KR20000072335A - Purification of Pool Water by Calm Soil - Google Patents

Abstract

PURPOSE: A purification system for swimming pool water using native soil is provided, which is characterized in that the soil concentrated with poly-phenol aromatic compounds can disinfect colon bacilli and pathogenic bacteria without chlorination and cultivate helpful bacteria to product metabolic products. CONSTITUTION: A purification system for swimming pool water using native soil proceeds the following steps: a first step to flow in a reactor tower(4) for water polluted at a swimming pool(2) by using a pump(7); a second step to react activated silicates with organic materials of the swimming pool water in the reactor tower(4); and a third step to filtrate(3) the treated water after injecting coagulants(30% or less of conventional quantities). The soil concentrated with poly-phenol aromatic compounds can disinfect colon bacilli and pathogenic bacteria without chlorination and NaOH and cultivate helpful bacteria to product metabolic products with poly-phenol aromatic specific characters.

Description

Method of Purifying Pool Water by Calm Soil {.}

2. Field of invention

As swimming pools are bathed by a large number of swimmers, various organic substances are dissolved in the swimming pool and various harmful microorganisms live, so it is necessary to purify organic substances regularly and sterilize harmful microorganisms. However, the water purification method is not suitable and there is no sure method for sterilization of harmful microorganisms. In recent years, problems of occupational diseases of swimming pool workers are raised. The present invention seeks to solve this problem.

3. Problems of the prior art

(1) The water is purified by passing the pool water through a sand and activated carbon filter to purify the water. In order to aggregate and remove various organic substances, a large amount of flocculant with low pH is used.

(2) Due to the high amount of flocculant used, the pH is lowered, and a neutralizing agent such as caustic soda is used to neutralize it.

(3) To sterilize harmful bacteria, chlorine disinfectant is used.

(4) By injecting such toxic chemicals into the swimming pool, the eyes will not be able to swim without swimming.

(5) The swimmer complains of tingling skin and the skin becomes rough.

(6) The hair color turns yellow.

(7) The pool smells of chemicals.

4. Technical principle of the invention for solving the conventional problems

(1) Corrosion of organic matter in soil with corrosive substances

Modern science teaches that organic matter is decomposed by microorganisms and turned into gas.

But 衆生 必死 必死 歸 土 ( 記)

The living must die and the dead return to the soil.

"You are dirt and return to dirt" (Genesis)

Eastern thought has been that, as mentioned above, organic matter dies and returns to the soil.

1) in soil

A) Corrosion inherent: Humic acid, flavore, humin

B) Powerful degradation products of organic fluids and recombination products of microorganisms, matters of light nature, carbohydrates and their derivatives, 臘, 脂, 脂質, tannin 質, lignin and their degradable products, in which fresh animal and plant fluids are present. Dosing is decomposition and resynthesis by microorganisms to form new corrosion.

MM Konono and Ms. MM Konono and Ms. described the process of organic material degeneration in Mother Nature by synthesizing vast data by combining the research results of researchers in each field as follows.

① Corrosion of plant fluids results in inorganic constituents of CO ₂ , H ₂ , O, NH ₃ and other products. (Double CO _{2 is} gasified and scattered in the atmosphere, while H ₂ O, It looks like water that is scattered in the atmosphere or shiny and soaks into rivers or soil.)

(2) All components of plant tissue will be a source of structural units as follows.

Degradation products (lignin, tannins and other similar compounds are phenols)

Metabolites (Phenolol compounds; these are metabolites produced when microorganisms use carbohydrates)

-Degradation products and recomposites (amino and pepuccith, which are produced by the breakdown of proteins and metabolites of microorganisms)

③ An important factor in the formation of corrosive substances is the condensation of structural units. This condensation is caused by the oxidation of phenol from semiquinone to quinone by a phenol oxidase-type enzyme, and also by the interaction of quinone with amino or amino peptides.

④ The decisive factor in the formation of corrosive substances is the chemical process or With regard to the corrosive decay of each process, the individual processes of this process proceed simultaneously in close interrelationship.

This The formula is as follows.

圖 1 腐植 化 過程 圖 式

2) product of the corrosive process

A) Corrosion and Chirate Structure

In this process, the product of decomposition of organic fluid, chilate fungus, metabolite of Bacteria 群, and chilate constituent, which is a resynthesis product, are produced. These groups include many members, especially landlords. Compounds with aromatic properties of polyphenols These substances form Al-Fe, Mn- or other elements from rocks or minerals by forming a compound or chelate with them as if they were eyeballs. . In the chirate, 分子 根基 is combined with the 中心 and some 配 位 位置. In the chelate, the metal Ion has two adjacent bases and combines with a chelatable organic material that can bond with the metal.

Various chirate structures are known which differ in form of bonding with metals.

The key rate is usually I have ion base and this Water ions in ions are dissolved by the metal ion.

In the grape sol-like form, the compound or compound of aluminum and aluminum plays an active role. Many organic compounds with individual essences, particularly dicalbon, uron, earth, color, amino, and amino acids, have bonds that form a special complex.

In recent years, researchers have been interested in the ability of polyphenols, the degradation products of lignin and tannin products in soil litter or forests (Bloom friled 1953,1954, 1957; Lossaint 1954, 1956, 1957, 1958; Coulson, Davis, Lewis (1960).

Based on the same principle, Deuel (1959: Hers, Bach, Deuel (1960)) reported that catechins-pyrogal, 沒 食 子 酸, and pyrocatechins-decomposed safe compounds such as silicates and amino silicates, To form a complex.

The high content of chelates in humic acid or humic acid or erosion-deficient organic fluids in the corium composition of the grape sol-like or colour-colored soils is associated with the formation of chelate-like compounds in these soils. Promote.

Fe, Al (probably Si) are the densities under the influence of the above-mentioned organic matter from the state of the first mineral or hydroxide. It is transformed into the state of the non-mechanical compound, which is a stable matter, and moves in the soil cross-section in the form of soil, and reaches the unsustainable stability of the compound, and forms corrosion corrosion therein. . It was named 分子 浸透.

B) Organics and Soil Structure

AF and Churin paid particular attention to the importance of high-particle-containing colloids in the formation of indices (1946). He divided the colloids into two groups by the splitting method. The first feature is the loose bond form of the corrosive material, which incorporates the substitute calcium and the crystals of the clay mineral. The second feature is the R ₂ O _3, which combines the corrosive material with the inorganic part of the soil. AF Chuurin considered that the first group of colloids was the most important in terms of agricultural structure and soil participation in substitution.

The complex Mechanism of the soil formation process became apparent (NA Kachinsky 1947, 1949, 1960; IN Anchipov, Karataef et al. 1948: DG Barenski, 1945: PV, Versinin, 1953, 1958). The overall effects are shown: the mechanical and mineral composition of the soil, the nature of the corrosion, the nature of the interactions with the organic and inorganic parts of the soil, the water conditions, and the mechanical action on the soil.

Differences in the composition of deposits in various types of soil are evident and depend on the nature of the corrosion and the nature of the inorganic parts of the soil. I.N Anchipov, Karataev, V.V Kerermann, D, Han (1948)

① Chernozom: Microforms are formed by calcified lime, and these microforms form large forms in association with micel bonds between organic matter and montmorillonite.

② grape solstice and 赤色 결합: the combination of the three-tiered compound (mainly Fe ₂ O ₃ ) and Furbo 을 has the basic 膠結 性.

③ gray (and brown) 森 林 土: shows the intermediate form. In other words, when humic acid and lime are present, they are present in the soil in the form of a combination of huruboic acid and R ₂ O ₃ .

As VV Kerermann continued in the study, it became clear that organic compounds penetrated evenly when the compounds of furboic acid or furboic acid and tricyclic compounds play an important role in the removal of these compounds. It was. This state of joining is characteristic of 土色 土 or grape sol.

Kerman's results are in complete agreement with the MM-conono and group data, which characterize the nature of various soil-type corrosive substances. In the corrosive composition of grape sol-like or colour-free, there are a lot of fuboic acid and by-acid which are hardly coagulated as CaCl ₂ .

This fact not only explains the uniform penetration of corrosive substances into the inlets of these soils, but also provides the incidence to the inlets.

Many researchers have pointed out that inherent corrosive substances participate clearly in the regeneration of soils, and that many organic compounds with individual essences contained in the composition of microorganisms or in the metabolites of microorganisms play an important role. Doing.

Microscopic strains of fungi (Clado sporium, Penicillium, Tricoderma, and Stachybotris strains) have been clarified to envelop soil particles and aid in their flow. However, this phenomenon is short-lived and disappears along with the fungus. When the fungal hyphae changed to a stable product of corrosive action, the indentation continued to resist water for a long time (Kernvets and Cornier and 1938, 1942: Gersette 1940: Missuschin and Pushkinsky 1942). , 1945: martin 1945: Douns et al, 1955: Thornton et al. 1956)

Plants of Bacteria, especially those made by members of Pseudomonas, have a great effect on the composition of water-soluble properties (Gerszer 1943, McCalla, 1945: MARTN 1945: Peele 1940)

C) biologically active substances

It is certain that VITAMIN®, Ocusin® and antibiotic-active substances in the soil organic fractions are present in the soil organic fraction composition (NA Krashirnikov, 1952, 1958 / K Orcharov: 1953 / Yu Larcatin: 1953). / wh Chofeier: 1950 / Andus: 1949 / Schmidt: 1951 / Fshnich: 1955 / Locf fead: 1958)

① VITAMIN 類

B 6 B 1 2, Pantothene 葉 酸, Nicotine 코, Paraamino, Benzol 리, Riboflavin, Biotin 其他 VITAMIN 類 are recognized in the soil. The main producers of VITAMIN® in the soil are microbiota.

植物 VITAMIN's involvement in the enzymatic action and metabolism of humans was investigated by M. Kh Charayan (1956) or EL Latoville (1958). It is.

② 生長 促進 劑 Ouchin Shin 類

Hetero-orchicin (β-indole), a representative member of soil-o-kisin, is a product of many soil microorganisms, especially azotobacters, and het-o-okin-sin action on plants (Smari, 1948). Stimulates the growth of 器 管 and accelerates maturity of fruit.

③ 生物學 的 促進 劑 質

-Sibererin

It appeared in the genesis of FUSARIUM Moniliborme and was produced by Gibberella Fujihuroi.

Siberine promotes the growth or flowering of the plants of the larvae and affects the metabolism of both plants. It should be noted that their facilitation functions appear only at low concentrations.

-低分子 有機物 especially Zicalbon 酸

The Kohak, Nakkei, Hmal, and Sesame have the properties of biomaterials. These substances have good effects on seed germination at low concentrations, growth of root and ground organs, yield and quality of harvest.

④ Antibiotic

There are streptomycin, grobisporin, penicillin, oreomycin, teramicin 其他. Their way of expressing vitality does not alter the shape of the soil (Krasirnikov, 1959), the nature of corrosion (Petgel 1959), despite the relatively large antibiotic molecules in the plant (300-500 or more). It is important to note the fact that it does not interfere with the plant's entry into the plant (Krishilunkov 1958: Schelles Und Klocke 1956).

3) When the above theory is applied to wastewater treatment plant waste treatment plant

Since the wastewater treatment plant or the waste treatment plant is an artificial environment, even if there are no silicic acid salts or corrosive substances present in the natural environment, even if it is a trace amount, it cannot be a soil environment, and therefore, no deterioration of organic matter occurring in the soil environment where the corrosive substances exist.

However, I would like to write below the Mechanism that assumes an environment where corrosive substances or silicates exist in a wastewater treatment plant.

A) Removal of Organics and Ionics

The organic matter contained in waste water as mentioned above is decomposed by microorganisms in an environment that is corrosive materials present in the soil CO _2. Inorganicized with N ₂ , H ₂ O, etc., various microbial metabolites, decomposition products of organic matter, chelate products, recombination products, caking substances, etc. The organic substances contained in the wastewater are removed from the liquid phase and at the same time, they are combined and removed from the liquid phase in the form of various ionic substances, arrival compounds, internal compounds, and other organic-inorganic compounds contained in the wastewater.

B) Eliminate Odor

Odor molecules exist in water in ions. These chelating products of odor molecules Ions (eg NH _4, etc.) are captured as chelates and become compounds different from their original properties. Odor is removed in this process.

C) Sterilization of pathogenic microorganisms and bioactivity of symbiotic microorganisms

Various antibiotics produced during the corrosive process sterilize pathogenic microorganisms, and microbial groups that are not affected by the antibiotics are promoted by biologically active substances. As a result, the treatment efficiency is higher than the conventional method.

(2) Corrosion of organics in an artificial environment without corrosive substances

In anthropogenic environments such as wastewater treatment plants and waste treatment plants where no corrosives are present, organic substances are enzymatically degraded in the form of enzymatic decomposition. This is not a common occurrence in Mother Nature, but is a rare occurrence locally, such as the initial decay of an animal's dead body, and is common in anthropogenic environments. By the above reaction, no corrosive substances are produced and microbial metabolites (chelate products, growth promoters, antimicrobial substances, etc.) having various aromatic essences generated during the formation of corrosive substances are not produced. This is going to be thrilled.

Corrosion reactions of organic substances occurring in the great outdoors are very slow, taking 10 to 20 years in large areas. Even if the corrosive substances or silicates are present in the wastewater treatment plant or waste treatment plant, the corrosion reaction is terminated. In order to take a very large area and a lot of time, economic efficiency is low. To solve this problem, microbial metabolites with excellent activity and polyphenol aromatic qualities are found among the corrosive substances in nature and processed again to produce strong polycondensation reactions. By repeatedly injecting active silicates, which are more active than existing ones, at the point where organic matter is introduced, they try to speed up the corrosion reaction more than what is happening in Mother Nature.

** The theoretical background is as follows **

1) Duality of the organic process of metamorphosis

Degeneration of organic matter in nature is directed in two directions.

In other words, as indicated in the first paragraph, the metamorphosis into two completely different methods of low molecular weight and high molecular weight of organic matter is known. Among the degenerations of these organic matters, which one is more common, it can be said to be the direction of high molecular giantization. Degeneration to low molecular weight can be widely seen in the decay of organic matter in the form of 酵素 分解, but in a quantitative way. On the other hand, metamorphosis of macromolecules is a major problem occurring in the natural world. For example, it is the weight of organic compounds and minerals, which are connected to the soil, and the weights of stone systems such as rock, stone, soil, and grass. There are countless things like swamps and lakes.

The high molecular weight of organic matter in nature is associated with the formation of metabolites and organic compounds, including aerobic bacteria and common phenols and / or phenolic compounds produced in the common soil bacteria group. It is a reaction produced by reacting with. In addition, when a substance containing a large amount of activated fractions is administered to the reaction system, a corrosive reaction is known, but 巨大 分子 化, oniization is expanded.

... Basic Reaction 1 ...

Organic matters include microorganisms containing phenols and / or compounds containing phenolic compounds, which are rapidly bonded, deformed, collected, mixed, and weighed, macromolecular, and bulky. Productize.

... Basic Reaction 2 ...

If an appropriate amount of a substance containing a large amount of activated minutes for the reaction is added, a weighting reaction for corrosion occurs.

The above-mentioned compound having a phenolic compound has a general meaning of an organic substance having a phenolic compound, but an enzyme having a phenolic compound is particularly effective.

In addition, a substance containing a large amount of activated fraction refers to a highly stable substance having high activity such as pyrogenous glass having an anoxic acid and a flux composition.

The following only refers to basic reaction 1. If the substance containing a large amount of active substance in the same system is added or added, or if the raw water contains the same substance, for example, it is included in the clay mineral in the water and the compound in the water. All of the reactions in the 鑛物 性 增量 劑 occur in the state of basic reaction 2.

The difference between the basic reaction 1 and the basic reaction 2 is that in the case of the purpose of the removal of the non-ionic ionic substance, the chelate is more prominent in the antibacterial product. It is beneficial to squeeze a substance containing a large amount of minutes into an anti-system. And it does not mean that the chilate VII does not develop in the reaction product of the basic reaction 1, but only that the development of the chiret 레 is accompanied by more technical difficulties.

Influence of Organisms in the First Stage

低分子 化: 酵素 分解

有機物

高分子 化: Weighing, mixing, etc.

2) variety of microbial metabolic function

Microbial groups change metabolic functions in order to adapt sensitively to environmental changes.

In particular, when microorganism metabolites with aromatic polyphenols are concentrated in a high concentration of environmental substances into the "intestinal field", the microbial population that adapts to the "field of pollution" adapts its metabolic function to the "field of purification". Metabolites, i.e. compounds with polyphenolaromatic essences, are secreted and pathogens that do not adapt are killed. On the contrary, if contaminants with high concentrations are continuously introduced into the "cleaning place", the microbial population living in the "cleaning place" will adapt to the "cleaning place".

Therefore, in order to maintain the sewage treatment plant at all times, it is necessary to repeatedly input a highly concentrated material of microbial metabolites having an aromatic nature of polyphenol at the point of sewage treatment. When the concentration of substances with poly phenol aromatic nature is weak compared to the input organic matter or when the input is stopped, the "field of purification" is induced as the "field of pollution". (UCHIMIZU 1985)

3) Induction culture of microbial metabolic function

The phenolic metabolic function is expressed in soil anaerobic bacteria or soil aerobic bacteria and aerobic bacteria in an artificial environment, with or without free oxygen. It has already been said that it is indispensable to be placed in the presence of a phenol or / and a metabolite comprising a compound with a phenol exposure group. To this end, the addition of (outside the system (metabolites containing compounds with phenol and / or phenol exposure groups or substances containing the same metabolites <corrodes, etc.)), or the phenol-based metabolic function in nature is particularly enhanced It has already been written about the use of the bacteriological group, which is a related group with the soil-organic anaerobic bacterial group, as a spawn under certain conditions.

So how can you get a seed, a phenolic metabolite or a substance containing a phenolic metabolite? To do this, first of all, it is necessary to clarify the characteristics and characteristics of the substances that were their microorganisms.

<種 菌>

If only good spawns are available, it is feasible to induce metabolic functions of the soil microbial populations in the wastewater by phenol-based culture. However, in order to find a good seed, it requires considerable high sensitivity and proficiency. Therefore, it is not reasonable to induce and cultivate using seed.

The natural world is full of soil flora, and the soil flora inhabiting the soil generally expresses phenolic metabolism. Then, it is not easy to ask if it is good to inject the soil with high soil density into the wastewater. Then, what kind of soil soil group can we use as spawn?

To be used as a spawn, firstly, it is a group consisting of soil-based aerobic bacteria and aerobic anaerobic bacteria with current phenolic metabolic function that coexist with soil-based anaerobic bacteria group, and bacteria groups other than soil bacteria, especially Escherichia coli or rot bacteria. Back fungi must be completely suppressed or killed. As described for the history of soil bacteria, it is preferable that the bacterial group consisting of soil aerobic bacteria and aerobic anaerobic bacteria be promulgated with the soil-based anaerobic bacteria group for a long time for stable expression of phenolic metabolic function. As phenolic metabolites accumulate, bacteria other than soil bacteria living in the system, such as Escherichia coli or rot bacteria, should be suppressed or sterilized by the antibacterial action of phenolic metabolites.

Second, the physical properties of the environment itself of the population of bacteria that can be used as spawn should suggest the presence of phenolic compounds. For example, the chromaticity or phenol odor inherent in the phenolic compound, or at least sensory should be detected. This means that phenol-based metabolites need to accumulate at a certain concentration or higher in the system in order to completely inhibit or sterilize other fungi other than soil bacteria.

Third, the sludge-like material produced in the system should have a chirate structure. The sludge sludge material produced in the presence of phenolic metabolites has a chilate structure, and conversely, the sludge phase material having a chilate structure is produced, and thus the presence of phenolic metabolites can be confirmed.

As long as it has the first and third requirements mentioned above, it can be utilized as a spawn. Then where can you find the seed when you look realistically? For example, sewage sludge containing seeds is easily collected at a point where it is deposited in a pit made in a drainage channel such as a livestock wastewater, etc., and a state in which the sludge continuously flows over the sedimentation surface continues for a long period of years or decades. Is possible.

<Induction and culture substance>

The extraction of phenolic metabolites per se is possible experimentally but is not practical given quantitative and economic issues. On the other hand, substances containing phenolic metabolites are widely distributed in nature.

The most widely distributed substance containing phenolic metabolites is the soil itself. Soil is the end product of the reaction (corrosion reaction) caused by the action of phenolic metabolites on organic matter and silicates. The process material of the corrosion reaction is collectively referred to as corrosion precursors, corrosion precursors and mixtures of corrosion. Called corrosive, it is possible to say that good quality soil is the corrosive itself. However, silicates are generally physicochemically stable substances, and the ratios of phenolic metabolites, organic substances and silicates are not overwhelmingly increasing rates of corrosion reactions. As a result, the soil should generally be regarded as a mixture of humus and silicate.

Corrosion precursors are generic terms of process substances in which various organic substances are changed to corrosion by the action of phenolic metabolites and silicates as described above. In other words, corrosion precursors are substances derived from phenolic metabolites and silicates. It will contain. Therefore, the corrosive precursors, and moreover the corrosives, are those containing phenolic metabolites as described herein, but only corrosive precursors function as induction and culture materials for the soil flora.

In the corrosive reaction, silicate is involved, and the average composition of the earth's crust in which the soil flora originated is granite or nitrite silicate, and it is alkalite, which is unstable or activated under surface physicochemical conditions. In the presence of volcanic glass, it is assumed that the high-quality corrosive layer with high content of corrosive precursors is relatively widely distributed in the special terrain of the andesite volcanic zone. In addition, since corrosives may be produced by synthesis, it may be more rational to use corrosives than to use spawn when inducing cultivation of metabolic functions of soil bacterial groups to phenolic systems.

A) Cohesive condensation, macromolecularization, polymerization and polycondensation mechanisms of organics

① When microbial metabolite having polyphenol aromatic essence is added to organic matter, it coagulates, condenses, macromolecules and agglomerates. Soil soiling reaction) occurs to polycondensate. (1985.UCHIMIZU)

② Formation of Water Resistant Penetration Structure

It is clear that the original corrosives participate in the formation of water-resistant granules in the soil, and that many organic compounds with individual essences contained in the composition of the microorganisms or in the metabolites of the microorganisms are playing an important role. Numerous researchers have clarified that microscopic mycelium of fungi (cladosporium, Penicillium, TRICODERMA, etc.) has wrapped soil particles and prevented their flow. However, the phenomenon is short-lived and disappears with the disappearance of mold. Only when the fungus hyphae changed to a stable product of the corrosive action, the group continued to resist long-term water. (Kanibetsu and Korunierwa (1938, 1942; Kyrgyzère, 1940; Misouscin and Pushkinskaya, 1942, 1945; MARTIN 1945; Downs al, 1955; Thornton et al, 1956) In particular, the composition of the water-resistant structure produced by the memeber of Pesudomonas confers a great effect (Cirsaner, 1943; McCalla, 1945; MARRIN 1945; Peela 1940). It is contained in this viscous substance, due to amino acids (Rudakov 1953; Geoghegan et al, 1948; Rennie 1954; Metha, Streuli, Muller, Deull 1960; Greenland, LINDSLROM, Quirk 1961).

It is known from the work of F. YU Kyres (1940) that microbial composites have a high ability to form incidences. Soil standing wetting or subsequent drying of the turbidity of these compounds significantly increased the reusability of the standing and its water resistance was maintained for a long time, even in the case of optimum temperature and moisture for microbial activity. The same experiments were carried out on the grape sol, chernosome, and sirosome. At that time, the amount of the product of microbial origin was very small, about 0.139% (as carbon) of the soil weight.

We observed a similar phenomenon in experiments with newly produced humic acids. Even small applications of these materials (0.07 to 0.1% as carbon to soil weight) essentially increased the content of water resistant granules. This entrée retained resistance to spills over time. (Konono and 1951) Although microbial metabolites participate in the creation of water-resistant soil structures, it should be taken into account that most of these microorganisms are aerobic. (Cutres 1955, Samtes Beach 1955)

③ production of chelate products

Significant changes or degradation of organisms are caused by chelating products of living activities. These groups include many types of organic acid members, in particular land derivatives, derivatives of uron 酸, pigments of some kind, amino sugars, amines, and 其他. In the soil, these compounds are decomposition products of organic fluids, but are mainly metabolites or resynthesis products of scalp, mold, and many kinds of Bacteria. (I.N.Ancipov, Karataev and I.G Churva (1961), Schatz (1955), Schatz et al (1954), Scheffer, Uluich m, Hiester mann (1957a)

These materials form complexes or internal complexes (chelates) from Al or Fe, Mn, Cu and other elements by "contacting the eyeballs" from stone or metal by contact. The latter is highly mobile and actively participates not only in the early stages of soil formation, but also in later stages, and participates in the geochemistry of Fe, Al, 라, uranium, arsenic, zinc, serene, gelatin, Mn, gold and other elements. (S.M Manskaya (1956, 1958, 1959))

5. Preferred Embodiments of the Invention

When a part of the water contaminated by the swimmer in the swimming pool ② is introduced into the culture tank ④ by the pump ⑦ and stirred, the calm soil and active silicate filled in the reactor tower mounted on the culture tank ④ Contact will cause a soiling reaction. As a result, the organic material becomes a corrosive process material for the corrosiveness, and the first, which is a function of the calm soil, secretes a compound having a polyphenol aromatic nature such as the metabolic function inhabiting the calm soil of microorganisms. Second, it has excellent function of coagulating and condensing organic matters, and third, it has antibacterial activity against harmful microorganisms such as Escherichia coli and pathogens.

In this way, when the culture-induced microbial metabolism function is introduced into the swimming pool ②, the corrosion reaction occurred in the swimming pool ④ also occurs in the swimming pool ②, and the entire swimming pool is induced to the calm soil environment.

In this way, the organic substances in the water in the pool ② are condensed and condensed by the soilification reaction, so when the pump is sent to the filter ③ through the filter ⑥, the organic matter is easily removed and the water is clean. At the same time, antibiotics contained in calm soil and various antibiotics contained in secretions of microorganisms living in calm soil environment sterilize E. coli and pathogens.

On the other hand, the chelate compound contained in the calm soil traps various ionic substances contained in the water and these are also removed from the filter.

As a result, even without chlorine sterilization, E. coli and pathogens do not exist, and low pH or coagulant is not easily removed from the filter even if only a very small amount of water does not lower the pH of the water, thus eliminating the need for caustic soda for neutralization. do.

.

.

.

(1) Even without chlorine disinfection in the pool, E. coli and pathogens are absent.

(2) The amount of flocculant used can be minimized (less than 30% of the previous amount).

(3) It is not necessary to use caustic soda.

(4) The smell of chemicals in the pool disappears.

(5) By swimming, the skin does not worsen, but rather improves the skin.

(6) The environment of the pool becomes the atmosphere of a deep pool in the mountains.

Claims (2)

A method of minimizing the amount of flocculant used by agglomeration, condensation, and polycondensation of organic matter contained in swimming pool water by contacting a soothing soil enriched with a polyphenol aromatic substance with microbial metabolites. A method of sterilizing harmful bacteria such as Escherichia coli and pathogens in chlorine without chlorine disinfection by contacting water with concentrated soybean enriched with microbial metabolites having an aromatic nature of polyphenols.