JP2003190941A - Adsorbent for water cleaner, method for manufacturing the same and water cleaner using the adsorbent - Google Patents

Adsorbent for water cleaner, method for manufacturing the same and water cleaner using the adsorbent

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Publication number
JP2003190941A
JP2003190941A JP2001391910A JP2001391910A JP2003190941A JP 2003190941 A JP2003190941 A JP 2003190941A JP 2001391910 A JP2001391910 A JP 2001391910A JP 2001391910 A JP2001391910 A JP 2001391910A JP 2003190941 A JP2003190941 A JP 2003190941A
Authority
JP
Japan
Prior art keywords
adsorbent
water purifier
water
lead
water cleaner
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
JP2001391910A
Other languages
Japanese (ja)
Inventor
Takashi Tachikawa
敬史 立川
Naoya Kanno
直也 官野
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.)
Mitsubishi Rayon Co Ltd
Original Assignee
Mitsubishi Rayon 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 Mitsubishi Rayon Co Ltd filed Critical Mitsubishi Rayon Co Ltd
Priority to JP2001391910A priority Critical patent/JP2003190941A/en
Publication of JP2003190941A publication Critical patent/JP2003190941A/en
Pending legal-status Critical Current

Links

Abstract

<P>PROBLEM TO BE SOLVED: To provide an adsorbent for a water cleaner excellent in the adsorpability of heavy metals, especially lead, to provide a method for manufacturing the same and the water cleaner using the adsorbent. <P>SOLUTION: Since the adsorbent with a lead adsorption quantity of 200 mg/g or more and a compression strength of above 1.0 N/mm<SP>2</SP>develops high lead removing capacity at the time of passage of water and not collapsed during the passage of water, it is preferable as the adsorbent for the water cleaner. The adsorbent for the water cleaner excellent in lead removing capacity and strength can be obtained by heating a powder of a synthetic calcium phosphate compound to 200-500°C to solidify the same. The water cleaner using this adsorbent can develop excellent heavy metal removing capacity over a long period of time. <P>COPYRIGHT: (C)2003,JPO

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、安全性やおいしさ
を損なう原因となる重金属類、特に鉛を除去できる浄水
器用吸着材及びその製造方法と、これを用いた浄水器に
関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an adsorbent for a water purifier capable of removing heavy metals, particularly lead, which impairs safety and taste, a method for producing the same, and a water purifier using the same.

【0002】[0002]

【従来の技術】水道水中に含まれる残留塩素、トリハロ
メタンなどを除去するために活性炭を使用した浄水器が
ある。この種の浄水器は、長時間使用しなかった場合、
活性炭中に雑菌が発生し、好ましくない。そこで、活性
炭中に発生した雑菌の流出を防ぐために多孔質膜などの
膜濾過を利用した浄水器が開発され、最近ではこのタイ
プが主流となっている。
2. Description of the Related Art There is a water purifier that uses activated carbon to remove residual chlorine, trihalomethane, etc. contained in tap water. If you don't use this type of water purifier for a long time,
It is not preferable because various bacteria are generated in the activated carbon. Therefore, a water purifier using membrane filtration such as a porous membrane has been developed to prevent outflow of various bacteria generated in activated carbon, and this type has recently become the mainstream.

【0003】一方、地中、配水管などから溶出し、井戸
水、水道水中にイオンの形態として含まれている可能性
があるものとして、有害物質である鉛や、鉄、銅、ニッ
ケル、亜鉛、クロム、カドミウムなどの重金属類があ
り、これらを除去する方法については様々な検討がなさ
れている。
On the other hand, as a substance which may be eluted from the ground or a water distribution pipe and contained in well water or tap water in the form of ions, harmful substances such as lead, iron, copper, nickel and zinc, There are heavy metals such as chromium and cadmium, and various studies have been made on methods for removing them.

【0004】[0004]

【発明が解決しようとする課題】重金属類の中で、特に
鉛の吸着性能に優れた吸着剤として、ヒドロキシアパタ
イトが知られている。ヒドロキシアパタイトは粒子径が
小さいほうが重金属イオン吸着性能は高いものの、脆い
ために通水により微粉末が発生して吸着材の移動抑制部
材等を閉塞させて通水圧力を上昇させる可能性があっ
た。
Among the heavy metals, hydroxyapatite is known as an adsorbent having a particularly excellent lead adsorption performance. Although hydroxyapatite has a higher heavy metal ion adsorption performance when the particle size is smaller, because it is brittle, it is possible that fine powder may be generated due to water flow and block the adsorbent movement suppression member etc. to increase water flow pressure. .

【0005】特開2001−47038には、結合剤を
用いてヒドロキシアパタイトを繊維状活性炭とともに成
型し、微粉の流出を防止する方法が記載されている。し
かしながら結合剤を用いた場合、活性炭やヒドロキシア
パタイトの表面が結合剤で覆われるために、残留塩素や
重金属イオンの除去性能が低下するという問題点があっ
た。
Japanese Patent Laid-Open No. 2001-47038 describes a method of forming hydroxyapatite together with fibrous activated carbon using a binder to prevent the outflow of fine powder. However, when a binder is used, the surface of activated carbon or hydroxyapatite is covered with the binder, so that there is a problem that the removal performance of residual chlorine and heavy metal ions deteriorates.

【0006】本発明者らは、かかる状況に鑑み、上記の
問題点を解決し、重金属類、特に鉛を含まず、長期的に
安全でおいしい水を得ることのできる浄水器用吸着材に
つき鋭意検討を重ねた結果、本発明を完成させた。
In view of the above situation, the present inventors have diligently studied an adsorbent for a water purifier which solves the above-mentioned problems and does not contain heavy metals, especially lead, and which can obtain safe and delicious water in the long term. As a result of repeating, the present invention was completed.

【0007】[0007]

【課題を解決するための手段】即ち、本発明の第一の要
旨は、鉛の吸着量が200mg/g以上かつ圧縮強度が
1.0N/mmよりも大きい浄水器用吸着材である。
That is, the first gist of the present invention is an adsorbent for a water purifier having an adsorbed amount of lead of 200 mg / g or more and a compressive strength of more than 1.0 N / mm 2 .

【0008】前記浄水器用吸着材の平均粒径は20〜7
50μmであると、吸着性能が優れると共に通水が容易
となり好ましい。また、前記浄水器用吸着材がリン酸カ
ルシウム系化合物からなると、吸着性能が優れるため好
ましい。さらに、前記リン酸カルシウム系化合物が、ヒ
ドロキシアパタイト、リン酸三カルシウム、リン酸四カ
ルシウムから選ばれる少なくとも1種類以上であると、
それぞれ吸着性能に優れるためより好ましい。
The average particle size of the adsorbent for water purifier is 20 to 7
When it is 50 μm, the adsorption performance is excellent and water is easily passed, which is preferable. Further, it is preferable that the adsorbent for a water purifier is made of a calcium phosphate-based compound, because the adsorption performance is excellent. Furthermore, the calcium phosphate-based compound is at least one selected from hydroxyapatite, tricalcium phosphate, and tetracalcium phosphate,
It is more preferable because each has excellent adsorption performance.

【0009】本発明の第二の要旨は、合成リン酸カルシ
ウム系化合物の粉末を200℃〜500℃で加熱固化す
る浄水器用吸着材の製造方法である。
The second aspect of the present invention is a method for producing an adsorbent for a water purifier, which comprises heating and solidifying a powder of a synthetic calcium phosphate compound at 200 to 500 ° C.

【0010】また、合成リン酸カルシウム系化合物の粉
末と水の混合スラリーを乾燥した後、200℃〜500
℃で加熱固化すると、収率が向上するため好ましい。こ
の際乾燥温度は80〜150℃が好ましい。前記合成リ
ン酸カルシウム系化合物は、ヒドロキシアパタイト、リ
ン酸三カルシウム、リン酸四カルシウムから選ばれる少
なくとも1種類以上であると、それぞれ吸着性能に優れ
るため好ましい。
Further, after drying the mixed slurry of the synthetic calcium phosphate compound powder and water, the mixture is heated to 200 ° C. to 500 ° C.
It is preferable to heat and solidify at ℃ because the yield is improved. At this time, the drying temperature is preferably 80 to 150 ° C. The synthetic calcium phosphate-based compound is preferably at least one selected from hydroxyapatite, tricalcium phosphate, and tetracalcium phosphate because each has excellent adsorption performance.

【0011】本発明の第三の要旨は、前述の浄水器用吸
着材を用いた浄水器である。
The third gist of the present invention is a water purifier using the adsorbent for a water purifier described above.

【0012】[0012]

【発明の実施の形態】以下、本発明を詳しく説明する。
本発明の浄水器用吸着材は、鉛の吸着量が200mg/
g以上かつ圧縮強度が1.0N/mmよりも大きいの
ものを使用する。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention is described in detail below.
The adsorbent for water purifiers of the present invention has a lead adsorption amount of 200 mg /
A material having a compression strength of g or more and a compression strength of more than 1.0 N / mm 2 is used.

【0013】ここで、鉛の吸着量(mg/g)とは、鉛
を含む水溶液に、浄水器用吸着剤を24時間浸漬させた
際に、浄水器用吸着剤が1gあたり吸着する鉛の量をい
う。具体的には、例えば硝酸鉛水溶液を鉛濃度200m
g/Lとなるように調製して三角フラスコに200ml
分取し、浄水器用吸着材50mgを添加し、振とうさせ
た後、24時間後にフィルターで濾過し、濾液水中の残
留鉛濃度を測定することによって鉛吸着量を求めること
ができる。
Here, the amount of lead adsorbed (mg / g) means the amount of lead adsorbed by 1 g of the adsorbent for water purifier when the adsorbent for water purifier is immersed in an aqueous solution containing lead for 24 hours. Say. Specifically, for example, a lead nitrate aqueous solution is used to obtain a lead concentration of 200 m.
200 ml in Erlenmeyer flask prepared to be g / L
The amount of adsorbed lead can be determined by collecting 50 mg of the adsorbent for a water purifier, shaking the mixture, and filtering after 24 hours with a filter, and measuring the residual lead concentration in the filtrate water.

【0014】また、圧縮強度(N/mm)とは、平
松、岡、木山:日本鉱業会誌、81、10、24(19
65)の方法を参考に、浄水器用吸着剤を平板で圧縮す
る際に、浄水器用吸着剤にかかる加重から求めるもので
あり、圧縮強度;St(N/mm)、P;荷重
(N)、d;粒子径(mm)としたとき、St=2.8
P/πdの式から算出する。
The compressive strength (N / mm 2 ) means Hiramatsu, Oka, Kiyama: Journal of the Japan Mining Industry Association, 81, 10, 24 (19).
It is obtained from the weight applied to the adsorbent for a water purifier when the adsorbent for a water purifier is compressed with a flat plate by referring to the method of 65), and the compressive strength: St (N / mm 2 ), P; load (N) , D; St = 2.8 when the particle diameter (mm) is used.
It is calculated from the equation P / πd 2 .

【0015】浄水器は通常、水道圧力による通水量とし
て1〜5L/分程度の流量が要求される。このような流
量で水を流すにあたって、鉛の吸着量が200mg/g
よりも小さいと、充分に鉛除去を行うことが困難とな
る。鉛の吸着量は、220mg/g以上がより好まし
く、250mg/g以上が更に好ましい。
A water purifier is usually required to have a flow rate of about 1 to 5 L / min as a water flow rate by water pressure. When flowing water at such a flow rate, the lead adsorption amount is 200 mg / g
If it is smaller than this, it becomes difficult to sufficiently remove lead. The lead adsorption amount is more preferably 220 mg / g or more, still more preferably 250 mg / g or more.

【0016】また、浄水器に通水するにあたり、浄水器
用吸着剤が経時的に崩れてしまうのを防ぐためには、
1.0N/mmよりも大きい圧縮強度が必要である。
圧縮強度は、1.3N/mm以上がより好ましく、
1.5N/mm以上が更に好ましい。
Further, in order to prevent the adsorbent for a water purifier from collapsing with time when passing water through the water purifier,
A compressive strength of greater than 1.0 N / mm 2 is required.
The compressive strength is more preferably 1.3 N / mm 2 or more,
It is more preferably 1.5 N / mm 2 or more.

【0017】浄水器用吸着剤の大きさは、平均粒径20
〜750μmの顆粒状が好ましく、150〜500μm
がより好ましい。粒径が20μmより小さいと濾過抵抗
が上昇し通水性が悪くなる。一方、750μmより大き
い場合、粒子間の空隙が大きくなり、除去性能は低くな
る傾向が見られる。
The size of the adsorbent for the water purifier has an average particle size of 20.
~ 750 μm granular form is preferred, 150-500 μm
Is more preferable. When the particle size is smaller than 20 μm, filtration resistance increases and water permeability deteriorates. On the other hand, when it is larger than 750 μm, the voids between particles become large, and the removal performance tends to be low.

【0018】鉛の吸着量が200mg/g以上かつ圧縮
強度が1.0N/mmよりも大きい浄水器用吸着剤を
得るためには、リン酸カルシウム系化合物を使用するこ
とが好ましく、合成リン酸カルシウム系化合物の粉末を
200℃〜500℃で加熱固化することによって、強度
及び鉛吸着性能を共に満足する浄水器用吸着剤を得る事
ができる。
In order to obtain an adsorbent for a water purifier having a lead adsorption amount of 200 mg / g or more and a compressive strength of more than 1.0 N / mm 2, it is preferable to use a calcium phosphate compound, which is a synthetic calcium phosphate compound. By heating and solidifying the powder at 200 ° C. to 500 ° C., an adsorbent for a water purifier that satisfies both strength and lead adsorption performance can be obtained.

【0019】合成リン酸カルシウム系化合物の加熱固化
温度は、200℃よりも低いと、固化が不十分となっ
て、浄水器に通水を行った際に崩れ、微粉が発生する。
一方、加熱固化温度が500℃よりも高いと、得られる
粒子の強度は強くなるものの、吸着剤の高密度化が起こ
り、比表面積が低下するために吸着性能が低下する。加
熱時間は30分〜5時間行えばよく、1時間〜2時間が
より好ましい。
When the heating and solidifying temperature of the synthetic calcium phosphate-based compound is lower than 200 ° C., the solidification becomes insufficient and the water is broken when water is passed through the water purifier to generate fine powder.
On the other hand, when the heating and solidifying temperature is higher than 500 ° C., the strength of the obtained particles becomes strong, but the density of the adsorbent increases, and the specific surface area decreases, so that the adsorption performance decreases. The heating time may be 30 minutes to 5 hours, more preferably 1 hour to 2 hours.

【0020】浄水器用吸着剤の比表面積は、50m2
g以上とすることが好ましく、60m/g以上とする
ことがより好ましい。
The specific surface area of the adsorbent for the water purifier is 50 m 2 /
It is preferably at least g, and more preferably at least 60 m 2 / g.

【0021】合成リン酸カルシウム系化合物は、ヒドロ
キシアパタイト、リン酸三カルシウム、リン酸四カルシ
ウムのうち、少なくとも1種類以上であることが好まし
く、中でもヒドロキシアパタイトが吸着性能に優れるた
め最も好ましい。合成リン酸カルシウム系化合物は、リ
ン酸塩水溶液とカルシウム塩水溶液を反応させることに
より合成することが出来る。特にヒドロキシアパタイト
は、市販でスラリー状として入手することも出来る。
The synthetic calcium phosphate-based compound is preferably at least one kind of hydroxyapatite, tricalcium phosphate and tetracalcium phosphate. Among them, hydroxyapatite is most preferable because of its excellent adsorption performance. The synthetic calcium phosphate-based compound can be synthesized by reacting a phosphate aqueous solution with a calcium salt aqueous solution. In particular, hydroxyapatite can be obtained as a slurry on the market.

【0022】浄水器用吸着剤の粒径は、前述したように
平均粒径として20μm〜750μmが好ましいが、こ
の範囲に調整するためには、篩い分けを行えばよい。こ
こで、合成リン酸カルシウム系化合物と水の混合スラリ
ーを用いる場合、混合スラリーを直接加熱固化させても
良いが、加熱固化を行う前に、80℃〜150℃程度の
温度で乾燥を行った後、篩い分けを行って粒径を調整
し、その後で加熱固化を行うことにより、粒径が外れた
ものを再度スラリー化することが可能となるため、収率
を向上させることができる。乾燥温度は100℃〜13
0℃が好ましく、110℃程度が最も好ましい。
The particle size of the adsorbent for a water purifier is preferably 20 μm to 750 μm as an average particle size as described above, but sieving may be performed to adjust to this range. Here, in the case of using a mixed slurry of the synthetic calcium phosphate compound and water, the mixed slurry may be directly heated and solidified, but before being heated and solidified, after drying at a temperature of about 80 ° C to 150 ° C, By sieving to adjust the particle size and then heating and solidifying, it is possible to re-slurry the particles having a deviated particle size, so that the yield can be improved. Drying temperature is 100 ° C-13
0 degreeC is preferable and about 110 degreeC is the most preferable.

【0023】前述した本発明の浄水器用吸着材を用いた
浄水器は、重金属類を効率的に除去することができる。
また、残留塩素、トリハロメタンなどを効率よく除去す
るためには、本発明の浄水器用吸着材に加えて活性炭を
用いるのが好ましい。活性炭は、除去能力は低いもの
の、重金属類も吸着し、吸着材の吸着性能の長寿命化に
寄与するため、活性炭と併用することがより好ましい。
The water purifier using the water purifier adsorbent of the present invention described above can efficiently remove heavy metals.
Further, in order to efficiently remove residual chlorine, trihalomethane, etc., it is preferable to use activated carbon in addition to the adsorbent for a water purifier of the present invention. Although activated carbon has a low removal ability, it also adsorbs heavy metals and contributes to prolonging the adsorption performance of the adsorbent, so it is more preferably used in combination with activated carbon.

【0024】活性炭としては、残留塩素、トリハロメタ
ンなどの除去する目的に合致する性能を有しているもの
であれば特に限定されず、その形状は粉末状、繊維状、
或いは粒状のものなどを用いることが出来る。また、活
性炭の種類は必ずしも限定はされず、ヤシ殻活性炭、骨
炭、木炭等天然系活性炭、ピッチ系、石油コークス系、
樹脂やゴム等の焼成賦活物或いは化学的賦活物等を用い
ることが出来るが、除去すべき物質はトリハロメタンな
ど比較的分子量の小さなものが多く、経済性をも含めて
考慮すると、水蒸気賦活ヤシガラ活性炭が実用的に最も
好適に使用される。さらに、抗菌性を付与するために、
銀等を添着しても構わない。
The activated carbon is not particularly limited as long as it has a performance meeting the purpose of removing residual chlorine, trihalomethane, etc., and its shape is powdery, fibrous,
Alternatively, a granular material or the like can be used. Further, the type of activated carbon is not necessarily limited, and natural activated carbon such as coconut shell activated carbon, bone charcoal, charcoal, pitch type, petroleum coke type,
A burning activator such as resin or rubber or a chemical activator can be used, but the substances to be removed are often those having a relatively small molecular weight such as trihalomethane, and when considering the economical efficiency, steam activated coconut shell activated carbon is also considered. Is most practically used. Furthermore, in order to impart antibacterial properties,
You may attach silver etc.

【0025】本発明の浄水器用吸着材、活性炭に加え、
多孔質膜を用いると、鉄錆や細菌等の固形物を除去でき
るためより好ましい。多孔質膜としては、平膜、中空糸
膜、チューブラー膜等を用いることが出来るが、容積効
率が高い中空糸膜を用いることがより好ましい。
In addition to the adsorbent for water purifier and activated carbon of the present invention,
It is more preferable to use a porous film because solid substances such as iron rust and bacteria can be removed. As the porous membrane, a flat membrane, a hollow fiber membrane, a tubular membrane or the like can be used, but it is more preferable to use a hollow fiber membrane having high volume efficiency.

【0026】中空糸膜としては、例えば、セルロース
系、ポリオレフィン系(ポリエチレン、ポリプロピレ
ン)、ポリビニルアルコール系、エチレン・ビニルアル
コール共重合体、ポリエーテル系、ポリメタクリル酸メ
チル(PMMA)系、ポリスルフォン系、ポリアクリロ
ニトリル系、ポリ弗化エチレン(テフロン(登録商
標))系、ポリカーボネート系、ポリエステル系、ポリ
アミド系、芳香族ポリアミド系等の各種材料からなるも
のを好適に使用できる。中でも、膜の強伸度や耐屈曲
性、洗浄性、取扱性や耐薬品性の高さ等を考慮すると、
ポリエチレンやポロプロピレン等のポリオオレフィン系
中空糸膜が好ましい。また、特に限定されるものではな
いが、中空糸の外径は20〜2000μm、孔径は0.
01〜2μm、空孔率は20〜90%、膜厚は5〜30
0μmのものが好ましい。
Examples of the hollow fiber membrane include cellulose type, polyolefin type (polyethylene, polypropylene), polyvinyl alcohol type, ethylene / vinyl alcohol copolymer, polyether type, polymethylmethacrylate (PMMA) type, polysulfone type. Materials made of various materials such as polyacrylonitrile-based, polyfluorinated ethylene (Teflon (registered trademark))-based, polycarbonate-based, polyester-based, polyamide-based, and aromatic polyamide-based materials can be preferably used. Above all, considering the strength and elongation of the film, the bending resistance, the washability, the handleability and the high chemical resistance, etc.,
Polyoolefin-based hollow fiber membranes such as polyethylene and polypropylene are preferred. Although not particularly limited, the hollow fiber has an outer diameter of 20 to 2000 μm and a pore diameter of 0.
01 to 2 μm, porosity 20 to 90%, film thickness 5 to 30
It is preferably 0 μm.

【0027】本発明の浄水器において多孔質膜を使用す
る際には、他の濾材を水が通過した後の最終段に設ける
と、浄水出口からの菌逆汚染の懸念を最小限とできるた
め好ましい。本発明の浄水器用吸着材、活性炭について
は、どのような順序であっても、或いは、二者の混合を
して用いても差し支えない。また、活性炭に加えて、例
えばイオン交換樹脂、亜硫酸カルシウム、コーラルサン
ド、麦飯石、医王石、トルマリンなど他の成分を併用さ
せても構わない。
When a porous membrane is used in the water purifier of the present invention, if another filter medium is provided at the final stage after water has passed, the risk of reverse contamination of bacteria from the water purification outlet can be minimized. preferable. The adsorbent for a water purifier and the activated carbon of the present invention may be used in any order, or may be used as a mixture of the two. Further, in addition to the activated carbon, other components such as an ion exchange resin, calcium sulfite, coral sand, barley stone, meio stone, tourmaline may be used together.

【0028】本発明の浄水器用吸着材、活性炭、並びに
多孔質膜は、一つの容器内に収められていても、複数個
の容器に収められこれらを組み合わせた形のものでも構
わない。また、上記の組み合わせに更に一次フィルター
を用いて粗ゴミを予め除去できるようにすると好まし
い。
The adsorbent for a water purifier, activated carbon and porous membrane of the present invention may be contained in one container or a combination of a plurality of containers. Further, it is preferable to use a primary filter in addition to the above combination so that coarse dust can be removed in advance.

【0029】以下、実施例を基に本発明を具体的に説明
する。 <実施例1>ヒドロキシアパタイトと水の混合スラリー
を、110℃で乾燥し、30〜60メッシュの篩で篩い
分けしたあと、200℃で1時間加熱して、粒径250
μm〜500μmの浄水器用吸着剤を得た。得られた浄
水器用吸着剤について、日機装社製ベータソーブ自動表
面積計4200型を用いて、BET法により比表面積を
測定した。
The present invention will be specifically described below based on examples. Example 1 A mixed slurry of hydroxyapatite and water was dried at 110 ° C., sieved with a 30-60 mesh sieve, and then heated at 200 ° C. for 1 hour to give a particle size of 250.
An adsorbent for a water purifier having a size of μm to 500 μm was obtained. The specific surface area of the obtained adsorbent for a water purifier was measured by the BET method using a Betasorb automatic surface area meter 4200 type manufactured by Nikkiso Co., Ltd.

【0030】また、得られた浄水器用吸着剤について、
硝酸鉛水溶液を鉛濃度200mg/Lとなるように調製
して三角フラスコに200ml分取し、浄水器用吸着材
50mgを添加し、振とうさせた後、24時間後にフィ
ルターで濾過し、濾液水中の残留鉛濃度を測定すること
によって鉛吸着量を求めた。
Regarding the obtained adsorbent for water purifier,
An aqueous solution of lead nitrate was prepared to have a lead concentration of 200 mg / L, 200 ml was collected in an Erlenmeyer flask, 50 mg of the adsorbent for a water purifier was added, shaken, and after 24 hours, filtered with a filter to remove water in the filtrate water. The amount of lead adsorbed was determined by measuring the residual lead concentration.

【0031】また、得られた浄水器用吸着剤について、
島津製作所製微小圧縮試験機MCTM−200(平面圧
子500μm径)を用いて、負荷速度7.056×10
−3N/secにて測定を行い、圧縮強度を、St=
2.8P/πdの式より算出した。ここで、圧縮強
度;St(N/mm)、P;荷重(N)、d;粒子径
(mm)である。
Regarding the obtained adsorbent for water purifier,
Using Shimadzu Corporation micro compression tester MCTM-200 (plane indenter 500 μm diameter), load speed 7.056 × 10
-3 N / sec is measured and the compressive strength is St =
It was calculated from the formula of 2.8 P / πd 2 . Here, compressive strength: St (N / mm 2 ), P: load (N), d: particle diameter (mm).

【0032】また、得られた浄水器用吸着剤を用いて、
図1に示す構造の浄水器を作成した。ここで、1は浄水
器用吸着剤、2は100メッシュのナイロン製メッシュ
からなる多孔性仕切り板、3は多孔質中空糸膜、4は一
次フィルター、5は原水流入口、6は吐水口、7は容
器、8は膜モジュールケース、9はOリングである。な
お、浄水器用吸着剤は40g充填した。そして、この浄
水器に2L/minで総濾過量として2000L通水
し、通水前の浄水器用吸着剤の充填量(40g)と、多
孔性仕切り板を通過せずに残った浄水器用吸着剤の量
(37.2g)から、多孔性仕切り板を通過した微粉の
重量%((40−37.2)/40×100=7:以
下、これを微粉発生率という)を求めた。鉛吸着量、圧
縮強度、微粉発生率を表1に示した。
Further, using the obtained adsorbent for water purifier,
A water purifier having the structure shown in FIG. 1 was created. Here, 1 is an adsorbent for a water purifier, 2 is a porous partition plate made of 100 mesh nylon mesh, 3 is a porous hollow fiber membrane, 4 is a primary filter, 5 is a raw water inlet, 6 is a water outlet, 7 Is a container, 8 is a membrane module case, and 9 is an O-ring. 40 g of the adsorbent for the water purifier was filled. Then, 2000 L of water was passed through this water purifier at a rate of 2 L / min as a total filtration amount, and the filling amount (40 g) of the adsorbent for water purifier before water passage and the adsorbent for water purifier that remained without passing through the porous partition plate From the amount of (37.2 g), the weight% of the fine powder that passed through the porous partition plate ((40-37.2) / 40 × 100 = 7: hereinafter, referred to as the fine powder generation rate) was determined. Table 1 shows the amount of lead adsorbed, the compression strength, and the fine powder generation rate.

【0033】<実施例2>加熱固化温度を300℃とし
た以外は、実施例1と同様にして浄水器用吸着剤を作成
し、実施例1と同様にして比表面積、鉛吸着量、圧縮強
度を求めた。また、実施例1と同様の浄水器を作成し、
同様の通水を行って微粉発生率を求めた。結果は表1に
示した。
<Example 2> An adsorbent for a water purifier was prepared in the same manner as in Example 1 except that the heating and solidifying temperature was changed to 300 ° C, and the specific surface area, the amount of lead adsorbed, and the compression strength were obtained in the same manner as in Example 1. I asked. In addition, the same water purifier as in Example 1 was created,
The same water flow was performed to obtain the fine powder generation rate. The results are shown in Table 1.

【0034】<実施例3>加熱固化温度を500℃とし
た以外は、実施例1と同様にして浄水器用吸着剤を作成
し、実施例1と同様にして比表面積、鉛吸着量、圧縮強
度を求めた。また、実施例1と同様の浄水器を作成し、
同様の通水を行って微粉発生率を求めた。結果は表1に
示した。
<Example 3> An adsorbent for a water purifier was prepared in the same manner as in Example 1 except that the heating and solidifying temperature was set to 500 ° C, and the specific surface area, the amount of lead adsorbed, and the compression strength were obtained in the same manner as in Example 1. I asked. In addition, the same water purifier as in Example 1 was created,
The same water flow was performed to obtain the fine powder generation rate. The results are shown in Table 1.

【0035】<比較例1>加熱固化温度を110℃とし
た以外は、実施例1と同様にして浄水器用吸着剤を作成
し、実施例1と同様にして比表面積、鉛吸着量、圧縮強
度を求めた。また、実施例1と同様の浄水器を作成し、
同様の通水を行ったが、途中で中空糸膜が目詰まりした
ため2000L通水することはできなかったため、通水
不能になった時点での微粉発生率を求めた。結果は表1
に示した。
<Comparative Example 1> An adsorbent for a water purifier was prepared in the same manner as in Example 1 except that the heating and solidifying temperature was 110 ° C., and the specific surface area, the amount of lead adsorbed, and the compression strength were obtained in the same manner as in Example 1. I asked. In addition, the same water purifier as in Example 1 was created,
Water was passed through in the same manner, but 2000 L could not be passed because the hollow fiber membrane was clogged in the middle, so the rate of generation of fine powder at the time when water could not be passed was determined. The results are shown in Table 1.
It was shown to.

【0036】<比較例2>加熱固化温度を700℃とし
た以外は、実施例1と同様にして浄水器用吸着剤を作成
し、実施例1と同様にして比表面積、鉛吸着量、圧縮強
度を求めた。また、実施例1と同様の浄水器を作成し、
同様の通水を行って微粉発生率を求めた。結果は表1に
示した。
Comparative Example 2 An adsorbent for a water purifier was prepared in the same manner as in Example 1 except that the heating and solidifying temperature was 700 ° C., and the specific surface area, the amount of lead adsorbed, and the compression strength were obtained in the same manner as in Example 1. I asked. In addition, the same water purifier as in Example 1 was created,
The same water flow was performed to obtain the fine powder generation rate. The results are shown in Table 1.

【0037】[0037]

【表1】 [Table 1]

【0038】表1に示すように、温度200℃〜500
℃で加熱固化させた吸着剤は、鉛吸着量、圧縮強度が共
に高く、微粉発生率が低いため、浄水器に好適に用いる
ことができる。一方、温度110℃で加熱したものは、
鉛吸着量は高いものの微粉発生率が高く、従って崩れや
すいため浄水器用吸着剤としては適さない。また、70
0℃で加熱したものは、微粉発生率は低いものの、鉛吸
着量が低く、浄水器用吸着剤としては適さない。
As shown in Table 1, a temperature of 200 ° C. to 500 ° C.
The adsorbent solidified by heating at ℃ has a high lead adsorption amount, a high compression strength, and a low fine powder generation rate, and thus can be suitably used in a water purifier. On the other hand, the one heated at a temperature of 110 ° C
Although the amount of lead adsorbed is high, the rate of generation of fine powder is high, and therefore it easily collapses, so it is not suitable as an adsorbent for water purifiers. Also, 70
The one heated at 0 ° C has a low fine powder generation rate, but has a low lead adsorption amount, and is not suitable as an adsorbent for a water purifier.

【0039】[0039]

【発明の効果】本発明の浄水器用吸着材は、鉛の吸着量
が200mg/g以上かつ圧縮強度が1.0N/mm
よりも大きいため、通水した際に高い鉛除去能力を発揮
し、かつ通水中に崩れることが無いため浄水器用吸着剤
として好適である。また、本発明の浄水器用吸着材の製
造方法は、合成リン酸カルシウム系化合物の粉末を、2
00℃〜500℃で加熱固化させる為、吸着材の性能を
低下させることがない。さらに、本発明の浄水器は、鉛
等の重金属の除去性能を長期間に渡って発揮することが
できる。
The adsorbent for water purifiers of the present invention has a lead adsorption amount of 200 mg / g or more and a compressive strength of 1.0 N / mm 2.
Since it is larger than the above, it exhibits a high lead removal ability when water is passed through it, and it does not collapse during water passage, so it is suitable as an adsorbent for water purifiers. In addition, the method for producing an adsorbent for a water purifier according to the present invention uses a powder of a synthetic calcium phosphate-based compound,
Since it is heated and solidified at 00 ° C to 500 ° C, the performance of the adsorbent is not deteriorated. Further, the water purifier of the present invention can exhibit the heavy metal removal performance such as lead over a long period of time.

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

【図1】本発明の浄水器の一例を示す概略断面図であ
る。
FIG. 1 is a schematic cross-sectional view showing an example of a water purifier of the present invention.

【符号の説明】[Explanation of symbols]

1 浄水器用吸着剤 2 多孔性仕切り板 3 多孔質中空糸膜 4 一次フィルター 5 原水流入口 6 吐水口 7 容器 8 膜モジュールケース 9 Oリング Adsorbent for 1 water purifier 2 Porous partition plate 3 Porous hollow fiber membrane 4 primary filters 5 Raw water inlet 6 spout 7 containers 8 membrane module case 9 O-ring

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 20/30 B01J 20/30 Fターム(参考) 4D024 AA02 AB11 AB16 BA02 BA05 BA11 BB01 CA11 DB03 DB05 DB19 DB26 4G066 AA50B BA20 BA26 BA35 BA36 BA38 CA46 DA07 EA20 FA21 FA22 FA34 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) B01J 20/30 B01J 20/30 F term (reference) 4D024 AA02 AB11 AB16 BA02 BA05 BA11 BB01 CA11 DB03 DB05 DB19 DB26 4G066 AA50B BA20 BA26 BA35 BA36 BA38 CA46 DA07 EA20 FA21 FA22 FA34

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 鉛の吸着量が200mg/g以上かつ圧
縮強度が1.0N/mmよりも大きい浄水器用吸着
材。
1. An adsorbent for a water purifier having a lead adsorption amount of 200 mg / g or more and a compressive strength of more than 1.0 N / mm 2 .
【請求項2】 平均粒径が20〜750μmである請求
項1記載の浄水器用吸着材。
2. The adsorbent for a water purifier according to claim 1, which has an average particle size of 20 to 750 μm.
【請求項3】 リン酸カルシウム系化合物からなる請求
項1又は2に記載の浄水器用吸着材。
3. The adsorbent for a water purifier according to claim 1, which is composed of a calcium phosphate-based compound.
【請求項4】 前記リン酸カルシウム系化合物が、ヒド
ロキシアパタイト、リン酸三カルシウム、リン酸四カル
シウムから選ばれる少なくとも1種類以上である請求項
1〜3いずれかに記載の浄水器用吸着材。
4. The adsorbent for a water purifier according to claim 1, wherein the calcium phosphate compound is at least one selected from hydroxyapatite, tricalcium phosphate and tetracalcium phosphate.
【請求項5】 合成リン酸カルシウム系化合物の粉末を
200℃〜500℃で加熱固化する浄水器用吸着材の製
造方法。
5. A method for producing an adsorbent for a water purifier, which comprises heating and solidifying a powder of a synthetic calcium phosphate-based compound at 200 ° C. to 500 ° C.
【請求項6】 合成リン酸カルシウム系化合物の粉末と
水の混合スラリーを乾燥した後、200℃〜500℃で
加熱固化する請求項5記載の浄水器用吸着材の製造方
法。
6. The method for producing an adsorbent for a water purifier according to claim 5, wherein the mixed slurry of the synthetic calcium phosphate compound powder and water is dried and then solidified by heating at 200 ° C. to 500 ° C.
【請求項7】 前記乾燥温度が80〜150℃である請
求項6記載の浄水器用吸着材の製造方法。
7. The method for producing an adsorbent for a water purifier according to claim 6, wherein the drying temperature is 80 to 150 ° C.
【請求項8】 前記合成リン酸カルシウム系化合物が、
ヒドロキシアパタイト、リン酸三カルシウム、リン酸四
カルシウムのうち、少なくとも1種類以上である請求項
5〜7いずれかに記載の浄水器用吸着材の製造方法。
8. The synthetic calcium phosphate-based compound,
The method for producing an adsorbent for a water purifier according to any one of claims 5 to 7, wherein at least one kind of hydroxyapatite, tricalcium phosphate and tetracalcium phosphate is used.
【請求項9】 請求項1〜4いずれかに記載の浄水器用
吸着材を用いた浄水器。
9. A water purifier using the adsorbent for a water purifier according to claim 1.
JP2001391910A 2001-12-25 2001-12-25 Adsorbent for water cleaner, method for manufacturing the same and water cleaner using the adsorbent Pending JP2003190941A (en)

Priority Applications (1)

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Publication Number Publication Date
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Country Link
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105771875A (en) * 2016-05-18 2016-07-20 湖南大学 Magnetic nano-chlorine apatite adsorbent and preparation method thereof
CN105948157A (en) * 2016-05-18 2016-09-21 湖南大学 Method for removing heavy metals in waste water by using magnetic nano chlorapatite adsorbent
CN106000338A (en) * 2016-06-08 2016-10-12 芜湖市长江起重设备制造有限公司 Modified silica sol-based treatment agent used for crane electroplating wastewater and capable of effectively absorbing organic matters and preparation method thereof
CN106040169A (en) * 2016-06-08 2016-10-26 芜湖市长江起重设备制造有限公司 Wear-resistant crane electroplating wastewater treating agent and production method thereof
CN106064074A (en) * 2016-06-08 2016-11-02 芜湖市长江起重设备制造有限公司 A kind of crane compound for treatment of electroplating wastes of hole even density based on modified waster paper slag and preparation method thereof
CN106064075A (en) * 2016-06-08 2016-11-02 芜湖市长江起重设备制造有限公司 A kind of can the crane compound for treatment of electroplating wastes and preparation method thereof of deodorization

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02180706A (en) * 1988-12-31 1990-07-13 Tonen Corp Phosphorus compound grain assemblage and its production
JPH09299932A (en) * 1996-05-08 1997-11-25 Toto Ltd Purifying method of city water
JP2001047038A (en) * 1999-08-09 2001-02-20 Nonogawa Shoji Kk Cartridge for water cleaner

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02180706A (en) * 1988-12-31 1990-07-13 Tonen Corp Phosphorus compound grain assemblage and its production
JPH09299932A (en) * 1996-05-08 1997-11-25 Toto Ltd Purifying method of city water
JP2001047038A (en) * 1999-08-09 2001-02-20 Nonogawa Shoji Kk Cartridge for water cleaner

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105771875A (en) * 2016-05-18 2016-07-20 湖南大学 Magnetic nano-chlorine apatite adsorbent and preparation method thereof
CN105948157A (en) * 2016-05-18 2016-09-21 湖南大学 Method for removing heavy metals in waste water by using magnetic nano chlorapatite adsorbent
CN105948157B (en) * 2016-05-18 2019-01-29 湖南大学 Utilize the method for magnetic Nano chlorapatite adsorbent removal heavy metal in waste water
CN106000338A (en) * 2016-06-08 2016-10-12 芜湖市长江起重设备制造有限公司 Modified silica sol-based treatment agent used for crane electroplating wastewater and capable of effectively absorbing organic matters and preparation method thereof
CN106040169A (en) * 2016-06-08 2016-10-26 芜湖市长江起重设备制造有限公司 Wear-resistant crane electroplating wastewater treating agent and production method thereof
CN106064074A (en) * 2016-06-08 2016-11-02 芜湖市长江起重设备制造有限公司 A kind of crane compound for treatment of electroplating wastes of hole even density based on modified waster paper slag and preparation method thereof
CN106064075A (en) * 2016-06-08 2016-11-02 芜湖市长江起重设备制造有限公司 A kind of can the crane compound for treatment of electroplating wastes and preparation method thereof of deodorization

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