulk density than granular activated carbon, and generally has higher water purification performance per unit volume than granular activated carbon and fibrous activated carbon. Has features. However, using only the powdered activated carbon as an integral part
There are problems that the bulk density of the adsorptive molded body is large, the water flow resistance is large, the flow rate is reduced, and dust is generated, resulting in poor operability.

【0007】上記の通り、粒状活性炭、繊維状活性炭、
粉末状活性炭を単独に用いた場合に生じる欠点をカバー
することを目的に、上記を組み合わせた吸着体が開発さ
れている。
As described above, granular activated carbon, fibrous activated carbon,
Adsorbents combining the above have been developed for the purpose of covering the drawbacks caused when powdered activated carbon is used alone.

【0008】例えば、特開平4−271830には、繊
維状活性炭と粒状活性炭を混合した吸着体、特開平8−
24637には、繊維状活性炭と粉末活性炭を混合した
吸着体が開示されている。しかし、前者においては、粒
状活性炭部比を増加させるに従い残留塩素除去効率が低
下し、後者においては、粉末活性炭部比を増加させるに
従い圧力損失が向上し流量が低下するという問題点を有
していた。従って、それぞれの場合、所期の浄水性能及
び流量を得るためには粒状活性炭或いは粉末活性炭の混
合率に、一定の限界を生じていた。
For example, JP-A-4-271830 discloses an adsorbent obtained by mixing fibrous activated carbon and granular activated carbon.
No. 24637 discloses an adsorbent in which fibrous activated carbon and powdered activated carbon are mixed. However, in the former, the residual chlorine removal efficiency decreases as the granular activated carbon part ratio increases, and in the latter, the pressure loss increases and the flow rate decreases as the powdered activated carbon part ratio increases. Was. Therefore, in each case, a certain limit is imposed on the mixing ratio of granular activated carbon or powdered activated carbon in order to obtain the desired water purification performance and flow rate.

【0009】[0009]

【発明が解決しようとする課題】本発明は以上の点を鑑
みて、水中に含まれる遊離残留塩素の分解除去におい
て、通水時に長期に渡って流量の低下を起こさず、かつ
高い浄水性能を持つ吸着体を得ることを目的とするもの
である。
SUMMARY OF THE INVENTION In view of the above points, the present invention provides a method for decomposing and removing free residual chlorine contained in water without causing a decrease in flow rate over a long period of time when passing water and achieving high water purification performance. It is intended to obtain an adsorbent having the same.

【0010】本発明者らは、上記の課題を解決すること
を目的に、種々の形態の活性炭素の組み合わせやフィブ
リル集合体の添加に関して、種々検討した結果、繊維状
活性炭、粒状活性炭、粉末活性炭に一定量のフィブリル
集合体を混合し一定密度となるように一体成形して得ら
れた吸着成形体が優れた残留塩素の分解除去効率の経時
的安定性を有することを見出した。
The present inventors have conducted various studies on the combination of various forms of activated carbon and the addition of fibril aggregates in order to solve the above-mentioned problems. As a result, fibrous activated carbon, granular activated carbon, powdered activated carbon, etc. It has been found that an adsorbent molded body obtained by mixing a certain amount of fibril aggregates and integrally molding to a constant density has excellent temporal stability of decomposition and removal efficiency of residual chlorine.

【0011】また、本発明者らは、上記において、粒状
活性炭の含有量を一定範囲内の量とし、且つ、粒状活性
炭を吸着成形体中に均一に存在させることにより、より
優れた性能を発現し、さらには取り扱い性に優れた成形
体を作成できることを見いだした。
In addition, the inventors of the present invention have demonstrated that, in the above, the content of the granular activated carbon is within a certain range, and that the granular activated carbon is uniformly present in the adsorbent molded article, thereby exhibiting more excellent performance. In addition, it has been found that a molded article excellent in handleability can be produced.

【0012】本発明者らは、上記の知見に基づき、さら
に重ねて検討した結果、本発明を完成したものである。
The present inventors have made further studies based on the above findings, and have completed the present invention.

【0013】[0013]

【課題を解決するための手段】即ち、本発明は、活性炭
及びフィブリル集合体を一体成形してなる吸着成形体で
あって、前記活性炭が繊維状活性炭、粉末状活性炭、粒
状活性炭からなり、且つ、前記吸着成形体の充填密度が
0.15〜0.30g/ccである吸着成形体を提供す
るものである。
That is, the present invention relates to an adsorption molded article obtained by integrally molding activated carbon and a fibril aggregate, wherein the activated carbon comprises fibrous activated carbon, powdered activated carbon, granular activated carbon, and An object of the present invention is to provide an adsorption molded article having a packing density of 0.15 to 0.30 g / cc.

【0014】本発明の吸着成形体の好ましい実施態様
は、前記吸着成形体の比表面積が850〜2000m3
/gである。
[0014] In a preferred embodiment of the adsorption molded article of the present invention, the specific surface area of the adsorption molded article is 850 to 2000 m 3.
/ G.

【0015】本発明の吸着成形体の好ましい実施態様
は、前記繊維状活性炭の繊維径が5〜50μmである。
In a preferred embodiment of the adsorption molded article of the present invention, the fibrous activated carbon has a fiber diameter of 5 to 50 μm.

【0016】本発明の吸着成形体の好ましい実施態様
は、前記粒状活性炭が、前記吸着成形体中に実質的に均
一に分散され、前記吸着成形体に対して4〜40重量%
含有されてなる。
In a preferred embodiment of the adsorptive molded article of the present invention, the granular activated carbon is substantially uniformly dispersed in the adsorptive molded article, and 4 to 40% by weight based on the adsorptive molded article.
Be contained.

【0017】[0017]

【発明の実施の形態】本発明の吸着成形体は、活性炭及
びフィブリル集合体を一体成形してなる吸着成形体であ
り、前記活性炭が繊維状活性炭、粉末活性炭、粒状活性
炭からなることが必要である。上記の一体成形してなる
吸着成形体とは、繊維状活性炭、粒状活性炭、粉末活性
炭がフィブリル集合体により所定の形状に三次元的に組
織化されたものをいう。
BEST MODE FOR CARRYING OUT THE INVENTION The adsorptive molded article of the present invention is an adsorptive molded article obtained by integrally molding activated carbon and fibril aggregates, and it is necessary that the activated carbon comprises fibrous activated carbon, powdered activated carbon, and granular activated carbon. is there. The above-mentioned integrally formed adsorbent molded body refers to one in which fibrous activated carbon, granular activated carbon, and powdered activated carbon are three-dimensionally organized into a predetermined shape by a fibril aggregate.

【0018】かかる成形体は、例えば、繊維状活性炭、
粒状活性炭、粉末活性炭及びフィブリル集合体を水に分
散させて均一なスラリーとして、水が透過することがで
きる小孔を有する所定形状の成形型に該スラリーを吸
引、或いは加圧により流し込んで成形型から水を抜いて
脱水し、脱型、乾燥することにより製造することができ
る。なお、スラリーに凝集剤、添加剤などを適宜添加し
てもよい。
Such a molded article is, for example, a fibrous activated carbon,
Granular activated carbon, powdered activated carbon, and fibril aggregates are dispersed in water to form a uniform slurry, and the slurry is poured into a molding die having a predetermined shape having small holes through which water can pass by suction or pressure to form a molding die. Can be produced by draining water, dehydrating, demolding and drying. Note that a coagulant, an additive, and the like may be appropriately added to the slurry.

【0019】本発明の吸着成形体の充填密度は、0.1
5〜0.30g/ccであることが必要である。より好
ましい範囲としては、下限値として0.16g/ccで
あり、更に好ましくは0.17g/ccである。また、
上限値としてより好ましくは0.28g/ccであり、
更に好ましくは0.27g/ccである。充填密度が
0.15g/cc未満の場合には、成形体の強度が十分
ではなく容器等への装着時に破損する可能性があり、
0.30g/ccを超える場合には、成形体の通水時の
圧力損失が大きくなり、透水量を十分にとれない事にな
る。
The packing density of the adsorption molded article of the present invention is 0.1
It needs to be 5 to 0.30 g / cc. A more preferred range is 0.16 g / cc as a lower limit, and still more preferably 0.17 g / cc. Also,
The upper limit is more preferably 0.28 g / cc,
More preferably, it is 0.27 g / cc. If the packing density is less than 0.15 g / cc, the strength of the molded body is not sufficient, and the molded body may be damaged when mounted on a container or the like.
If it exceeds 0.30 g / cc, the pressure loss during the passage of water through the molded article becomes large, and the water permeability cannot be sufficiently obtained.

【0020】本発明の吸着成形体に用いられるフィブリ
ル集合体の含有量は、1〜40重量%であることが好ま
しい。より好ましい範囲として、下限値としては3重量
部であり、更に好ましくは4重量部である。一方上限値
としてより好ましくは30重量部であり、更に好ましく
は25重量部である。フィブリル集合体は、活性炭同士
をフィブリル集合体により結束させ、成形体が実用的な
強度を有するために必要である。フィブリル集合体が1
重量%未満の場合は、成形体の強度が十分でなく、30
重量%を越える場合は成形体の通水時の圧力損失が大き
くなるため好ましくない。
The content of the fibril aggregate used in the adsorption molded article of the present invention is preferably 1 to 40% by weight. As a more preferred range, the lower limit is 3 parts by weight, and further preferably 4 parts by weight. On the other hand, the upper limit is more preferably 30 parts by weight, and still more preferably 25 parts by weight. The fibril aggregate is necessary for binding the activated carbons with the fibril aggregate and for the molded body to have practical strength. 1 fibril aggregate
If it is less than 30% by weight, the strength of the molded product is not sufficient,
If the amount is more than 10% by weight, the pressure loss at the time of passing water through the molded product is undesirably increased.

【0021】本発明の吸着成形体に用いられるフィブリ
ル集合体は、特に限定されるものではないが、例えば、
木材パルプ、ポリエチレン系、ポリプロピレン系、ポリ
スチレン系、ポリビニルアルコール系などの合成パル
プ、ポリアクリロニトリル繊維やアラミド繊維等を叩解
してフィブリル化したものを単独或いは混合して好適に
用いることができる。なお、上記でフィブリルとは、数
nm〜数μmの太さを有し、枝状に多数分岐した微細な
繊維状組織をいう。
The fibril aggregate used in the adsorption molded article of the present invention is not particularly limited.
Wood pulp, synthetic pulp of polyethylene type, polypropylene type, polystyrene type, polyvinyl alcohol type and the like, and polyacrylonitrile fiber and aramid fiber obtained by beating and fibrillating can be suitably used alone or in combination. In addition, the fibril mentioned above refers to a fine fibrous structure having a thickness of several nm to several μm and branched into many branches.

【0022】本発明の吸着成形体の比表面積は850〜
2000m2/gであることが好ましい。より好ましい範
囲としては下限値は900m2 /g、更に好ましくは9
50m2 /gであり、一方上限値としてより好ましく
は、1900m2 /gである。比表面積が850m2
g未満の場合十分な遊離塩素除去性能が得られず、20
00m2 /gを越える場合は、成形体が高価な物となり
実用的でない。
The specific surface area of the adsorption molded article of the present invention is 850 to
It is preferably 2000 m 2 / g. As a more preferred range, the lower limit is 900 m 2 / g, and further preferably 9 m 2 / g.
It is 50 m 2 / g, while the upper limit is more preferably 1900 m 2 / g. Specific surface area is 850m 2 /
If the amount is less than 20 g, sufficient free chlorine removal performance cannot be obtained,
If it exceeds 00 m 2 / g, the molded article is expensive and not practical.

【0023】なお、上記の比表面積とは、低温窒素吸着
法でBET多点法により分圧0.05〜0.20の範囲
で測定するものである。例えば、高速比表面積・細孔分
布測定装置(島津製作所製ASAP2010)を用いて
測定される。
The specific surface area is measured at a partial pressure of 0.05 to 0.20 by a low temperature nitrogen adsorption method and a BET multipoint method. For example, it is measured using a high-speed specific surface area / pore distribution measuring device (ASAP2010 manufactured by Shimadzu Corporation).

【0024】本発明の吸着成形体に用いられる繊維状活
性炭の平均繊維径は5〜50μmであることが好まし
い。より好ましい範囲としては、下限値は7μm、更に
好ましくは8μm、上限値としてより好ましくは40μ
m、更に好ましくは35μmである。繊維経が5μm未
満の場合、成形体の外観が悪くなったり、通水時の圧力
損失が大きくなるため好ましくなく、50μmを越える
場合は、液と接触する外表面積が小さくなり、残留塩素
除去性能が低下することとなるため好ましくない。また
繊維断面形状としては、特に規定はないが、水との接触
面積を大きくとれる平板状、楕円状、瓢箪状の形状が好
ましい。また、使用する繊維状活性炭の比表面積として
は、残留塩素除去能力を十分に出すために1000m2
/g以上の物を使用する事が好ましい。
The average fiber diameter of the fibrous activated carbon used in the adsorption molded article of the present invention is preferably 5 to 50 μm. As a more preferable range, the lower limit is 7 μm, further preferably 8 μm, and the upper limit is more preferably 40 μm.
m, more preferably 35 μm. If the fiber diameter is less than 5 μm, the appearance of the molded article becomes poor or the pressure loss during water passage becomes large, which is not preferable. If the fiber diameter exceeds 50 μm, the external surface area in contact with the liquid becomes small, and the residual chlorine removal performance is reduced. Is undesirably reduced. The cross-sectional shape of the fiber is not particularly limited, but is preferably a flat plate shape, an elliptical shape, or a gourd-shaped shape capable of providing a large contact area with water. The specific surface area of the fibrous activated carbon used is 1000 m 2 in order to sufficiently remove residual chlorine.
/ G or more is preferably used.

【0025】なお、上記の繊維状活性炭の平均繊維径と
は、成形体の原料の繊維状活性炭をランダムに30本抜
き取り、JIS R7601により測微顕微鏡で測定し
た平均値をいう。
The average fiber diameter of the above-mentioned fibrous activated carbon refers to an average value obtained by randomly extracting 30 fibrous activated carbons as raw materials of a molded product and measuring the same with a microscopic microscope according to JIS R7601.

【0026】本発明の吸着成形体に用いられる繊維状活
性炭の含有率は、20〜75重量%が好ましい。より好
ましい範囲として、下限値としては30重量%、更に好
ましくは35重量%以上が好ましい。また、上限値とし
てより好ましくは72重量%、更に好ましくは70重量
%以下が好ましい。繊維状活性炭の含有率が20重量%
未満の場合、成形体の硬度が高くなり、容器等に装着し
て使用する場合、容器と成形体の間に隙間ができやすく
なり処理水がリークする可能性が高くなり、また、75
重量%を越える場合は、成形体の密度が上げられず活性
炭の量が低下する。
The content of the fibrous activated carbon used in the adsorption molded article of the present invention is preferably 20 to 75% by weight. As a more preferred range, the lower limit is 30% by weight, more preferably 35% by weight or more. The upper limit is more preferably 72% by weight, and even more preferably 70% by weight or less. 20% by weight of fibrous activated carbon
If it is less than 70%, the hardness of the molded body increases, and when used in a container or the like, a gap is easily formed between the container and the molded body, and the possibility that treated water leaks increases.
If the amount exceeds 10% by weight, the density of the compact cannot be increased and the amount of activated carbon decreases.

【0027】本発明の吸着成形体に用いられる繊維状活
性炭の原料は、特に限定されるものではないが、例え
ば、セルロース系、ポリアクリロニトリル系、フェノー
ル樹脂系、ピッチ系等が好適に用いられる。
The raw material of the fibrous activated carbon used in the adsorptive molded article of the present invention is not particularly limited. For example, cellulose-based, polyacrylonitrile-based, phenolic resin-based, pitch-based, etc. are preferably used.

【0028】本発明の吸着成形体に用いられる粒状活性
炭の平均粒子径は150μm以上であることが好まし
い。より好ましくは180μm以上であり、更に好まし
くは200μm以上である。粒状活性炭の平均粒子径が
100μm未満の場合、通液時の圧力損失が大きくなる
ため好ましくない。また、使用する粒状炭の比表面積と
しては残留塩素の除去能力を高めるために800m2
g以上の物を使用する事が好ましい。
The average particle size of the granular activated carbon used in the adsorption molded article of the present invention is preferably 150 μm or more. It is more preferably at least 180 μm, even more preferably at least 200 μm. If the average particle diameter of the granular activated carbon is less than 100 μm, it is not preferable because the pressure loss at the time of liquid passage becomes large. The specific surface area of the granular coal used is 800 m 2 /
It is preferable to use a substance of g or more.

【0029】本発明の吸着成形体に用いられる粒状活性
炭の含有率は、2〜40重量%が好ましい。より好まし
い範囲として、下限値としては3重量%であり、更に好
ましい範囲としては4重量%である。一方上限値として
より好ましい範囲としては37重量%であり、更に好ま
しくは35重量%である。粒状炭の含有率が4重量%未
満の場合は、成形体の充填密度を上げる事が難しくなり
残留塩素処理能力が低下し、40重量部を越える場合
は、成形体の密度が高くなり通液時の圧損が上がり透水
量の低下を招く恐れがある。
The content of the granular activated carbon used in the adsorption molded article of the present invention is preferably 2 to 40% by weight. A more preferable range is 3% by weight as a lower limit, and a further preferable range is 4% by weight. On the other hand, a more preferable range as the upper limit is 37% by weight, and further preferably 35% by weight. When the content of the granular coal is less than 4% by weight, it is difficult to increase the packing density of the molded body, and the residual chlorine treatment capacity is reduced. There is a possibility that the pressure loss at the time increases and the water permeation amount decreases.

【0030】本発明の吸着成形体に用いられる粒状活性
炭の原料は、特に限定されるものではなく、植物系、鉱
物系等のいずれであっても良く、殺菌を目的とした銀添
着等の加工を施してあっても良い。
The raw material of the granular activated carbon used in the adsorptive molded article of the present invention is not particularly limited, and may be any of a plant type, a mineral type, and the like. May be applied.

【0031】本発明の吸着成形体に用いられる粒状活性
炭は、吸着成形体中に実質的に均一に分散されているこ
とが好ましい。粒状炭は、使用する他の活性炭に対し粒
子径が大きいため、不均一に分布する場合には吸着成形
体の実用的な強度が得られなかったり粒状炭の脱落が起
こる可能性があり、また、製造した成形体に密度むらを
生じ、通水時に流路が偏在してリークが発生することが
あるからである。
It is preferable that the granular activated carbon used in the adsorption molded article of the present invention is substantially uniformly dispersed in the adsorption molded article. Granular charcoal has a larger particle size than other activated carbons to be used, so if it is unevenly distributed, practical strength of the adsorptive molded body may not be obtained or granular charcoal may fall off. This is because unevenness in density may occur in the manufactured molded article, and the flow path may be unevenly distributed during water flow, causing a leak.

【0032】なお、上記において、粒状活性炭が実質的
に均一に分散されているとは、例えば、吸着成形体から
約0.5〜1gの範囲で一定重量のサンプルを複数個採
取し、それらのサンプル中の粒状活性炭の含有量を求め
た場合、複数個のサンプル中の粒状炭の含有量の値の分
散が20%以下であることをいう。
In the above description, the expression that the granular activated carbon is substantially uniformly dispersed means, for example, that a plurality of samples having a constant weight in the range of about 0.5 to 1 g are collected from the adsorbent molded body, When the content of the granular activated carbon in the sample is obtained, it means that the dispersion of the value of the content of the granular carbon in a plurality of samples is 20% or less.

【0033】本発明の吸着成形体に用いられる粉末活性
炭の平均粒子径は5〜80μmであることが好ましい。
より好ましい範囲として、下限値にとして10μm、更
に好ましくは12μmである。一方上限値としてより好
ましい範囲としては70μm、更に好ましくは60μm
である。粉末炭の平均粒径が5μm未満の物は、成形体
製造時の取り扱い性が悪く、80μmを越える場合は、
粉末炭の外表面積が小さくなり水との接触面積が低下す
るため、残留塩素除去性能が低下することとなり、粉末
炭を使用するメリットが出にくくなる。また、使用する
粉末活性炭の比表面積は残留塩素処理能力を十分に80
0m2 /g以上が好ましい。
The average particle diameter of the activated carbon powder used in the adsorption molded article of the present invention is preferably 5 to 80 μm.
A more preferred range is 10 μm, more preferably 12 μm, as the lower limit. On the other hand, a more preferable range as the upper limit is 70 μm, and further preferably 60 μm.
It is. If the average particle size of the powdered charcoal is less than 5 μm, the handleability during the production of a molded article is poor. If it exceeds 80 μm,
Since the outer surface area of the powdered coal is reduced and the contact area with water is reduced, the residual chlorine removal performance is reduced, and the merit of using the powdered coal is less likely to be obtained. Also, the specific surface area of the powdered activated carbon to be used should be sufficient for the residual chlorine treatment capacity to be sufficient.
It is preferably 0 m 2 / g or more.

【0034】本発明の吸着成形体に用いられる粉末活性
炭の含有率は、10〜40重量%が好ましい。より好ま
しい範囲として、下限値としては12重量%であり、更
に好ましくは15重量%である。一方上限値としては、
37重量%であり、更に好ましくは35重量部である。
粉末炭の含有率が10重量%未満の場合は、粉末炭を使
用し水との接触面積を上げ残留塩素除去性能を向上させ
る効果が小さくなり、40重量%を超える場合には、成
形体の通水時の圧力損失が大きく透水量が低下すること
となる。
The content of the activated carbon powder used in the adsorption molded article of the present invention is preferably 10 to 40% by weight. As a more preferable range, the lower limit is 12% by weight, and further preferably 15% by weight. On the other hand,
It is 37% by weight, more preferably 35 parts by weight.
When the content of the powdered charcoal is less than 10% by weight, the effect of increasing the contact area with water and improving the residual chlorine removal performance is reduced by using the powdered charcoal. The pressure loss at the time of passing water is large, and the amount of permeated water decreases.

【0035】なお、上記の粒状活性炭及び粉末活性炭の
平均粒子径とは、自然沈降・遠心沈降法による光透過測
定方式により測定した体積基準の累積粒度分布の50%
に相当する粒子径をいい、例えば、自動粒度分布測定装
置(堀場製作所製CAPA−500)を用いて測定され
る。
The average particle size of the granular activated carbon and the powdered activated carbon is defined as 50% of the volume-based cumulative particle size distribution measured by a light transmission measurement method based on a natural sedimentation / centrifugal sedimentation method.
The particle size corresponds to, for example, measured using an automatic particle size distribution analyzer (CAPA-500 manufactured by Horiba, Ltd.).

【0036】本発明の吸着成形体に用いられる粉末活性
炭の原料は、特に限定されるものではなく、植物系、鉱
物系等のいずれであっても良い。
The raw material of the powdered activated carbon used in the adsorptive molded article of the present invention is not particularly limited, and may be any of plant-based, mineral-based, and the like.

【0037】本発明の吸着成形体においては、ポリビニ
ルアルコールなどの接着性のあるバインダーを適宜添加
したり、熱融着性のあるフィブリル集合体を熱融着した
りして、該成形体の強度を増強することもできる。
In the adsorptive molded article of the present invention, the strength of the molded article is obtained by appropriately adding an adhesive binder such as polyvinyl alcohol or by heat-fusing a heat-fusible fibril aggregate. Can also be increased.

【0038】[0038]

【実施例】実施例に基づき本発明を詳述するが、本発明
はこれら実施例に限定されるものではない。
EXAMPLES The present invention will be described in detail based on examples, but the present invention is not limited to these examples.

【0039】(実施例1)平均繊維径18μm、比表面
積1450m2 /gのセルロース系繊維状活性炭68重
量%、平均粒子径250μm、比表面積1750m2
gのヤシ殻系粒状活性炭4重量%、平均粒子径20μ
m、比表面積1150m2 /gのオガ屑系粉末活性炭2
3重量%、フィブリル化アクリル繊維(旭化成製 A−
104)5重量%を水に分散して攪拌し、均一なスラリ
ーを調整し、内径10mmの成形型により吸引、脱水、
脱型、乾燥して外径40mm、高さ25mm、重量6.
2g、充填密度0.21g/cc、比表面積1320m
2 /gの円柱形状の成形体を作製した。
[0039] (Example 1) mean fiber diameter 18 [mu] m, a specific surface area of 1450 m 2 / g cellulosic fibrous activated carbon 68 wt% of an average particle diameter of 250 [mu] m, a specific surface area of 1750m 2 /
g of coconut shell-based granular activated carbon 4% by weight, average particle diameter 20μ
sawdust-based powdered activated carbon 2 with a specific surface area of 1150 m 2 / g
3% by weight, fibrillated acrylic fiber (A-
104) Disperse 5% by weight in water and stir to prepare a uniform slurry.
5. Demold, dry, outer diameter 40 mm, height 25 mm, weight 6.
2g, packing density 0.21g / cc, specific surface area 1320m
A 2 / g cylindrical shaped body was produced.

【0040】該成形体を内径40mmのプラスチック製
ケースに装填し、浄水カートリッジを作製し、市販の家
庭用浄水器に取り付け、該浄水器に水圧2kgf/cm
2 一定で水道水を通水して試験を行い、浄水器の残留塩
素除去効率(原水の残留塩素濃度に対する浄水器出口の
残留塩素濃度より算出)の経時変化及び浄水器出口の水
の流量の経時変化を測定した。試験結果をそれぞれ第1
図、第2図に示す。
The molded body was loaded into a plastic case having an inner diameter of 40 mm to prepare a water purification cartridge, which was attached to a commercially available water purifier, and the water pressure was applied to the water purifier at 2 kgf / cm.
2 Perform a test by passing tap water at a constant rate, and evaluate the residual chlorine removal efficiency of the water purifier (calculated from the residual chlorine concentration at the outlet of the water purifier with respect to the residual chlorine concentration of the raw water) and the flow rate of the water at the water purifier outlet. The change over time was measured. The test results are first
FIG. 2 and FIG.

【0041】(実施例2)平均繊維径18μm、比表面
積1450m2 /gのセルロース系繊維状活性炭47重
量%、平均粒子径250μm、比表面積1750m2
gのヤシ殻系粒状活性炭25重量%、平均粒子径20μ
m、比表面積1150m2 /gのオガ屑系粉末活性炭2
3重量%、フィブリル化アクリル繊維(旭化成製 A−
104)5重量%を水に分散して攪拌し、均一なスラリ
ーを調整し、内径10mmの成形型により吸引、脱水、
脱型、乾燥して外径40mm、高さ25mm、重量6.
7g、充填密度0.23g/cc、比表面積1380m
2 /gの円柱形状の成形体を作製した。
[0041] (Example 2) mean fiber diameter 18 [mu] m, a specific surface area of 1450 m 2 / g cellulosic fibrous activated carbon 47 wt% of an average particle diameter of 250 [mu] m, a specific surface area of 1750M 2 /
g of coconut shell granular activated carbon 25% by weight, average particle diameter 20μ
sawdust-based powdered activated carbon 2 with a specific surface area of 1150 m 2 / g
3% by weight, fibrillated acrylic fiber (A-
104) Disperse 5% by weight in water and stir to prepare a uniform slurry.
5. Demold, dry, outer diameter 40 mm, height 25 mm, weight 6.
7g, packing density 0.23g / cc, specific surface area 1380m
A 2 / g cylindrical shaped body was produced.

【0042】該成形体から実施例1と同様に浄水カート
リッジを作製し、実施例1と同様の試験を行った。浄水
器の残留塩素除去効率(原水の残留塩素濃度に対する浄
水器出口の残留塩素濃度より算出)の経時変化及び浄水
器出口の水の流量の経時変化を測定した。試験結果をそ
れぞれ第1図、第2図に示す。
A water purification cartridge was prepared from the molded body in the same manner as in Example 1, and the same test as in Example 1 was performed. The change with time of the residual chlorine removal efficiency of the water purifier (calculated from the residual chlorine concentration at the outlet of the water purifier with respect to the residual chlorine concentration of the raw water) and the change with time of the flow rate of the water at the outlet of the water purifier were measured. The test results are shown in FIGS. 1 and 2, respectively.

【0043】(実施例3)平均繊維径18μm、比表面
積1450m2 /gのセルロース系繊維状活性炭36重
量%、平均粒子径250μm、比表面積1750m2
gのヤシ殻系粒状活性炭26重量%、平均粒子径20μ
m、比表面積1150m2 /gのオガ屑系粉末活性炭3
4重量%、フィブリル化アクリル繊維(旭化成製 A−
104)4重量%を水に分散して攪拌し、均一なスラリ
ーを調整し、内径10mmの成形型により吸引、脱水、
脱型、乾燥して外径40mm、高さ25mm、重量7.
8g、充填密度0.26g/cc、比表面積1390m
2 /gの円柱形状の成形体を作製した。
[0043] (Example 3) Average fiber diameter 18 [mu] m, a specific surface area of 1450 m 2 / g cellulosic fibrous activated carbon 36 wt% of an average particle diameter of 250 [mu] m, a specific surface area of 1750m 2 /
g of coconut shell type granular activated carbon 26% by weight, average particle diameter 20μ
sawdust activated carbon 3 having a specific surface area of 1150 m 2 / g
4% by weight, fibrillated acrylic fiber (A-Asei Kasei A-
104) Disperse 4% by weight in water and stir to prepare a uniform slurry.
Demold, dry, outer diameter 40 mm, height 25 mm, weight 7.
8g, packing density 0.26g / cc, specific surface area 1390m
A 2 / g cylindrical shaped body was produced.

【0044】該成形体から実施例1と同様に浄水カート
リッジを作製し、実施例1と同様の試験を行った。浄水
器の残留塩素除去効率(原水の残留塩素濃度に対する浄
水器出口の残留塩素濃度より算出)の経時変化及び浄水
器出口の水の流量の経時変化を測定した。試験結果をそ
れぞれ第1図、第2図に示す。
A water purification cartridge was prepared from the molded body in the same manner as in Example 1, and the same test as in Example 1 was performed. The change with time of the residual chlorine removal efficiency of the water purifier (calculated from the residual chlorine concentration at the outlet of the water purifier with respect to the residual chlorine concentration of the raw water) and the change with time of the flow rate of the water at the outlet of the water purifier were measured. The test results are shown in FIGS. 1 and 2, respectively.

【0045】(比較例1)平均繊維径18μm、比表面
積1450m2 /gの繊維状活性炭95重量%、フィブ
リル化アクリル繊維(旭化成製 A−104)5重量%
を水に分散して攪拌し、均一なスラリーを調整し、内径
10mmの成形型により吸引、脱水、脱型、乾燥して外
径40mm、高さ25mm、重量5.3g、充填密度
0.18g/cc、比表面積1370m2 /gの円柱形
状の成形体を作製した。
Comparative Example 1 95% by weight of fibrous activated carbon having an average fiber diameter of 18 μm and a specific surface area of 1450 m 2 / g, 5% by weight of fibrillated acrylic fiber (A-104 manufactured by Asahi Kasei)
Is dispersed in water and stirred to prepare a uniform slurry. The slurry is suctioned, dehydrated, demolded and dried by a molding die having an inner diameter of 10 mm, and is dried to obtain an outer diameter of 40 mm, a height of 25 mm, a weight of 5.3 g, and a packing density of 0.18 g. / Cc and a cylindrical shaped body having a specific surface area of 1370 m 2 / g were produced.

【0046】該成形体から実施例1と同様に浄水カート
リッジを作製し、実施例1と同様の試験を行った。浄水
器の残留塩素除去効率(原水の残留塩素濃度に対する浄
水器出口の残留塩素濃度より算出)の経時変化及び浄水
器出口の水の流量の経時変化を測定した。試験結果をそ
れぞれ第1図、第2図に示す。
A water purification cartridge was prepared from the molded body in the same manner as in Example 1, and the same test as in Example 1 was performed. The change with time of the residual chlorine removal efficiency of the water purifier (calculated from the residual chlorine concentration at the outlet of the water purifier with respect to the residual chlorine concentration of the raw water) and the change with time of the flow rate of the water at the outlet of the water purifier were measured. The test results are shown in FIGS. 1 and 2, respectively.

【0047】比較例1は繊維状活性炭とフィブリル集合
体であるフィブリル化アクリル繊維のみで構成された成
形体であり、通水時の残留塩素除去効率は低い。
Comparative Example 1 is a molded article composed only of fibrous activated carbon and fibrillated acrylic fiber which is an aggregate of fibrils, and has a low efficiency of removing residual chlorine when passing water.

【0048】(比較例2)平均繊維径18μm、比表面
積1450m2 /gのセルロース系繊維状活性炭53重
量%、平均粒子径250μm、比表面積1750m2
gのヤシ殻系粒状活性炭42重量%、フィブリル化アク
リル繊維(旭化成製 A−104)5重量%を水に分散
して攪拌し、均一なスラリーを調整し、内径10mmの
成形型により吸引、脱水、脱型、乾燥して外径40m
m、高さ25mm、重量6.8g、充填密度0.23g
/cc、比表面積1500m2 /gの円柱形状の成形体
を作製した。
[0048] (Comparative Example 2) Average fiber diameter 18 [mu] m, a specific surface area of 1450 m 2 / g cellulosic fibrous activated carbon 53 wt% of an average particle diameter of 250 [mu] m, a specific surface area of 1750M 2 /
g of coconut shell-based granular activated carbon (42% by weight) and fibrillated acrylic fiber (A-104 manufactured by Asahi Kasei Corporation) (5% by weight) are dispersed in water and stirred to prepare a uniform slurry. Demold, dry, outer diameter 40m
m, height 25mm, weight 6.8g, packing density 0.23g
/ Cc and a cylindrical shaped body having a specific surface area of 1500 m 2 / g.

【0049】該成形体から実施例1と同様に浄水カート
リッジを作製し、実施例1と同様の試験を行った。浄水
器の残留塩素除去効率(原水の残留塩素濃度に対する浄
水器出口の残留塩素濃度より算出)の経時変化及び浄水
器出口の水の流量の経時変化を測定した。試験結果をそ
れぞれ第1図、第2図に示す。
A water purification cartridge was prepared from the molded body in the same manner as in Example 1, and the same test as in Example 1 was performed. The change with time of the residual chlorine removal efficiency of the water purifier (calculated from the residual chlorine concentration at the outlet of the water purifier with respect to the residual chlorine concentration of the raw water) and the change with time of the flow rate of the water at the outlet of the water purifier were measured. The test results are shown in FIGS. 1 and 2, respectively.

【0050】比較例2は粉末活性炭を含まず繊維状活性
炭と粒状活性炭及びフィブリル集合体であるフィブリル
化アクリル繊維のみで構成された成形体であり、通水時
の残留塩素除去効率が低い。
Comparative Example 2 is a molded article which does not contain powdered activated carbon and is composed only of fibrous activated carbon, granular activated carbon, and fibrillated acrylic fiber which is an aggregate of fibrils, and has a low efficiency of removing residual chlorine when passing water.

【0051】(比較例3)平均繊維径18μm、比表面
積1450m2 /gのセルロース系繊維状活性炭21重
量%、平均粒子径250μm、比表面積1750m2
gのヤシ殻系粒状活性炭34重量%、平均粒子径20μ
m、比表面積1150m2 /gのオガ屑系粉末活性炭3
5重量%、フィブリル化アクリル繊維(旭化成製 A−
104)重量10%を水に分散して攪拌し、均一なスラ
リーを調整し、内径10mmの成形型により吸引、脱
水、脱型、乾燥して外径40mm、高さ25mm、重量
9.8g、充填密度0.33g/cc、比表面積130
0g/ccの円柱形状の成形体を作製した。
[0051] (Comparative Example 3) an average fiber diameter of 18 [mu] m, a specific surface area of 1450 m 2 / g cellulosic fibrous activated carbon 21 wt% of an average particle diameter of 250 [mu] m, a specific surface area of 1750m 2 /
g of coconut shell-based granular activated carbon (34% by weight), average particle size 20μ
sawdust activated carbon 3 having a specific surface area of 1150 m 2 / g
5% by weight, fibrillated acrylic fiber (A-Asei Kasei A-
104) Disperse 10% by weight in water and stir to prepare a uniform slurry, suction, dehydrate, demold, and dry with a mold having an inner diameter of 10 mm to obtain an outer diameter of 40 mm, a height of 25 mm, a weight of 9.8 g, Packing density 0.33 g / cc, specific surface area 130
A cylindrical shaped body of 0 g / cc was produced.

【0052】該成形体から実施例1と同様に浄水カート
リッジを作製し、実施例1と同様の試験を行ったが、初
期から所定の流量を得る事が出来ず、残留塩素除去性能
試験については実施しなかった。通水時の流量について
の試験結果を第2図に示す。
A water purification cartridge was prepared from the molded body in the same manner as in Example 1, and the same test as in Example 1 was performed. However, a predetermined flow rate could not be obtained from the initial stage. Not implemented. FIG. 2 shows the test results for the flow rate during the passage of water.

【0053】前述の通り、比較例に対し実施例はいずれ
も浄水性能は優れており、かつ通水時に長期に渡って流
量の低下を起こさなかった。
As described above, the water purification performance of each of the examples was superior to that of the comparative example, and the flow rate did not decrease for a long time during the passage of water.

【0054】[0054]

【発明の効果】以上説明した通り、本発明の吸着成形体
は、浄水器等に適用する際し、成形体の密度が高いゆえ
に取り扱い性に優れ、また、高寿命、低圧量損失なが
ら、吸着容量が高く、例えば、水中の遊離残留塩素の分
解除去において、通水時に長期に渡って流量の低下を起
こさずに、遊離残留塩素を分解除去することが可能であ
り、本発明の効果は大である。
As described above, when applied to a water purifier, the adsorption molded article of the present invention is excellent in handleability due to the high density of the molded article. The capacity is high and, for example, in the removal and removal of free residual chlorine in water, free residual chlorine can be decomposed and removed without causing a decrease in the flow rate over a long period of time when passing water, and the effect of the present invention is large. It is.

【図面の簡単な説明】[Brief description of the drawings]

【図1】 通水時(3L/min)の残留塩素除去効率
の経時変化
FIG. 1 Changes with time of residual chlorine removal efficiency when passing water (3 L / min)

【図2】 通水時(2kgf/cm2 )の流量の経時変
Fig. 2 Time-dependent change of flow rate when passing water (2 kgf / cm 2 )

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 活性炭及びフィブリル集合体を一体成形
してなる吸着成形体であって、前記活性炭が繊維状活性
炭、粉末状活性炭、粒状活性炭からなり、且つ、前記吸
着成形体の充填密度が0.15〜0.30g/ccであ
ることを特徴とする吸着成形体。
1. An adsorption molded article obtained by integrally molding activated carbon and a fibril aggregate, wherein said activated carbon is made of fibrous activated carbon, powdered activated carbon, or granular activated carbon, and said adsorption molded article has a packing density of 0%. An adsorption molded article having a weight of 15 to 0.30 g / cc.
【請求項2】 前記吸着成形体の比表面積が850〜2
000m2 /gであることを特徴とする請求項1に記載
の吸着成形体。
2. The specific surface area of the adsorption molded article is 850 to 2
The adsorption molded article according to claim 1, wherein the molded article is 000 m 2 / g.
【請求項3】 前記繊維状活性炭の繊維径が5〜50μ
mであることを特徴とする請求項1又は2に記載の吸着
成形体。
3. The fibrous activated carbon has a fiber diameter of 5 to 50 μm.
3. The adsorption molded article according to claim 1, wherein m is m.
【請求項4】 前記粒状活性炭が、前記吸着成形体中に
実質的に均一に分散され、前記吸着成形体に対して2〜
40重量%含有されてなることを特徴とする請求項1乃
至3に記載の吸着成形体。
4. The method according to claim 1, wherein the granular activated carbon is substantially uniformly dispersed in the adsorption molded body,
The adsorption molded article according to any one of claims 1 to 3, comprising 40% by weight.
JP14777698A 1998-05-28 1998-05-28 Adsorption molded body Withdrawn JPH11333290A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14777698A JPH11333290A (en) 1998-05-28 1998-05-28 Adsorption molded body

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14777698A JPH11333290A (en) 1998-05-28 1998-05-28 Adsorption molded body

Publications (1)

Publication Number Publication Date
JPH11333290A true JPH11333290A (en) 1999-12-07

Family

ID=15437935

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14777698A Withdrawn JPH11333290A (en) 1998-05-28 1998-05-28 Adsorption molded body

Country Status (1)

Country Link
JP (1) JPH11333290A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013014457A (en) * 2011-07-01 2013-01-24 Yamaha Livingtec Corp Method for manufacturing granulated activated carbon and granulated activated carbon
JP2016022399A (en) * 2014-07-16 2016-02-08 フタムラ化学株式会社 Water purification filter body
WO2017138477A1 (en) * 2016-02-08 2017-08-17 ベーシック株式会社 Water purification filter
JP2017529230A (en) * 2014-08-15 2017-10-05 ハロソース, インコーポレイテッド Granular filter media mixture and use in water purification

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013014457A (en) * 2011-07-01 2013-01-24 Yamaha Livingtec Corp Method for manufacturing granulated activated carbon and granulated activated carbon
JP2016022399A (en) * 2014-07-16 2016-02-08 フタムラ化学株式会社 Water purification filter body
JP2017529230A (en) * 2014-08-15 2017-10-05 ハロソース, インコーポレイテッド Granular filter media mixture and use in water purification
US10668416B2 (en) 2014-08-15 2020-06-02 Strix (Usa), Inc. Granular filtration media mixture and uses in water purification
WO2017138477A1 (en) * 2016-02-08 2017-08-17 ベーシック株式会社 Water purification filter
JPWO2017138477A1 (en) * 2016-02-08 2018-12-13 ベーシック株式会社 Water purification filter

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