JPS6028892A - Water making process - Google Patents

Water making process

Info

Publication number
JPS6028892A
JPS6028892A JP13909083A JP13909083A JPS6028892A JP S6028892 A JPS6028892 A JP S6028892A JP 13909083 A JP13909083 A JP 13909083A JP 13909083 A JP13909083 A JP 13909083A JP S6028892 A JPS6028892 A JP S6028892A
Authority
JP
Japan
Prior art keywords
raw water
humic
water
humus
precursor
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
JP13909083A
Other languages
Japanese (ja)
Inventor
Mamoru Uchimizu
内水 護
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP13909083A priority Critical patent/JPS6028892A/en
Publication of JPS6028892A publication Critical patent/JPS6028892A/en
Pending legal-status Critical Current

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  • Water Treatment By Sorption (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PURPOSE:To obtain water having approximately equal quality to natural mineral water by passing raw water through alternately heaped layers or a mixture consisting of humic substance and a large amt. of activated silicate and allowing org. components to react with inorg. components. CONSTITUTION:Raw water is passed through alternately heaped layers or a mixture consisting of humic substance consisting essentially of humus contg. precursor of humus or consisting essentially of humic precursor contg. humus, and inorg. component contg. a large amt. of activated silicate e.g. volcanic ash consisting of andesite or rhyolite, and fine powder of vitreous volcanic product such as pumice, etc. Thus, several polycondensation reaction or similar reactions including combination and polymerization between organic components in the raw water and phenol group exposing compds. as humic precursor in the humic substance, oxydase such as phenol oxydase as catalyst, and quinones as oxidized product of phenols, are caused.

Description

【発明の詳細な説明】 この発明は河川、湖沼などの原水の遣水方法、更に詳し
くいうと、原水中に含まれる有機・無機成分を腐植化反
応を介して除去する造水方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for supplying raw water from rivers, lakes, etc., and more specifically, to a method for producing fresh water in which organic and inorganic components contained in raw water are removed through a humication reaction.

従来より、原水を砂濾過して原水中の懸濁物質を除去し
た後、更に活性炭処理を施し°ζ原水中の有機成分を取
り除き、そして塩素滅菌をする遣水方法が広(行われζ
いるが、この方法においては、活性炭の使用が経済的に
高価につくとか、塩素殺菌に伴い造水後の水に苦みが加
えられるなどの欠点を有していた。
Traditionally, raw water has been widely used to sand filter raw water to remove suspended solids, then undergo activated carbon treatment to remove organic components from the raw water, and then chlorine sterilization.
However, this method has disadvantages, such as the use of activated carbon being economically expensive and the chlorine sterilization imparting a bitter taste to the water produced.

この発明は上記事情に鑑みなされたものであって、自然
の造水プロセスに近似したプロセスにより、原水を経済
的にしかも苦みなく造水する造水方法を提供することを
目的としたものであり、その特徴とするところは、原水
を腐植物と活性化した珪酸分を多量に含む物質の互層又
は混合物に透過させることにより、前記腐植物、活性化
した珪酸分を多量に含む物質そして原水中の溶解性成分
とによる腐植化反応を惹起し、原水中の有機並びに無機
成分の除去及び滅菌を行って、天然のミネラルウォータ
ーに近い水を造水するところにある。
This invention was made in view of the above circumstances, and aims to provide a method for producing water economically and without bitterness from raw water using a process similar to the natural water production process. The feature is that by passing the raw water through an alternating layer or mixture of humic plants and a substance containing a large amount of activated silicic acid, the humic plant, the substance containing a large amount of activated silicic acid, and the raw water are separated. The process involves inducing a humic reaction with the soluble components of raw water, removing organic and inorganic components from the raw water, and sterilizing it to produce water that is similar to natural mineral water.

ここで、腐植物とは腐植に腐植前駆物質が混っているも
の若しくは腐植前駆物質に腐植が混っているものをいう
、腐植前駆物質とは、フェノール化合物、及びフェノー
ルオキシダーゼ等の酸化酵素、又はフェノール化合物の
酸化物であるキノン類、並びに有機酸、多m類、アミノ
酸等の混合物及びそれらの一部重縮合反応物を含むもの
である。
Here, humus refers to humus mixed with humus precursors, or humus precursors mixed with humus, and humus precursors include phenolic compounds and oxidizing enzymes such as phenol oxidase, Alternatively, it contains quinones which are oxides of phenolic compounds, mixtures of organic acids, polyesters, amino acids, etc., and some polycondensation products thereof.

又、前記活性化された珪酸分を多量に含む物質としては
、安山岩、流紋岩質の火山灰や軽石等の火山ガラスの微
粉、粘土鉱物、グリーンタフ(greentaff)等
に起因するゼオライト(zeolite )鉱物を主体
とした岩石の微わ)、微粉状の珪藻上等が挙げられる。
Further, the substances containing a large amount of activated silicic acid include fine powder of volcanic glass such as andesite, rhyolitic volcanic ash and pumice, clay minerals, zeolite derived from green taff, etc. Examples include rocks (based on minerals) and finely powdered diatoms.

これらの物質中には、多量の活性化された珪酸分を含む
と共に、鉄等の金属を含んでいるために、尚一層有効で
ある。又、人工物である活性珪酸に鉄等の金属を、前記
天然物に含まれるのとほぼ同じ割合で混合した物であっ
てもよい。
These substances are even more effective because they contain a large amount of activated silicic acid and metals such as iron. Alternatively, it may be a mixture of active silicic acid, which is an artificial product, and a metal such as iron in approximately the same proportion as that contained in the natural product.

この場合において鉄等の金属を混合しなくても、造水作
用は果たせるが、金属を混合した方がより天然のミネラ
ルウメ−ターに近い水を造水することができる。
In this case, the water production effect can be achieved without mixing metals such as iron, but water that is closer to natural mineral content can be produced by mixing metals.

前記腐植物と活性化された珪酸分を多量に含む物質との
互層中若しくは混合物中におりる配合比率は、腐植物1
0%以上90%以下が好ましく、腐植物の配合比率が低
い程造水のための活性化された珪酸分を多量に含む物質
の交換頻度が少なくなる。逆に、腐植物の配合比率が高
い程造水のための活性化された珪酸分を多量に含む物質
の交換頻度が多くなる一方原水中の溶解成分の除去機能
が向上する。したがって原水の種麹1により適宜配合比
率を変更することが望ましい。
The blending ratio of the humic plant and the substance containing a large amount of activated silicic acid in the alternating layers or mixture is as follows: humic plant 1
It is preferably 0% or more and 90% or less, and the lower the blending ratio of humic plants, the less frequently the substance containing a large amount of activated silicic acid for water generation must be replaced. Conversely, the higher the blending ratio of humic plants, the more frequently the substance containing a large amount of activated silicic acid for water generation will be replaced, and the more the removal function of dissolved components in raw water will improve. Therefore, it is desirable to change the blending ratio appropriately depending on the seed koji 1 in the raw water.

このようにして適当な配合比率で互層又は混合された腐
植物と活性化された珪酸分を多量に含む物質に原水を透
過させると、腐植物中の腐植前駆物質としてのフェノー
ル露出基のある化合物及び触媒としてのフェノールオキ
シダーゼ等の酸化酵素又はフェノール化合物の酸化物で
あるキノン類、並びにアミノ酸、多糖頬等と、投下原水
中に含まれる有機成分とが結合から重合に至るまでの広
義の重縮合反応を起こす。この反応に更に活性化された
珪酸分を多量に含む物質が参加すると腐植化のための重
縮合反応が行われる。この重縮合反応は反応系に存在す
る物質を選択的でなく一括して腐植化のための重縮合に
取り組む。このため原水中に含まれる塩素、窒素、リン
等の無機成分も上記重縮合反応の進行と共に、効率よく
取り除かれる。
When raw water is passed through a material containing a large amount of activated silicic acid and a humic plant that is alternately layered or mixed at an appropriate blending ratio in this way, compounds with exposed phenol groups as humic precursors in the humic plant are absorbed. and oxidizing enzymes such as phenol oxidase as a catalyst, or quinones which are oxides of phenolic compounds, as well as amino acids, polysaccharides, etc., and organic components contained in the raw water to be thrown into the raw water. cause a reaction. When a substance containing a large amount of activated silicic acid further participates in this reaction, a polycondensation reaction for humification takes place. This polycondensation reaction tackles the polycondensation of the substances present in the reaction system for humification, not selectively but all at once. Therefore, inorganic components such as chlorine, nitrogen, and phosphorus contained in the raw water are also efficiently removed as the polycondensation reaction progresses.

又、前記腐植前駆物質並びに腐植存在下における腐植化
のための重縮合反応においては、大腸菌等有害菌に対す
る滅菌効果も作用するため、腐植物の質並びに量が最適
である場合には、従来法のように塩素滅菌を行う必要が
なくなる。
In addition, in the polycondensation reaction for humification in the presence of the humic precursor and humus, the sterilization effect against harmful bacteria such as Escherichia coli also acts, so if the quality and quantity of humus are optimal, conventional methods can be used. There is no need to perform chlorine sterilization as in

尚、腐植物と活性化した珪酸分を多量に含む物質の互層
又は混合物と原水との接触時間は、該原水の種類によっ
て異なるが、腐植化のための重縮合反応を急速に進行さ
せるには原理的には数分、実用的には30分以上が好ま
しい。
The contact time between raw water and an alternating layer or mixture of humic plants and a substance containing a large amount of activated silicic acid content varies depending on the type of raw water, but in order to rapidly advance the polycondensation reaction for humification, In principle, it is preferably several minutes, but in practice, it is preferably 30 minutes or more.

このように腐植化が急速に進行すると、上記反応及び作
用により原水中の有機並びに無機成分が効率良く取り除
かれると共に滅菌作用も働き造水が完成される。腐植化
がかなり進行し遣水機能が低下しだした時点で、形成さ
れた腐植を取り出して活性化した珪酸分を多量に含む物
質を入れると再び遣水機能が向上する。取り出した腐植
は、例えば重縮合剤、良好な腐植土などとして他方面に
有効利用することができる。
When humification progresses rapidly in this way, the organic and inorganic components in the raw water are efficiently removed by the above reactions and actions, and the sterilization action also works to complete water production. When humus formation has progressed considerably and the water distribution function begins to decline, the water distribution function will be improved again by removing the formed humus and adding a substance containing a large amount of activated silicic acid. The extracted humus can be effectively used as a polycondensation agent, a good humus soil, etc.

又、海水を原水とした場合にこの発明方法を適用すると
、上記腐植化反応に伴う海水よりの脱塩効果が大となる
ので海水の処理方法とし゛ζ充分に使用し得る。
Furthermore, when the method of the present invention is applied to seawater as raw water, the desalination effect from the seawater accompanying the humication reaction becomes greater, so that it can be fully used as a method for treating seawater.

以上の説明からも明らかなように、この発明の造水方法
によると、腐植化反応という天然の地下水が形成される
のと同様の反応を惹起して原水を処理することに加えて
、活性化した珪酸分を多量に含む物質中に含有される無
機塩類が適度に原水中に溶り込むので、自然界で形成さ
れるミネラルウォーターに非常に近い水が形成される。
As is clear from the above explanation, according to the water production method of the present invention, in addition to treating raw water by inducing a humication reaction, which is similar to the formation of natural groundwater, Since the inorganic salts contained in the substance containing a large amount of silicic acid dissolve into the raw water in an appropriate amount, water that is very similar to mineral water formed in nature is formed.

又、腐植物の質並びに量が最適である場合には大きな滅
菌効果も得られるので、塩素滅菌の必要がなくなり苦み
のない良質の水を形成することができ、非常に有用性に
富んだものとなる。
In addition, if the quality and quantity of humus are optimal, a great sterilization effect can be obtained, eliminating the need for chlorine sterilization and producing high-quality water without bitterness, making it extremely useful. becomes.

次にこの発明方法の実施例について説明する。Next, an example of the method of this invention will be described.

原水・−B OD濃度30〜50ppm a活性化した
珪酸分を多量に含む物質−ゼオライドと珪藻土とのl:
1混合物。
Raw water - B OD concentration 30-50 ppm a Substance containing a large amount of activated silicic acid - Zeolide and diatomaceous earth l:
1 mixture.

上記活性化した珪酸分を多量に含む物質と腐植物の1:
2混合物に、該混合物100gに対して上記原水を11
の割合で透過させた。この時の両者の接触時間は10分
であった。
1 of the above-mentioned activated silicic acid-rich substances and humic plants:
2 mixture, add 11 of the above raw water per 100g of the mixture.
It was transmitted at a rate of . The contact time between the two at this time was 10 minutes.

コノ結果BOD濃度3〜4 ppmの水が得られた。As a result, water with a BOD concentration of 3 to 4 ppm was obtained.

大腸菌は検出されなかった。No E. coli was detected.

特許出願人 内 水 護 代理人 弁理士渡辺三彦Patent applicant Mamoru Naimizu Agent: Patent attorney Mihiko Watanabe

Claims (1)

【特許請求の範囲】[Claims] t m植物と活性化した珪酸分を多量に含む物質との互
層若しくは混合物に原水を透過させることにより、原水
中の有機成分及び無機成分をこれら腐植物と活性化した
珪酸分を多量に含む物質と反応させることによって除去
することを特徴とする造水方法。
By passing the raw water through an alternating layer or mixture of plants and a substance containing a large amount of activated silicic acid, organic and inorganic components in the raw water are converted to humic plants and a substance containing a large amount of activated silicic acid. A water production method characterized by removing water by reacting with.
JP13909083A 1983-07-28 1983-07-28 Water making process Pending JPS6028892A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13909083A JPS6028892A (en) 1983-07-28 1983-07-28 Water making process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13909083A JPS6028892A (en) 1983-07-28 1983-07-28 Water making process

Publications (1)

Publication Number Publication Date
JPS6028892A true JPS6028892A (en) 1985-02-14

Family

ID=15237252

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13909083A Pending JPS6028892A (en) 1983-07-28 1983-07-28 Water making process

Country Status (1)

Country Link
JP (1) JPS6028892A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0416278A (en) * 1990-05-10 1992-01-21 Tomohiko Morikawa Water making material and method therefor, and water maker
EP0763502A2 (en) * 1995-09-09 1997-03-19 Bakelite AG Water and sludge treatment with humic matter
CN106365310A (en) * 2016-10-21 2017-02-01 大连理工大学 Method for promoting biological reduction of nitrobenzene by synergy of clay mineral and humic acid

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0416278A (en) * 1990-05-10 1992-01-21 Tomohiko Morikawa Water making material and method therefor, and water maker
EP0763502A2 (en) * 1995-09-09 1997-03-19 Bakelite AG Water and sludge treatment with humic matter
EP0763502A3 (en) * 1995-09-09 1998-04-22 Bakelite AG Water and sludge treatment with humic matter
CN106365310A (en) * 2016-10-21 2017-02-01 大连理工大学 Method for promoting biological reduction of nitrobenzene by synergy of clay mineral and humic acid
CN106365310B (en) * 2016-10-21 2019-04-23 大连理工大学 A kind of method that clay mineral cooperates with promotion biological reducing nitrobenzene with humic acid

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