JP5924464B2 - Centralized management system for water supply lines - Google Patents
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- JP5924464B2 JP5924464B2 JP2010255341A JP2010255341A JP5924464B2 JP 5924464 B2 JP5924464 B2 JP 5924464B2 JP 2010255341 A JP2010255341 A JP 2010255341A JP 2010255341 A JP2010255341 A JP 2010255341A JP 5924464 B2 JP5924464 B2 JP 5924464B2
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/152—Water filtration
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- Treatment Of Water By Ion Exchange (AREA)
- Removal Of Specific Substances (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Domestic Plumbing Installations (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Description
本発明は戸建て住宅において家内の給水回路の水質を水の使用目的に対応して改質する技術に関する。さらに詳しくは水道メーターを経由して家庭に供給される水道水を給水栓以降(水道メータ以降)の段階で水の利用目的に最適なように水質を変化させて多種類の水質の水を消費点まで供給する管理システムである。 The present invention relates to a technique for modifying the water quality of a water supply circuit in a house in accordance with the purpose of use of water in a detached house. More specifically, tap water supplied to the home via a water meter changes the water quality at the stage after the water tap (after the water meter) and consumes water of various types by changing the water quality. It is a management system that supplies up to a point.
マンションに限らず戸建には居住者の水道水の水質を自由に変えて、水利用の目的に適用した水質にしたいとの要望がある。実際、戸建の家の水道の一部には浄水器を設置している。この場合の浄水器設置の目的は赤水が出ないこと、塩素臭がしないことにある。この場合の浄水器の機能として残留遊離塩素の除去である。そのためにこの種の浄水器には活性炭は利用されているが、使用初期では浄水器によって遊離塩素濃度が0ppmとなり、かびが発生する問題点がある。しかも活性炭の場合、長時間使用していると活性炭内部の孔に微生物を増殖している場合もある。 Not only condominiums but also detached houses have a desire to change the quality of residents' tap water freely so that it can be used for the purpose of water use. In fact, a water purifier is installed in a part of the water supply of a detached house. The purpose of installing the water purifier in this case is to prevent red water from coming out and to prevent the smell of chlorine. The function of the water purifier in this case is removal of residual free chlorine. For this reason, activated carbon is used in this type of water purifier, but the concentration of free chlorine is 0 ppm due to the water purifier in the initial stage of use, which causes mold. In addition, when activated carbon is used for a long time, microorganisms may grow in the pores inside the activated carbon.
軟水器の例のようにイオンを除去する浄水器もある。これは水中のカルシウムイオンやマグネシウムイオンを除去する機能を持つ。この浄水器はイオン交換樹脂を内臓している。この種の除水器にはイオン以外の物質(例、有機物や微生物など)を除去する機能を持たない。また浄水器の大きさや使用目的との関係で軟水は給湯器や業務用の料理用水として用いられる。 Some water purifiers remove ions, as in the example of water softeners. This has the function of removing calcium and magnesium ions in the water. This water purifier contains an ion exchange resin. This type of dehydrator does not have a function of removing substances other than ions (eg, organic substances and microorganisms). In addition, soft water is used as a water heater or cooking water for business purposes in relation to the size of the water purifier and the purpose of use.
水道管からの赤錆やクリプトスポリジウムなどの原虫の除去に高分子膜を装着した浄水器も市販されている。高分子膜としては除菌性を持つ膜が利用されている。しかし水道水の供給ラインが外気に開放される個所のある集合住宅(受水槽や高架水槽のあるマンション等)や戸建ての住宅での複数の水道栓がある場合には外気より微生物の混入の可能性が起こり、特に活性炭により遊離塩素を0.1ppm以下に除去している場合には微生物汚染の問題は深刻である。 Water purifiers equipped with a polymer membrane are also commercially available to remove protozoa such as red rust and Cryptosporidium from water pipes. As the polymer membrane, a membrane having sterilizing properties is used. However, if there are multiple taps in an apartment house where the tap water supply line is open to the open air (such as a condominium with a water receiving tank or an elevated water tank) or a detached house, microorganisms can be mixed from the open air. In particular, the problem of microbial contamination is serious when free chlorine is removed to 0.1 ppm or less by activated carbon.
特許文献1には空調等の冷却水に対して水中に溶解するカルシウム、マグネシウム、鉄やアルミニウムに対して従来の軟水器を用い、シリカに対しては凝集剤を用い、沈殿物に対してはミクロフィルターを用いたことにより、冷却水としての省エネルギー、環境対策、リサイクル可能な技術としての提案がある。ただしこの処理に対して安全性に対する対策が不足し戸建て住宅の水道水には適用できない。 Patent Document 1 uses a conventional water softener for calcium, magnesium, iron and aluminum that dissolves in cooling water for air conditioning and the like, uses a flocculant for silica, and for precipitates By using microfilters, there are proposals for energy saving as cooling water, environmental measures, and recyclable technology. However, this measure cannot be applied to tap water in detached houses due to lack of safety measures.
ウイルス除去の機能を有する浄水器も提案されている。例えば特許文献2のようにナノ繊維層を複数個積層することにより微生物を除去する。しかしウイルス除去性能は対数除去性能表示で3以上(99.9%以上の除去能)でかつふるい効果での除去機構で、除去性能に予測性を持たなくては未知ウイルス対策とはならない。 A water purifier having a virus removal function has also been proposed. For example, as in Patent Document 2, microorganisms are removed by laminating a plurality of nanofiber layers. However, the virus removal performance is 3 or more (removability of 99.9% or more) on the logarithmic removal performance display and a removal mechanism with a sieving effect.
戸別セントラル浄水で複数の浄化処理を行い有害物質を効率よく除去すると共に自動管理する技術の提案がある(特許文献3)。この方法ではウイルス除去の具体的提案もないし、水の消費目的に応じた水質の水が得られることはない。 There is a proposal of a technique for performing a plurality of purification processes with door-to-door central water purification to efficiently remove harmful substances and automatically manage them (Patent Document 3). In this method, there is no specific proposal for virus removal, and water of a quality suitable for the purpose of water consumption is not obtained.
浄化器の設置個所として水道の蛇口に取り付けるもの、屋内配管に組み込むもの(メインの水道栓の他に浄水器用の水道栓を持つもの)、あるいは水道メーターの後の回路に直結させたセントラル方式とがある。いずれの方式でも水も消費目的に対応した水の改質を実施するには処理効果を奥にする除水器を水道栓の数程度設置しなくてはならない。 A central system that is attached to a water faucet as a place to install a purifier, one that is built into an indoor pipe (one that has a water faucet for the water purifier in addition to the main water faucet), or a central system that is directly connected to the circuit after the water meter There is. In any method, in order to carry out water reforming in accordance with the purpose of consumption, it is necessary to install as many dewatering devices as the number of water taps that make the treatment effect deep.
水道水として各家庭に供給される水を、水の利用目的に応じて改質し、おいしい水、安全な水、管理に容易な水、として多種類の水を作製する。その水の作製を多種類の浄水器を各水道栓に装着するのではなく給水ラインの管理によって実現する。そのためには必要な水の種類の数と具体的にそれぞれの水の性質とその水の性質を与える水道水の改質方法とそれらの水の配送方法および改質用装置の設置方法を確立しなくてはならない。 The water supplied to each household as tap water is modified according to the purpose of use of water, and various kinds of water are produced as delicious water, safe water, and water that is easy to manage. The production of the water is realized by managing the water supply line instead of attaching various types of water purifiers to each water tap. To that end, we established the number of types of water required, specifically the properties of each water, the method of reforming tap water that gives the properties of the water, the method of delivering those water, and the method of installing the device for reforming. Must-have.
家庭用の水の使用目的は7種類に分類できる。すなわち(1)飲料水として1人当たり1日3リットル、(2)風呂用70リットル、(3)トイレ用70リットル、(4)洗濯用70リットル、(5)台所用65リットル(6)洗面所15リットル(7)その他(炊事、掃除、レジャー、散水用)7リットルである。これらの7種類の水に対して(1)に対しては安全性、低遊離塩素濃度(2)低遊離塩素濃度(3)高遊離塩素濃度、(4)軟水(5)適度の遊離塩素濃度(6)低塩素濃度と軟水(7)低シリカ濃度の要求性能が求められる。一日に必要な水量の比率を考慮した給水ラインを設計する必要がある。 The purpose of using household water can be classified into seven types. (1) 3 liters per person per day as drinking water, (2) 70 liters for baths, (3) 70 liters for toilets, (4) 70 liters for washing, (5) 65 liters for kitchens (6) Toilet 15 liters (7) Others (for cooking, cleaning, leisure, watering) 7 liters. For these seven types of water, safety for (1), low free chlorine concentration (2) low free chlorine concentration (3) high free chlorine concentration, (4) soft water (5) moderate free chlorine concentration (6) The required performance of low chlorine concentration and soft water (7) low silica concentration is required. It is necessary to design a water supply line that takes into account the ratio of the amount of water required per day.
水道水の使用目的を整理し、目的ごとに要求される性能を水質の観点でまとめることによって本発明の可能性が確認できた。すなわち供給される水道水中の遊離塩素濃度が0.5ppm以上でありPH<7であることを前提として、(a)低い遊離塩素濃度(b)PH=7〜8(c)軟水化(d)細菌、ウイルス、プリオン除去する技術を組み合わせれば目的ごとに最適化した水を供給できる。 The possibility of the present invention could be confirmed by organizing the purpose of use of tap water and summarizing the performance required for each purpose from the viewpoint of water quality. That is, assuming that the free chlorine concentration in the supplied tap water is 0.5 ppm or more and PH <7, (a) low free chlorine concentration (b) PH = 7-8 (c) water softening (d) Combining technologies that remove bacteria, viruses, and prions can provide optimized water for each purpose.
本発明の最大の特徴は戸建て住宅において各戸ごとの量水器より戸内へ給水する回路において、量水器より戸内への給水ラインが分岐する直後で水質を変化させる処理を加える点にある。分岐直後の配管部で水の改質処理を施すことにより、水の配水ラインとして処理前のラインと処理後のラインとの2種の水質の水が存在する。分岐直後であるために配管の管理が容易でかつ処理操作の時間的余裕が生じる。分岐点の数は6以上必要である。 The greatest feature of the present invention is that, in a detached house, in a circuit for supplying water from a meter for each door to the door, a process for changing the water quality immediately after the water supply line from the meter to the door forks is added. . By performing the water reforming process in the pipe part immediately after branching, there are two types of water quality water, a pre-treatment line and a post-treatment line, as water distribution lines. Since it is immediately after branching, the management of the piping is easy and a time margin for the processing operation occurs. The number of branch points should be 6 or more.
本発明では消費点での給水の目的に対応して水質を3種以上に変えることが特徴である。すなわち水道水として供給される水はそのままトイレ用および散水やレジャー用台所用水としての給水ラインを形成する。遊離塩素濃度を低めた処理を施した水は風呂用および洗面用としての給水ラインとなる。カルシウムやマグネシウム濃度を低下させかつ溶解しているシリカ成分を超軟水を供給するラインである。これら3種の供給ラインを組み合せると原理上7種類の水を供給することが出来る。 The present invention is characterized in that the water quality is changed to three or more according to the purpose of water supply at the consumption point. That is, the water supplied as tap water forms a water supply line as it is for toilets, sprinkling water and kitchen water for leisure. The water subjected to the treatment with a reduced free chlorine concentration serves as a water supply line for bathing and washing. This is a line for reducing the concentration of calcium and magnesium and supplying ultra-soft water to a dissolved silica component. By combining these three types of supply lines, seven types of water can be supplied in principle.
水からの微生物感染を防止するために特定された平均孔径と膜厚を持った多層構造膜を用いて微生物感染防止の給水ラインを加えることも可能である。この給水ラインで達成される新たな水質を取り入れると原理上15種類の水質を持つ水が入手できる。該15種類の水の特徴と生活の場で重要な温湯の供給とを考慮し、給水ラインを最小数の管理項目で集中管理する給水ラインを5種に集中化することが可能であることを発見したことで本発明の給水ラインの集中管理システムが完成した。 In order to prevent microbial infection from water, it is also possible to add a water supply line for preventing microbial infection using a multilayer structure film having a specified average pore size and film thickness. Incorporating new water quality achieved in this water supply line, in principle, water with 15 types of water quality can be obtained. In consideration of the characteristics of the 15 types of water and the supply of hot water important in daily life, it is possible to centralize the water supply lines to 5 types that centrally manage the water supply lines with the minimum number of management items. As a result of the discovery, the centralized water supply line management system of the present invention was completed.
本発明の給水ラインの特徴は、水質を異にする水を供給するのに水の消費目的を考慮して給水ラインの分岐の単純さにある。すなわち水道水として供給された水はまず(1)低遊離塩素水(低塩素水と略称)と(2)未処理水道水に分岐される。低塩素水はさらに(イ)微生物除去した飲料水用と(ロ)低塩素水のままの風呂場か洗面所水用と、(ハ)超軟水処理した水(超軟水と略称)へ3分岐する。(ハ)の超軟水は(ニ)給湯機を経由する水と(ハ)の超軟水のまま洗濯用水、掃除用(窓ガラス掃除など)洗車用水とに分岐される。(2)の未処理水道水はトイレ用、台所用、その他雑用(レジャー用、散水など)に利用する。 The water supply line of the present invention is characterized by the simplicity of the branching of the water supply line in consideration of the purpose of water consumption to supply water of different water quality. That is, the water supplied as tap water is first branched into (1) low free chlorine water (abbreviated as low chlorine water) and (2) untreated tap water. The low-chlorine water is further divided into (i) for drinking water from which microorganisms have been removed, (b) for bathroom or washroom water with low chlorine water, and (c) water that has been treated with ultra-soft water (abbreviated as ultra-soft water). To do. The (c) ultra-soft water is branched into (d) water passing through the water heater and (c) water for washing and cleaning (for window glass cleaning, etc.) for car washing. (2) Untreated tap water is used for toilets, kitchens, and other miscellaneous purposes (leisure, watering, etc.).
低塩素水および超軟水のように水質を変化させる処理の際、処理用材料から水中へ毒性物質等の溶解や変性があってはならない。また水道への微生物等の感染性物質が混入しない処理を加えておくことが必要である。 In the process of changing the water quality such as low chlorine water and ultra-soft water, there should be no dissolution or modification of toxic substances from the processing material into the water. In addition, it is necessary to add a treatment to prevent infectious substances such as microorganisms from entering the water supply.
低塩素水を与える低塩素化処理はウイルス除去膜を介して還元作用のある食品添加剤を給水ラインに注入する。注入の方法として孔拡散・濾過法であり、ウイルス除去膜は平均孔径が10nm〜30nmで膜厚が30μm以上200μm以下の再生セルロース製の多層構造膜である。孔拡散・濾過法とは水に溶解または分散した物質が膜中の孔を拡散で移動し、膜間差圧がたとえば0.05気圧以下の小さな圧力にすることにより水の濾過による移動速度を小さくした孔拡散を意味する。孔拡散・濾過法では物質が膜中の孔を透過する際の駆動力は濃度勾配が中心であり、物質のブラウン運動によって拡散するのが特徴で膜の孔の目詰まりがない物質の膜輸送である孔拡散の一種である。この運動に加えて圧力差による体積流れ(すなわち濾過)が加わるがこれによっての物質移動速度はブラウン運動による速度より小さい。In the low chlorination treatment that gives low chlorine water, a food additive having a reducing action is injected into a water supply line through a virus removal membrane. The injection method is a pore diffusion / filtration method, and the virus removal membrane is a multilayered membrane made of regenerated cellulose having an average pore diameter of 10 nm to 30 nm and a thickness of 30 μm to 200 μm. The pore diffusion / filtration method is a method in which the substance dissolved or dispersed in water moves through the pores in the membrane by diffusion, and the transmembrane differential pressure is reduced to a small pressure of, for example, 0.05 atm or less, thereby reducing the movement speed by water filtration. Means reduced pore diffusion. In the pore diffusion / filtration method, the driving force when a substance permeates through the pores in the membrane is centered on the concentration gradient, and is diffused by the Brownian motion of the material, and the membrane transports the material without clogging the pores of the membrane. Is a kind of pore diffusion. In addition to this motion, a volume flow (ie, filtration) due to a pressure difference is added, but the mass transfer speed is smaller than that due to the Brownian motion.
還元作用を持つ食品添加剤としてはクエン酸、アスコルビン酸およびそれらのアルカリ金属塩特にアスコルビン酸ナトリウムが適する。アスコルビン酸ナトリウム固体を封筒状に成型したウイルス除去膜内に充填する。薬剤を内蔵した該封筒状の膜を孔拡散・濾過モジュール内に装填して低塩素化処理用装置とする。 Suitable food additives with a reducing action are citric acid, ascorbic acid and their alkali metal salts, especially sodium ascorbate. It fills the inside of the virus removal membrane which shape | molded the sodium ascorbate solid in the shape of an envelope. The envelope-like membrane containing the drug is loaded into the hole diffusion / filtration module to form a low chlorination treatment apparatus.
超軟水化方法としてはまず無定形水酸化第二鉄コロイド粒子(粒経5nm以上で20nm以下)を添加して陰イオンで荷電しているイオンおよび微粒子を凝集し、沈殿化させる。次に陽イオンで荷電しているイオンおよび粒子を陽イオン交換性を持つ不織布または織布で濾過除去する。陽イオン交換容量が0.05ミリ当量/g以上で0.5ミリ当量/g以下であることが望ましい。これ以上の交換容量にすると不織布や織布としての形状維持がむつかしくなる。 As an ultra-softening method, first, amorphous ferric hydroxide colloidal particles (particle size of 5 nm or more and 20 nm or less) are added to aggregate and precipitate ions and fine particles charged with anions. Next, ions and particles charged with a cation are removed by filtration with a non-woven fabric or a woven fabric having a cation exchange property. The cation exchange capacity is desirably 0.05 meq / g or more and 0.5 meq / g or less. If the exchange capacity is larger than this, it is difficult to maintain the shape as a nonwoven fabric or a woven fabric.
織布および不織布を袋状に成型し、袋状物の長軸の方向が水平面に対して2〜10度の角度になるように設置し、処理対象水は袋状物の内部を通過する。この袋状物は陽イオンを吸着するのみでなく水中の微粒子の流動通過を防害する。 A woven fabric and a non-woven fabric are molded into a bag shape and installed so that the direction of the long axis of the bag-like material is an angle of 2 to 10 degrees with respect to the horizontal plane, and the water to be treated passes through the inside of the bag-like material. This bag-like material not only adsorbs cations but also prevents the passage of fine particles in water.
本発明により水道水として供給された水がその使用目的に対応してその性質を変えることが可能となる。すなわち飲料水用の水は遊離塩素濃度が低く、かつ微生物等の微粒子が存在しない安全でおいしい水となっている。風呂用と洗面用水は低塩素でかつ超軟水で給湯機を経由した湯水と低塩素の水の両者が供給される。給湯機への水は低塩素で超軟水であるため配管内のさびやスケールの付着が防止される。トイレ用、レジャー用、散水用は供給される水道水そのものが供給され遊離塩素濃度が高く細菌やカビの発生はない。台所用水として塩素濃度の高い水道水と低塩素で超軟水の湯と水とが供給され料理用や食器洗浄関係用と使い分けることができる。低塩素で超軟水はそのまま洗濯用、掃除用、洗車用として利用され乾燥後の窓ガラスのくもりが防止できる。 According to the present invention, water supplied as tap water can change its properties in accordance with its intended use. That is, the water for drinking water is a safe and delicious water having a low free chlorine concentration and no microparticles such as microorganisms. Both bath water and wash water are supplied with low chlorine and ultra soft water, both hot water and low chlorine water via a water heater. The water to the water heater is low-chlorine and ultra-soft water, which prevents rust and scale from adhering to the piping. For toilets, leisure and watering, the supplied tap water itself is supplied and the concentration of free chlorine is high and there is no generation of bacteria or mold. Kitchen water is supplied with tap water with high chlorine concentration and low-chlorine ultra-soft water and water, which can be used separately for cooking and dishwashing. Low chlorine and ultra soft water can be used as it is for washing, cleaning and car washing, and can prevent fogging of the window glass after drying.
図1に各戸に配水された水道水がそれぞれの消費場所へ送水される際の配管の様子をまとめて示す。配管は実線で示した給水管と破線で示された給湯管の2種類である。いずれも架橋ポリエチレン管で該管はサヤ管でカバーされ、給水管は青色で、給湯管は赤色で区別される。3個以上に分岐する個所は3〜5連のヘッダーを用い2個に分岐する場合にはソケットを用いる。水道水の水質を換える処理は(1)低塩素化(2)超軟水(3)微粒子除去(図中F)の3種である。 FIG. 1 summarizes the state of piping when tap water distributed to each house is sent to each consumption place. There are two types of piping: a water supply pipe indicated by a solid line and a hot water supply pipe indicated by a broken line. Each is a cross-linked polyethylene pipe, which is covered with a sheath pipe, the water supply pipe is distinguished in blue, and the hot water supply pipe is distinguished in red. Where three or more branches are used, 3 to 5 headers are used, and when two branches are used, sockets are used. There are three types of treatment for changing the quality of tap water: (1) low chlorination, (2) ultra-soft water, and (3) fine particle removal (F in the figure).
低塩素化処理装置の例を図2に示す。還元性の食品添付剤を固体状態でウイルス除去膜で包み込む。ウイルス除去膜と支持体で構成される複合体膜で薬剤を封入した容器を用い覆い、さらにもう一枚の複合体膜で覆った孔拡散・濾過用の容器と密着させる。この装置により食品添加剤は溶解→孔拡散濾過により水道水中へ拡散する。食品添加剤としてアスコルビン酸ナトリウムを採用する。水道水のPHを7.5〜8.0、遊離塩素濃度を0.1ppm〜0.3ppmにするためにウイルス除去膜の孔特性、膜面積、処理装置の大きさを定める。得られた処理水の流れる回路には赤錆は発生せず、皮膚への刺激性の少ないまた塩類の少ない水となる。 An example of a low chlorination treatment apparatus is shown in FIG. Encapsulate a reducing food appendage in a solid state with a virus removal membrane. A container containing the drug is covered with a composite membrane composed of a virus removal membrane and a support, and is further brought into close contact with a container for hole diffusion / filtration covered with another composite membrane. With this device, food additives are dissolved and diffused into tap water by pore diffusion filtration. Adopt sodium ascorbate as a food additive. In order to set the pH of tap water to 7.5 to 8.0 and the free chlorine concentration to 0.1 ppm to 0.3 ppm, the pore characteristics of the virus removal membrane, the membrane area, and the size of the treatment apparatus are determined. Red rust does not occur in the circuit in which the treated water flows, and the water becomes less irritating to the skin and less salty.
超軟水化処理装置の例を図3に示す。該装置は造核剤を注入する部分、沈殿槽部分とイオン交換・微粒子除去部分の3部分で構成される。造核剤は平均孔径13nmの無定形の水酸化第2鉄コロイド粒子の水溶液でPH=2.7、鉄換算濃度で5000ppmである。造核剤の添加濃度を鉄換算で0.1ppmになるよう低塩素化水に注入する。注入後の水溶液のPHは6.8〜7.2になる。沈殿槽の大きさは水の平均滞在期間が30分以上になるように1リットル以上10リットル以下の大きさに設計する。具体的な設置個所によって空間的制限を考慮して決定される。イオン交換・微粒子除去部分はイオン交換再生セルロース不織布(イオン交換容量0.2ミリ当量/g)100gを5層の袋状にし、水は封筒内部より外部へ向ってろ過する。 An example of an ultra-soft water treatment apparatus is shown in FIG. The apparatus is composed of three parts: a part for injecting a nucleating agent, a precipitation tank part, and an ion exchange / particulate removal part. The nucleating agent is an aqueous solution of amorphous ferric hydroxide colloidal particles having an average pore diameter of 13 nm, PH = 2.7, and the iron equivalent concentration is 5000 ppm. Inject into low chlorinated water so that the concentration of the nucleating agent is 0.1 ppm in terms of iron. The pH of the aqueous solution after the injection is 6.8 to 7.2. The size of the settling tank is designed to be not less than 1 liter and not more than 10 liters so that the average stay period of water is 30 minutes or more. It is determined in consideration of space restrictions depending on the specific installation location. In the ion exchange / fine particle removal portion, 100 g of ion exchange regenerated cellulose nonwoven fabric (ion exchange capacity 0.2 meq / g) is formed into a five-layer bag shape, and water is filtered from the inside of the envelope to the outside.
飲料水の安全性をより高めるためにウイルス除去膜による濾過工程を加える。ウイルス除去膜として平均孔径が20nm、膜厚80μmの再生セルロース製平膜を有効濾過面積0.1m2で膜間差圧2気圧で運転される。該平膜の孔径の小さい表面を加圧側にする。供給される飲料水は1分間当り1リットルである。In order to further improve the safety of drinking water, a filtration process using a virus removal membrane is added. As a virus removal membrane, a regenerated cellulose flat membrane having an average pore size of 20 nm and a thickness of 80 μm is operated with an effective filtration area of 0.1 m 2 and a transmembrane pressure of 2 atm. The surface of the flat membrane having a small pore diameter is set to the pressure side. The drinking water supplied is 1 liter per minute.
水道水として供給された水の性質はPH=6.4、鉄イオン濃度1.3ppm、遊離塩素濃度1.0ppm、カルシウム濃度12ppmであった。この水を用いて(1)アスコルビン酸ナトリウム濃度を0.05ppmの濃度になるように下記のウイルス除去膜を通して孔拡散・濾過法で滴下するとPH7.5、鉄イオン濃度=0ppm、遊離塩素=0.3ppm、カルシウム濃度11ppmとなった。ウイルス除去膜:平均孔径80nm,膜厚75μmの再生セルロース多層構造膜に重ねて平均孔径25nm、膜厚65μmの再生セルロース多層構造膜を設置した。この多段多層構造を封筒状に成型し、その内部にアスコルビン酸ナトリウム5gを封入した。 The properties of the water supplied as tap water were PH = 6.4, iron ion concentration 1.3 ppm, free chlorine concentration 1.0 ppm, and calcium concentration 12 ppm. When this water is used and (1) the sodium ascorbate concentration is dropped by the pore diffusion / filtration method through the following virus removal membrane to a concentration of 0.05 ppm, pH 7.5, iron ion concentration = 0 ppm, free chlorine = 0 0.3 ppm and calcium concentration 11 ppm. Virus removal membrane: A regenerated cellulose multilayer structure film having an average pore diameter of 25 nm and a film thickness of 65 μm was placed on the regenerated cellulose multilayer structure film having an average pore diameter of 80 nm and a film thickness of 75 μm. This multi-stage multilayer structure was molded into an envelope shape, and 5 g of sodium ascorbate was sealed inside.
上記の方法で得られた低塩素化処理後の水を濾過した。用いた膜は平均孔径18nm、膜厚80μmの再生セルロース膜をロール間にはさみ圧縮処理して作製した。処理後の膜の平均孔径は15nmで膜厚を72μmとなった。この膜について平均孔径20nmの水酸化第二鉄コロイド粒子(株式会社セパシグマ社製FCP20)を用いた対数除去係数は3以上であった。この膜を用いて孔径のより小さい表面から圧力2気圧を負荷して濾過した。濾液として得られた水はPH=7.5、鉄イオン濃度0ppm、遊離塩素=0.3ppmカルシウム濃度9ppmであった。この水は飲料水として最適な安全性を保証する水である。 The water after the low chlorination treatment obtained by the above method was filtered. The membrane used was produced by compressing a regenerated cellulose membrane having an average pore diameter of 18 nm and a thickness of 80 μm between rolls. The average pore diameter of the treated membrane was 15 nm and the thickness was 72 μm. For this membrane, the logarithmic removal coefficient using ferric hydroxide colloid particles having an average pore diameter of 20 nm (FCP20 manufactured by SepaSigma Co., Ltd.) was 3 or more. Using this membrane, filtration was performed by applying a pressure of 2 atm from a surface having a smaller pore diameter. Water obtained as a filtrate had a pH of 7.5, an iron ion concentration of 0 ppm, and a free chlorine of 0.3 ppm and a calcium concentration of 9 ppm. This water is water that guarantees optimum safety as drinking water.
低塩素化処理後の水に対して下記条件での超軟水化処理を加えた。超軟水化処理:平均孔径13nmの無定形水酸化第二鉄コロイド溶液(株式会社セパシグマ社製造核剤、鉄換算濃度5000ppm)を処理用水の体積に対して1万分の1の体積で添加した。添加後の水のPHは7.0となり30分間放置するとわずかに沈殿が生じる。上清液を陽イオン交換容量0.1ミリ当量/gの再生セルロース不織布を5層の袋状物に成型し、その内側を負荷圧力2気圧で通液した。濾液中のカルシウム濃度は4ppmに低下し、処理水中の陽イオン濃度が低下した。また溶解したシリカの濃度は0.1ppm以下となった。 Ultra-soft water treatment under the following conditions was added to the water after low chlorination treatment. Ultra-softening treatment: Amorphous ferric hydroxide colloidal solution having an average pore size of 13 nm (SepaSigma Co., Ltd., nucleating agent, iron equivalent concentration 5000 ppm) was added at a volume of 1 / 10,000 with respect to the volume of treatment water. The pH of the water after addition becomes 7.0, and slight precipitation occurs when left for 30 minutes. The regenerated cellulose nonwoven fabric with a cation exchange capacity of 0.1 milliequivalent / g was molded into a 5-layer bag-like material, and the inside thereof was passed at a load pressure of 2 atm. The calcium concentration in the filtrate decreased to 4 ppm, and the cation concentration in the treated water decreased. The concentration of dissolved silica was 0.1 ppm or less.
本技術は戸建て住宅での居住者の水に対する要求、および給水側の管や給湯機の維持管理からの水の要求を満足する水質を持つ水を箇便に供給することが可能となる。この技術は病院、工場、学校など大型の給水設備を持つ建物にも利用される。 This technology makes it possible to supply water with water quality that satisfies the demands of residents in detached houses and the water requirements from the maintenance of pipes and water heaters on the water supply side. This technology is also used in buildings with large water supply facilities such as hospitals, factories, and schools.
MB:メーターボックス F:ウイルス除去用膜 B:給湯機
1;給湯管
2;水の流れ方向
3;超軟水処理後の水の流れ方向
4;凝集沈殿槽
5;イオン交換部6を装着するための固定枠
6;イオン交換不織布を積層したイオン交換部
7;造核剤注入部
8;コック
9;沈殿物回収ドレイン
10;パッキング剤
11;イオン交換不織布
12;イオン交換部6をパッキン剤へ押し付けるバネ
13;造核剤
14;給水管への注入管
15;給水管内の流路をせまくし、かつ注入管の出入に可能するゴム材
21;孔拡散・濾過モジュールの薬剤を充填した容器
22;空気抜き孔
23;バルブ
24;ウイルス除去膜で封筒状の成型物
25;還元性植物添加剤(固体状)
26;孔拡散・濾過用膜
27;支持体
28;パッキング剤
29;給水管へ連結する容器で支持体27と孔拡散・濾過用膜26を付着するMB: Meter box F: Virus removal membrane B: Water heater 1; Hot water pipe 2;
26; pore diffusion / filtration membrane 27;
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JPS62227489A (en) * | 1986-03-31 | 1987-10-06 | Sekisui Chem Co Ltd | Water treatment appliance |
JPH06226259A (en) * | 1993-02-04 | 1994-08-16 | Takenori Hayakawa | Water feeding system and water feeding device used in same |
JPH09151503A (en) * | 1995-11-30 | 1997-06-10 | Toshiba Corp | Water purifying system |
JP3951227B2 (en) * | 2002-06-12 | 2007-08-01 | 株式会社安川電機 | Water purification system |
JP5136735B2 (en) * | 2005-07-15 | 2013-02-06 | 征一 真鍋 | Method for removing toxic substances in exudate from final disposal site for stable industrial waste |
CZ2005700A3 (en) * | 2005-11-10 | 2007-03-07 | Elmarco, S. R. O. | Filter for removing physical or biological contaminants |
JP5339033B2 (en) * | 2008-05-14 | 2013-11-13 | 真鍋 征一 | A multilayer structure film having different fine particle capturing performance on the front and back surfaces and a manufacturing method thereof. |
JP5486170B2 (en) * | 2008-07-16 | 2014-05-07 | オルガノ株式会社 | Domestic water supply system with hot water storage system |
JP2010247057A (en) * | 2009-04-15 | 2010-11-04 | Kurosaki:Kk | Water purification method combining fine particle-making method and membrane separation method |
-
2010
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