JPS6034789A - Filter medium for water purifier - Google Patents

Filter medium for water purifier

Info

Publication number
JPS6034789A
JPS6034789A JP14416583A JP14416583A JPS6034789A JP S6034789 A JPS6034789 A JP S6034789A JP 14416583 A JP14416583 A JP 14416583A JP 14416583 A JP14416583 A JP 14416583A JP S6034789 A JPS6034789 A JP S6034789A
Authority
JP
Japan
Prior art keywords
silver
water
activated carbon
copper
supported
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.)
Granted
Application number
JP14416583A
Other languages
Japanese (ja)
Other versions
JPH045518B2 (en
Inventor
Hidekama Ishizaki
石崎 日出鶴磨
Tsutomu Shibata
勉 柴田
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.)
Zojirushi Corp
Original Assignee
Zojirushi Vacuum Bottle 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 Zojirushi Vacuum Bottle Co Ltd filed Critical Zojirushi Vacuum Bottle Co Ltd
Priority to JP14416583A priority Critical patent/JPS6034789A/en
Publication of JPS6034789A publication Critical patent/JPS6034789A/en
Publication of JPH045518B2 publication Critical patent/JPH045518B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To obtain a filter medium for water purifier inhibiting proliferation of bacteria even if the water stagnates during purification, from a mixture consisting of 20-30wt% active carbon supporting silver, 10-15wt% active carbon supporting copper, and 55-70wt% pure active carbon. CONSTITUTION:20-30wt% active carbon supporting 0.35-1.0wt% silver on the surface, 10-15wt% active carbon supporting 0.5-3.0wt% copper on the surface, and 55-70wt% pure active carbon are mixed to obtain a filter medium for a water purifier. By regulating the amt. of silver supported by the active carbon to 0.35-1.0wt%, the concn. of silver ion in the stagnating water is regulated to 10-50ppb. When the above described filter medium is used, elution of silver is retarded by the presence of copper ion. Proliferation of bacteria is prevented even if stagnation of water for a long time is caused since proliferation of bacteria is inhibited by the sterilizing effect of coexisting copper ion.

Description

【発明の詳細な説明】 本発明は飲料水など生活用水を浄化、殺菌する浄水器用
ろ材に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a filter medium for a water purifier that purifies and sterilizes domestic water such as drinking water.

近年、上水道用原水の水質の悪化に伴ない、沈殿、ろ過
後、浄水場で消毒のため水に加えられる塩素量が増大し
、その結果、水道水中の残留塩素による不快な味とにお
いが問題となっている。この問題は、夏季に特に著しく
、最近では塩素だけでなく赤ジオの原因となる微生物に
よる不快な味とにおいが発生している。この水道水の残
留塩素を除去することを目的として、活性炭をろ材とす
る浄水器が提案され、家庭用として一部実用に供されて
いるが、この種の浄水器では、残留塩素の除去が行なわ
れる結果、停水時、浄水器内に滞留する水中で細菌の増
殖が生じ、通水初期に浄水器からでてくる水が飲料水と
して不適当となる欠点があった。このため、浄水器用ろ
材として、残留塩素の除去だけでなく細菌の増殖を抑制
する機能をも併有するろ材が、例えば、特公昭51−3
3608号公報、特公昭52−38666号公報、特開
昭51−90996号公報などにより提案され、実用に
供されるようになってきた。これらのろ材は、表面に銀
を担持させた活性炭(以下、銀担持活性炭という〕と活
性度とを混合したもので、活性炭で水中の塩素を吸着除
去する一方、残留塩素の除去に伴なう殺菌作用の低下を
銀担持活性炭から溶出する銀イオンの殺菌作用で補い、
細菌の増殖を抑制するようにしたものである。この種の
ろ材を用いた場合、滞水中での細菌の増殖を阻止する効
果は認められるが、その殺菌作用は水中での銀イオンの
濃度に依存するため、銀担持量が少ない場合あるいは水
温の低い冬季には、滞水中の細菌の増殖を防止すること
ができない欠点があった。銀担持量の問題は、夏季に銀
イオン濃度が米国飲料水水質基準の上限50 ppb以
−Lにならない範囲で銀担持量を増大させることにより
容易に解決できるが、低水温時の殺菌作用の低下を防止
することは不可能であった。
In recent years, as the quality of raw water for drinking water has deteriorated, the amount of chlorine added to water for disinfection at water treatment plants after sedimentation and filtration has increased, resulting in unpleasant taste and odor caused by residual chlorine in tap water. It becomes. This problem is particularly acute in the summer, and recently unpleasant tastes and odors have been caused not only by chlorine but also by the microorganisms that cause red geo. In order to remove residual chlorine from tap water, water purifiers using activated carbon as a filter material have been proposed, and some of them are in practical use for household use, but this type of water purifier cannot remove residual chlorine. As a result, when the water is stopped, bacteria proliferate in the water that remains in the water purifier, and the water that comes out of the water purifier at the beginning of water flow becomes unsuitable for drinking. Therefore, as filter media for water purifiers, filter media that not only removes residual chlorine but also suppresses the growth of bacteria are available, for example,
It has been proposed in Japanese Patent Publication No. 3608, Japanese Patent Publication No. 52-38666, Japanese Patent Application Laid-Open No. 51-90996, and has been put into practical use. These filter media are a mixture of activated carbon with silver supported on its surface (hereinafter referred to as silver-supported activated carbon) and high activity.While the activated carbon adsorbs and removes chlorine from water, it also removes residual chlorine. The decrease in bactericidal action is compensated for by the bactericidal action of silver ions eluted from silver-supported activated carbon.
It is designed to suppress the growth of bacteria. When this type of filter media is used, it is recognized that it is effective in inhibiting the growth of bacteria in standing water, but its bactericidal effect depends on the concentration of silver ions in the water, so if the amount of silver supported is small or the water temperature is In cold winter months, there was a drawback that it was not possible to prevent the growth of bacteria in standing water. The problem of the amount of silver supported can be easily solved by increasing the amount of silver supported in the summer to the extent that the silver ion concentration does not exceed the upper limit of 50 ppb-L of the U.S. drinking water quality standard, but the bactericidal effect at low water temperatures may be reduced. It was not possible to prevent the decline.

本発明は、冬季や夏季など季節のRO何を問わず、水道
水中の残留塩素を除去できると同時に、浄水器中に水が
滞留しても細菌の増殖をきたすことのない浄水器用ろ材
を得ることを目的とするもので、その要旨は、表面に銀
を担持させた活性炭10〜30重量%、表面に銅を担持
させた活性炭10〜15重量%、純活性炭残部からなる
ことを特徴とする浄水器用ろ材にある。
The present invention provides a filter medium for water purifiers that can remove residual chlorine from tap water regardless of the seasonal RO such as winter or summer, and at the same time does not cause bacterial growth even if water remains in the water purifier. It is characterized by consisting of 10 to 30% by weight of activated carbon with silver supported on its surface, 10 to 15% by weight of activated carbon with copper supported on its surface, and the remainder pure activated carbon. Found in filter media for water purifiers.

本発明の好ましい実施態様においては、銀担持活性炭と
して、表面に0.35〜1.0重量%の銀を担持させた
活性炭が使用される。また、銅担持活性炭として、表面
に0.5〜3.0重量%の銅を担持させた活性炭が使用
される。
In a preferred embodiment of the present invention, activated carbon having 0.35 to 1.0% by weight of silver supported on its surface is used as the silver-supported activated carbon. Further, as the copper-supported activated carbon, activated carbon having 0.5 to 3.0% by weight of copper supported on its surface is used.

銀担持活性炭のる材中の割合および銀担持量を前記のよ
うに定めたのは次の理由による。すなわち、銀担持活性
炭の割合が10重量%未満では、銀担持活性度粒子間の
間隔が大きすぎてその間にある多数の純活性炭粒子間を
通る水に完全に殺菌作用を及ぼすことができず、30重
量%を超えると銀担持量との関係で夏季に滞水中の銀イ
オン濃度が50 PPbを超える場合があるからである
。また、銀担持量が銀を担持する活性炭に対し0.35
〜1.0重量%とじたのは、冬季と夏季の如何を問わず
滞留水中の銀イオン濃度が10 PPb〜50ppbの
範囲におさまるようにすると共に、コストの点から定め
たものである。
The reason why the proportion and amount of silver supported in the silver-supported activated carbon material were determined as described above is as follows. That is, if the proportion of silver-supported activated carbon is less than 10% by weight, the spacing between the silver-supported active particles is too large and the water passing between the large number of pure activated carbon particles in between cannot be completely sterilized. This is because if the amount exceeds 30% by weight, the concentration of silver ions in the retained water may exceed 50 PPb in summer due to the amount of silver supported. In addition, the amount of silver supported is 0.35 compared to activated carbon that supports silver.
The reason for setting the silver ion concentration to 1.0% by weight was to keep the silver ion concentration in the retained water within the range of 10 PPb to 50 ppb regardless of whether it is winter or summer, and also from the viewpoint of cost.

また、銅担持活性炭は、銀担持活性炭から溶出する銀イ
オンとの相互作用によって、水中の細菌の増殖、特に、
水温の低い冬季における増殖を抑制することを目的とし
て併用されるもので、その含有量が10重量%未満では
、低温で増殖するアクロモバクタ−、フラボバクテリウ
ム、シュードモナスなどの増殖を阻止できず、15重量
%を超えると、滞水中での銅イオン濃度が高くなりすぎ
るからである。活性炭の銅担持量は、活性炭に対し0.
5〜3重量%に設定されているが、これは、冬季と夏季
における銅の溶出量が50 PPb〜IPPmの範囲内
にはいるようにするためである。
In addition, copper-supported activated carbon can inhibit the growth of bacteria in water, especially by interacting with silver ions eluted from silver-supported activated carbon.
It is used in combination with the purpose of suppressing the growth in winter when the water temperature is low, and if the content is less than 10% by weight, it will not be possible to inhibit the growth of Achromobacter, Flavobacterium, Pseudomonas, etc., which grow at low temperatures. This is because if the content exceeds % by weight, the concentration of copper ions in the retained water becomes too high. The amount of copper supported on activated carbon is 0.
The content is set at 5 to 3% by weight in order to ensure that the amount of copper eluted in winter and summer falls within the range of 50 PPb to IPPm.

一般に、常温での所定の殺菌効果を得るためには、銀イ
オン濃度は約20 ppb以上必要とされているが、本
発明のる材を用いた場合、銅イオンの存在によって銀の
溶出量が抑制され、銀イオン濃度が10 ppbJ)J
、下になっても、また、水温が10°Cに低下し銀イオ
ン濃度が10 ppb以下になっても、共存する銅イオ
ンの殺菌作用により細菌の増殖が抑制されるため、長時
間滞留しても細菌が増殖することがない。
Generally, in order to obtain the desired bactericidal effect at room temperature, a silver ion concentration of approximately 20 ppb or more is required, but when the material of the present invention is used, the amount of silver eluted is reduced due to the presence of copper ions. suppressed, and the silver ion concentration was 10 ppbJ)J
, even if the water temperature drops to 10°C and the silver ion concentration drops below 10 ppb, the bactericidal action of the coexisting copper ions suppresses the growth of bacteria, so the water remains in the water for a long time. However, bacteria will not grow.

本発明において使用する銀担持活性炭は、銀鏡反応によ
って活性炭の表面に銀を析出さ°せたものが好適である
。これは、銀鏡反応によって一表面に銀を析出させた活
性炭が、活性法自体の吸着能力および吸着容量を失なう
ことがなく、しかも任意の銀担持量のものを容易に得ら
れるからである。
The silver-supported activated carbon used in the present invention is preferably one in which silver is precipitated on the surface of the activated carbon by a silver mirror reaction. This is because activated carbon with silver precipitated on one surface by silver mirror reaction does not lose its adsorption capacity and adsorption capacity of the activation method itself, and it is easy to obtain any amount of silver supported. .

また、本発明において使用する銅担持活性炭は、無電解
メッキにより銅を活性炭表面に析出させたものが好適で
ある。この場合も、銀担持活性炭と同様、析出した銅が
活性法自体の吸着能力および吸着容量を損なうことがな
いからである。
Further, the copper-supported activated carbon used in the present invention is preferably one in which copper is deposited on the surface of the activated carbon by electroless plating. This is because, in this case as well, the deposited copper does not impair the adsorption ability and adsorption capacity of the activation method itself, as in the case of silver-supported activated carbon.

以下、本発明の実施例について説明する。Examples of the present invention will be described below.

実施例1 活性炭(粒度8〜32メツシユの水蒸気賦活やし殻活性
炭、以下、本実施例において同じ)200gを水洗、乾
燥させた後、10 PPmの塩化第一錫を含む水溶液2
00mJを加え、気泡の発生停止後、排液し、次いで硝
酸銀8gと28係アンモニア水100*tを含む水溶液
500πtと水酸化す) IJウム2.4fを含む水溶
液500mJとを混合して得た第1液IEを加えると同
時に、蔗糖10gを含む水溶液100++7に65%硝
酸0.5 mlを加え色力(黄変するまで煮沸し放玲し
た液24m1に水を加えて全量を1βとした第2液を加
え、20°Cで5分間よく攪拌しながら活性炭粒子表面
に銀を析出させた。次いで、銀を析出させた活性炭を数
回水洗し、110°Cで2時間熱風乾燥させ、活性炭1
g当り8、9 M9の銀を担持した銀担持活性炭を得た
Example 1 After washing and drying 200 g of activated carbon (steam-activated coconut shell activated carbon with a particle size of 8 to 32 mesh, the same applies hereinafter in this example), an aqueous solution 2 containing 10 PPm of stannous chloride was prepared.
00 mJ was added, and after the generation of bubbles had stopped, the liquid was drained, and then hydroxylated with 500 mJ of an aqueous solution containing 8 g of silver nitrate and 100 * t of 28% ammonia water. At the same time as adding the first liquid IE, 0.5 ml of 65% nitric acid was added to the aqueous solution 100++7 containing 10 g of sucrose for color strength. The two liquids were added and stirred well for 5 minutes at 20°C to precipitate silver on the surface of the activated carbon particles.Next, the activated carbon on which silver had been precipitated was washed with water several times and dried with hot air at 110°C for 2 hours to remove the activated carbon. 1
Silver-supported activated carbon carrying 8.9 M9 of silver per g was obtained.

また、これとは別に、活性炭20Ofを0.1%塩化パ
ラジウム溶液で洗浄した後、10 PPmの塩化第1錫
を含む水溶液200m1で洗い、排液し、次いで、ロッ
シェル塩170 y/l、水酸化ナトリウム50g/β
および硫酸銅35 f/l を含む水溶液30011/
、を加え、たyちに40%ホルムアルデヒド液150m
tを加えた後、50°Cにあたためて活性度粒子表向に
銅を析出させ、その後、水洗、乾燥させて活性炭1f当
り15.61119の銅を担持した銅担持活性炭を得た
Separately, 20Of activated carbon was washed with 0.1% palladium chloride solution, washed with 200ml of an aqueous solution containing 10 PPm of stannous chloride, drained, and then washed with 170 y/l of Rochelle salt and water. Sodium oxide 50g/β
and copper sulfate 35 f/l aqueous solution 30011/
, and immediately add 150ml of 40% formaldehyde solution.
After adding t, copper was precipitated on the surface of the activated particles by heating to 50°C, followed by washing with water and drying to obtain copper-supported activated carbon in which 15.61119 copper was supported per 1f of activated carbon.

このようにして得た銀担持活性炭37.59と、銅担持
活性炭37.5gと、純粋な活性炭225gを混合して
浄水器用ろ材とし、滞留水中の生菌数、銅、銀の溶出量
を測定した。それらの結果を比較例A、Cについての結
果と共に表1に示す。
37.59 g of silver-supported activated carbon thus obtained, 37.5 g of copper-supported activated carbon, and 225 g of pure activated carbon were mixed to make a filter material for a water purifier, and the number of viable bacteria and the elution amount of copper and silver in the retained water were measured. did. The results are shown in Table 1 together with the results for Comparative Examples A and C.

比較例Aは銀担持活性炭と純活性度とを混合して成るろ
材であり、ろ材1g当りの銀の量は1.34〜であった
。比較例Bは銀担持活性炭と純活性炭を含むろ材であり
、ろ材1g当りの銀の量は0.71夕であった。比較例
Cは銀担持活性炭と純活性炭を含むろ材であり、ろ材1
g当りの銀の量は1mgであった。
Comparative Example A is a filter medium made of a mixture of silver-supported activated carbon and pure activation, and the amount of silver per gram of filter medium was 1.34~. Comparative Example B is a filter medium containing silver-supported activated carbon and pure activated carbon, and the amount of silver per gram of filter medium was 0.71. Comparative example C is a filter medium containing silver-supported activated carbon and pure activated carbon, and filter medium 1
The amount of silver per g was 1 mg.

なお、生菌数の測定は、浄水器を水道水蛇口に取付け、
304放水した後、表に示す規定時間滞水させ、時間経
過後、初期流出水50m1を採取し、その中1πtをペ
トリ皿にとり、標準寒天培養法により一般生菌について
測定した。また、銀および銅の溶出量については、規定
時間滞水後、初期流出水250s+tを採取し、濃硝酸
1mlを加え煮沸して10倍にa縮し、原子吸光法によ
り定量した。
In addition, to measure the number of viable bacteria, attach the water purifier to the tap water faucet,
After 304 hours of water was discharged, the water was allowed to stand for the specified time shown in the table, and after the time had elapsed, 50 ml of the initial runoff water was collected, 1πt of it was placed in a Petri dish, and the presence of common viable bacteria was measured using a standard agar culture method. Regarding the amount of silver and copper eluted, 250 s+t of the initial effluent water was collected after the water had been retained for a specified period of time, and 1 ml of concentrated nitric acid was added and boiled to reduce the amount by 10 times, and the amount was determined by atomic absorption spectrometry.

また、生菌数の測定は、6月に行ない、測定時の水温は
20°Cであった。
The number of viable bacteria was measured in June, and the water temperature at the time of measurement was 20°C.

表1 表1の結果から明らかなように、本発明に係るろ材を用
いた浄水器は、72時間滞水後であっても生菌数はOで
、銀の溶出量も18 ppbと米国の飲料水水質基準の
50 PPb以下を充分に満足し、また、銅についても
108〜135 ppbと基準値I PPm以下を充分
に下まわっており、比較例A〜C°に示す従来のものに
比して優れた性能を示す。
Table 1 As is clear from the results in Table 1, the water purifier using the filter medium according to the present invention has a viable count of O even after 72 hours of water retention, and an eluted amount of silver of 18 ppb, which is lower than that of the United States. It fully satisfies the drinking water quality standard of 50 PPb or less, and also has copper content of 108 to 135 ppb, which is well below the standard value I PPm or less, and is better than the conventional ones shown in Comparative Examples A to C°. shows excellent performance.

実施例2 実施例1と同様にして、活性77117当り17.31
ffgの銀を担持した銀担持活性炭を製造し、この銀担
持活性炭15重量部、実施例1で用意した銅担持活性炭
10重量部、および純活性炭75重量部を混合し、この
混合物をろ材としてカートリッジに充填して浄水器にセ
ットして、水道蛇口に取付け、実施例1と同様にして、
冬季における規定時間滞留後の初期流出水(水温10°
C)中の一般生菌数および銀、銅の溶出量を測定した。
Example 2 In the same manner as in Example 1, 17.31 per active 77117
Silver-supported activated carbon carrying ffg of silver was produced, and 15 parts by weight of this silver-supported activated carbon, 10 parts by weight of the copper-supported activated carbon prepared in Example 1, and 75 parts by weight of pure activated carbon were mixed, and this mixture was used as a filter material in a cartridge. Fill it up, set it in the water purifier, attach it to the water faucet, and do the same as in Example 1.
Initial runoff water after staying for a specified time in winter (water temperature 10°)
The number of general viable bacteria and the amount of silver and copper eluted in C) were measured.

その結果を表2に示す。The results are shown in Table 2.

表2の結果から明らかなように、本発明のる材は低温に
おいても優れた細菌増殖防止効果を示す。
As is clear from the results in Table 2, the lumber of the present invention exhibits an excellent bacterial growth prevention effect even at low temperatures.

なお、上記実施例においては、銀と銅をそれぞれ別々に
活性炭に担持させているが、銀担持活性炭の表面にさら
に銅を析出させたもの、あるいは銅担持活性炭の表面に
さらに銀を析出させたものを使用することも可能である
。いずれの場合も、銀および銅の析出は、実施例に記載
の方法により行なうことができる。しかし、銀および銅
を同一活性炭粒子の表面に担持させた場合、先に担持さ
せた金属の溶出量が著しく低下し、またコストの面で難
点を生じるので、実施例のように別々に担持させるのが
好ましい。
In the above examples, silver and copper are supported on activated carbon separately, but copper is further precipitated on the surface of silver-supported activated carbon, or silver is further precipitated on the surface of copper-supported activated carbon. It is also possible to use In either case, silver and copper can be deposited by the methods described in the Examples. However, if silver and copper are supported on the surface of the same activated carbon particles, the amount of the previously supported metal will be significantly reduced, and there will also be a problem in terms of cost, so they are supported separately as in the example. is preferable.

以上説明したように、本発明によれば、銀担持活性炭と
銅担持活性炭を純活性炭と併用することにより季節の如
何を問わず、滞水中の細菌の増殖を防止でき、しかも、
水道水中の残留塩素による不快な味やにおいを完全に除
去することができる。
As explained above, according to the present invention, by using silver-supported activated carbon and copper-supported activated carbon in combination with pure activated carbon, the growth of bacteria in standing water can be prevented regardless of the season, and furthermore,
The unpleasant taste and odor caused by residual chlorine in tap water can be completely removed.

特許出願人 象印マホービン株式会社 代理人弁理士 青白 葆 ほか2名Patent applicant: Zojirushi Mahobin Co., Ltd. Representative patent attorney: Aohaku Ao and 2 others

Claims (3)

【特許請求の範囲】[Claims] (1)銀担持活性炭20〜30重量%、銅担持活性炭1
0〜15重量%、および純活性炭55〜70重量%を混
合してなることを特徴とする浄水器用ろ材。
(1) Silver-supported activated carbon 20-30% by weight, copper-supported activated carbon 1
A filter medium for a water purifier, characterized in that it is a mixture of 0 to 15% by weight of pure activated carbon and 55 to 70% by weight of pure activated carbon.
(2)銀担持活性炭が0.35〜1.0重量%の銀を担
持する特許請求の範囲第1項記載のろ材。
(2) The filter medium according to claim 1, wherein the silver-supported activated carbon supports 0.35 to 1.0% by weight of silver.
(3)銅担持活性炭が0.5〜3%の銅を担持する特許
請求の範囲第1項または第2項記載のる材。
(3) The material according to claim 1 or 2, wherein the copper-supported activated carbon supports 0.5 to 3% copper.
JP14416583A 1983-08-05 1983-08-05 Filter medium for water purifier Granted JPS6034789A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14416583A JPS6034789A (en) 1983-08-05 1983-08-05 Filter medium for water purifier

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14416583A JPS6034789A (en) 1983-08-05 1983-08-05 Filter medium for water purifier

Publications (2)

Publication Number Publication Date
JPS6034789A true JPS6034789A (en) 1985-02-22
JPH045518B2 JPH045518B2 (en) 1992-01-31

Family

ID=15355710

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14416583A Granted JPS6034789A (en) 1983-08-05 1983-08-05 Filter medium for water purifier

Country Status (1)

Country Link
JP (1) JPS6034789A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0271889A (en) * 1988-09-08 1990-03-12 Takuma Co Ltd Water purifier
JPH04210286A (en) * 1990-11-30 1992-07-31 Sharp Corp Water purifying filter for automatic ice manufacturing device
EP1319630A1 (en) * 2001-12-15 2003-06-18 Salamander (Engineering) Limited Anti-bacterial treatment

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0271889A (en) * 1988-09-08 1990-03-12 Takuma Co Ltd Water purifier
JPH04210286A (en) * 1990-11-30 1992-07-31 Sharp Corp Water purifying filter for automatic ice manufacturing device
EP1319630A1 (en) * 2001-12-15 2003-06-18 Salamander (Engineering) Limited Anti-bacterial treatment

Also Published As

Publication number Publication date
JPH045518B2 (en) 1992-01-31

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