KR100915958B1 - Eco-friendly active natural mineral water quality improvement composition and its manufacturing method - Google Patents

Eco-friendly active natural mineral water quality improvement composition and its manufacturing method Download PDF

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KR100915958B1
KR100915958B1 KR1020090051413A KR20090051413A KR100915958B1 KR 100915958 B1 KR100915958 B1 KR 100915958B1 KR 1020090051413 A KR1020090051413 A KR 1020090051413A KR 20090051413 A KR20090051413 A KR 20090051413A KR 100915958 B1 KR100915958 B1 KR 100915958B1
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water
water quality
weight
minerals
natural mineral
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KR1020090051413A
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Korean (ko)
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박기호
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주식회사 루미라이트
박기호
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/68Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds

Abstract

An eco-friendly active natural mineral water quality improver and a manufacturing method thereof are provided to improve water quality such as cloudiness by precipitating, dissolving, and decompose pollutants with natural minerals. An eco-friendly active natural mineral water quality improver includes clinoptilolite 60 ~ 80 weight%, rock-forming minerals 7 ~ 15 weight%, high CEC clay minerals 5 ~ 10 weight%, ash 5 ~ 10 weight%, and dolomite 2 ~ 6 weight%. The high CEC clay minerals is one or more selected from a group consisting of vermiculite, montmorillonite, and illite. THE high CEC clay minerals is the vermiculite, the illite or their mixture. The rock-forming minerals is one or more selected from a group consisting of rock-forming minerals muscovite and felspar.

Description

친환경 활성 천연광물 수질개선제 및 그 제조방법{Eco-friendly active natural mineral water quality improvement composition and its manufacturing method}Eco-friendly active natural mineral water quality improvement composition and its manufacturing method

본 발명은 저수지, 하천 및 자연 호소(湖沼) 등에 살포되어 녹조, 적조 및 각종 오탁물(汚濁物)로 오염된 수질을 개선하는 수질개선제 및 그 제조방법으로서, 본 발명의 수질개선제는 클리높틸로라이트(clinoptilolite), 조암광물, 점토광물, 화산재 및 돌로마이트 등의 천연광물이 혼합 구성되어, 오탁물을 응집, 침전시키는 동시에 분해시킴으로써 탁도를 비롯한 수질을 개선한다.The present invention is a water quality improving agent and a manufacturing method for improving the water quality, which is sprayed on reservoirs, rivers and natural appeals and contaminated with green algae, red tide and various pollutants, and the manufacturing method of the present invention, Natural minerals such as lite (clinoptilolite), coarse minerals, clay minerals, volcanic ash and dolomite are mixed to improve the water quality including turbidity by agglomerating, sedimenting and degrading soils.

천연광물을 주재로 하는 본 발명은 수생생물에 미치는 영향을 소화하면서도 별도의 대규모 처리설비 없이 간편한 살포만으로 수질을 개선할 수 있다.The present invention based on natural minerals can improve the water quality by simply spraying without extinguishing the impact on aquatic organisms without a large-scale treatment facility.

저수지, 하천 및 자연 호소의 오염 원인으로는 각종 점오염원 및 비점오염원으로부터의 오염물 유입, 수온상승 및 부영양화 등에 따른 녹조 및 담수적조의 발생, 홍수 및 건설공사 등에 의한 오탁물의 유입 등을 들 수 있다.The causes of contamination of reservoirs, rivers and natural appeals include the inflow of pollutants from various point sources and nonpoint sources, the occurrence of green algae and freshwater tides due to water temperature rise and eutrophication, and the inflow of contaminants due to flooding and construction work.

이러한 수질오염의 유형별 대처방안으로서, 각각 산업시설의 배출 오폐수 및 도시하천의 초기 강우유출 등으로 대표되는 점오염원 및 비점오염원에 대해서는 각종 하폐수처리시설을 들 수 있으며, 녹조 및 담수적조 등에 대해서는 오염수계에 대한 수처리제의 살포 등을 들 수 있다.As countermeasures for each type of water pollution, various kinds of sewage and wastewater treatment facilities are represented for point sources and nonpoint sources, which are represented by discharged wastewater from industrial facilities and initial rainfall runoff in urban streams, respectively. And spraying of a water treatment agent on the water.

저수지, 하천 및 자연 호소의 탁도를 비롯한 수질을 저하시킬 뿐 아니라 수변경관 및 수생생물의 서식환경을 훼손하는 녹조 및 담수적조의 원인으로는 수온상승과 부영양화를 들 수 있는데, 이 중 부영양화의 대표적인 원인은 점오염원 및 비점오염원으로부터 과다 유입된 유기물이나 영양염류라 할 수 있으므로, 이들의 처리시설인 하폐수처리시설 또한 녹조 및 담수적조 발생을 억제하는 역할을 수행한다 할 수 있다.Water temperature rise and eutrophication are the causes of green algae and desalination that not only degrade water quality, including turbidity of reservoirs, rivers, and natural lakes, but also damage the habitats of water-modifying pipes and aquatic organisms. Since it can be referred to as an organic substance or nutrient salts excessively introduced from point sources and nonpoint sources, their wastewater treatment facilities can also play a role of suppressing the occurrence of green algae and freshwater tides.

각종 생물학적, 화학적, 물리적 처리기법을 적용하여 오염된 물을 정화처리하는 하폐수처리시설은 고농도의 유기물은 물론 영양염류 또한 처리가 가능하지만, 이는 정해진 처리용량 내에서 특정 오염원으로부터 배출된 하폐수만을 처리하는 시설로서, 동일한 처리기법을 일반 하천이나 호소 등에 적용하는 것은 불가능하다.Sewage treatment facilities that purify contaminated water by applying various biological, chemical, and physical treatment techniques can treat nutrients as well as high concentrations of organic matter, but it treats only wastewater discharged from specific pollutants within a given treatment capacity. As a facility, it is impossible to apply the same treatment technique to a general river or an appeal.

이에, 하천이나 호소에 대한 직접 처리기법으로서 하천을 사행화(蛇行化)하거나 인공습지를 조성하는 등 자정작용을 극대화하는 방법이 적용되고 있으나, 사행천 또는 인공습지의 조성은 막대한 건설비가 소요될 뿐 아니라 유의한 효과를 얻기까지 장기간이 소요되는 문제점이 있다.Therefore, as a direct treatment method for rivers or appeals, a method of maximizing the self-cleaning action such as meandering rivers or creating artificial wetlands is applied. There is a problem that takes a long time to obtain a significant effect.

다른 방법으로 하천이나 호소에 석회계 수처리제를 살포하는 방법 등이 개발되어 적용되고 있으나, 강알칼리성인 석회계 수처리제의 살포는 수생생물의 서식환 경을 파괴할 수 있는 심각한 문제점이 있었다.Other methods have been developed and applied to spray the lime water treatment agent in rivers or lakes, but the spraying of a strong alkaline lime water treatment agent has a serious problem that can destroy the aquatic environment.

또한, 무기물을 이용한 수처리 방법으로서 한국공개특허 제2000-0053716호는 맥반석, 탈황석고, 석탄재를 함유하는 무기물 수처리제를 개시하고 있으나, 탈황석고 및 석탄재에는 오히려 부산물에 포함되어 있는 중금속 및 인체에 유해한 물질을 함유하고 있다. 한국공개특허 제2001-0036795호는 황토, 고령토, 규조토를 1100-1200℃에서 고온 소성하여 제조한 무기물 정수제를 개시하고 있으나, 정수제의 제조에 고비용이 소요되어 비용 대비하여 수처리 효율이 떨어지게 된다. In addition, Korean Patent Laid-Open Publication No. 2000-0053716 discloses an inorganic water treatment agent containing ganban stone, desulfurized gypsum and coal ash, but desulfurized gypsum and coal ash are rather heavy metals contained in by-products and harmful substances to the human body. It contains. Korean Patent Laid-Open No. 2001-0036795 discloses an inorganic water purifier prepared by calcining ocher, kaolin and diatomaceous earth at 1100-1200 ° C. at high temperature, but the cost of preparing the water purifier is high, resulting in inefficient water treatment efficiency. .

본 발명은 전술한 문제점을 해결하기 위하여, 별도의 처리시설을 증설하지 않고 저비용으로 제조 가능하며, 저수지, 하천 및 자연 호소 등에 살포하는 간단한 방법으로도 각종 오탁물을 응집, 침전시킴과 동시에 분해시켜 수질을 개선시킬 수 있는 친환경 활성 천연광물 수질개선제를 제공하는 것을 목적으로 한다.In order to solve the above problems, the present invention can be manufactured at low cost without adding a separate treatment facility, and by condensing and sedimenting various soils by a simple method of spraying on reservoirs, rivers, and natural appeals, An object of the present invention is to provide an environment-friendly active natural mineral water improver that can improve the water quality.

또한, 본 발명은 상기 친환경 활성 천연광물 수질개선제를 제조하는 방법을 제공하는 것을 다른 목적으로 한다. In addition, another object of the present invention to provide a method for producing the environmentally friendly active natural mineral water improver.

본 발명은 전술한 목적을 달성하기 위하여 창안된 천연광물이 혼합된 분말상의 수질개선제로서, 클리높틸로라이트(clinoptilolite) 60 내지 80중량%, 조암광 물(造巖鑛物) 7 내지 15중량%, 고CEC점토광물(高 Cation Exchange Capcity 粘土鑛物) 5 내지 10중량%, 화산재 5 내지 10중량% 및 돌로마이트 2 내지 6중량%로 구성됨을 특징으로 하는 친환경 활성 천연광물 수질개선제를 제공한다.The present invention is a powdered water quality improving agent mixed with natural minerals created to achieve the above object, 60 to 80% by weight of clinoptilolite, 7 to 15% by weight of rough rock minerals (造 巖 鑛物), It provides an environment-friendly active natural mineral water improver, characterized in that composed of 5 to 10% by weight of high CEC Exchange Minerals, 5 to 10% by weight volcanic ash and 2 to 6% by weight dolomite.

또한, 본 발명은 상기 수질개선제를 제조하는 방법으로서, 클리높틸로라이트(clinoptilolite), 조암광물(造巖鑛物), 고CEC점토광물(高 Cation Exchange Capcity 粘土鑛物), 화산재 및 돌로마이트를 각각 300메시(mesh) 체를 통과하는 입경의 분말로 분쇄하는 단계; 분쇄된 분말들을 혼합하여 혼합분말을 구성하는 단계; 및 혼합분말을 150℃로 가열하면서 다시 분쇄하는 단계로 이루어짐을 특징으로 하는 친환경 활성 천연광물 수질개선제의 제조방법을 제공한다. In addition, the present invention is a method for producing the water quality improver, clinoptilolite (clinoptilolite), crude rock (광 物), high CEC clay minerals (high Cation Exchange Capcity), volcanic ash and dolomite 300 mesh (mesh) pulverizing into a powder having a particle size passing through the sieve; Mixing the ground powder to form a mixed powder; And it provides a method for producing an environmentally friendly active natural mineral water improver, characterized in that consisting of the step of pulverizing again while heating the mixed powder to 150 ℃.

본 발명을 통하여 저수지, 하천 및 자연 호소의 각종 오탁물을 응집, 침전시켜 탁도를 크게 개선하고, 동시에 각종 오탁물을 분해시켜 녹조 및 담수적조의 원인이 되는 부영양화를 방지하여 수질을 개선함으로써, 수생생물의 서식환경을 개선하고 수변경관 확보 및 친수환경 조성 효과를 얻을 수 있으며, 처리시설의 증설 없이도 용수(用水)의 취수원 자체를 정화함으로써 각종 수처리시설의 처리부하를 경감하고 관련 시설의 건설 및 유지관리비용을 절감하는 효과를 얻을 수 있다.Through the present invention, by condensing and sedimenting various soils of reservoirs, rivers and natural lakes, the turbidity is greatly improved, and at the same time, various soils are decomposed to prevent eutrophication, which is the cause of green algae and freshwater tides, to improve water quality. It can improve the habitat environment of living organisms, secure water change pipes, and create a hydrophilic environment, and reduce the processing load of various water treatment facilities by constructing and maintaining the water intake source of water without the need for additional treatment facilities. It can reduce the management cost.

본 발명은 친환경 활성 천연광물 수질개선제 및 그 제조방법에 관한 것이다. The present invention relates to an environmentally friendly active natural mineral water improver and a method for producing the same.

이하, 본 발명을 상세하게 설명한다.EMBODIMENT OF THE INVENTION Hereinafter, this invention is demonstrated in detail.

본 발명의 수질개선제는 클리높틸로라이트(clinoptilolite) 및 양이온치환용량(CEC, Cation Exchange Capcity)이 큰 고CEC점토광물을 주요 구성요소로 포함함으로써, 표면에 많은 음전하가 발달하고 있어 많은 양의 양이온을 치환할 수 있는 친환경 활성 천연광물 수질개선제인 것을 특징으로 한다.The water quality improving agent of the present invention includes a high cec clay mineral having a large clinoptilolite and a high cation exchange capacity (CEC) as main components, so that a large amount of cations Characterized in that it is an environmentally friendly active natural mineral water improver that can substitute.

보다 상세하게, 본 발명의 친환경 활성 천연광물 수질개선제는 클리높틸로라이트(clinoptilolite) 60 내지 80중량%, 조암광물(造巖鑛物) 7 내지 15중량%, 고CEC점토광물(高 Cation Exchange Capcity 粘土鑛物) 5 내지 10중량%, 화산재 5 내지 10중량% 및 돌로마이트 2 내지 6중량%로 구성된다.In more detail, the eco-friendly active natural mineral water quality improving agent of the present invention is 60 to 80% by weight of clinoptilolite, 7 to 15% by weight of crude rock mineral, high CEC clay mineral (High Cation Exchange Capcity)鑛物) 5 to 10% by weight, 5 to 10% by weight ash and 2 to 6% by weight dolomite.

저수지, 하천 및 자연 호소 등에 빈번하게 발생되는 탁수(濁水)현상은 콜로이드상의 오탁물 입자가 주요 원인이며, 오탁물 입자 중의 유기물이나 영양염류는 부영양화를 일으켜 녹조 및 담수적조 현상을 발생시킨다. 이러한 오탁물 입자는 전기적으로 음이온의 성질을 가진다. 반면, 본 발명의 친환경 활성 천연광물 수질개선제는 클리높틸로라이트 및 고CEC점토광물을 포함하고 있어 많은 양의 양이온을 치환할 수 있는데, 도 1에 도시한 바와 같이, 이와 같이 양이온을 치환한 수질개선제 입자는 음전하를 띠는 오탁물 입자의 표면에 양이온이 분포되도록 함으로써, 결과적으로 수질개선제를 오탁물 입자가 감싸는 형태로 오탁물 입자를 응집하는 반응구조를 가지게 된다.Frequent turbidity in reservoirs, rivers, and natural lakes is mainly due to colloidal soil particles, and organic matter and nutrients in the soil particles cause eutrophication, resulting in green algae and freshwater red tide. These soil particles are electrically anionic. On the other hand, the eco-friendly active natural mineral water quality improvement agent of the present invention contains clinotillolite and high CEC clay minerals to replace a large amount of cations, as shown in FIG. The improver particles have a reaction structure in which cations are distributed on the surface of the negatively charged pollutant particles, thereby condensing the pollutant particles in a form in which the water improver surrounds the pollutant particles.

본 발명에 적용된 클리높틸로라이트는 국내에도 매장량이 풍부한 천연 제올 라이트로서, 제올라이트 총함량이 70% 이상이고 결정과 기공이 발달하여 양이온치환용량이 200meq/100g 이상인 특성을 가진다. 이러한 클리높틸로라이트는 (Si, Al)O4 사면체 내에서 Si4+가 Al3+로 일부 치환됨으로써 음(-)과 양(+)의 전하의 균형이 무너져 구조적으로 음(-)으로 가전된 상태를 나타내게 되며, 이와 같이 음(-)으로 가전된 상태에 대하여 양이온으로 치환시킴으로써 표면을 양(+)의 가전 상태로 치환시킨다. 이러한 표면의 양이온들은 주위의 다른 양이온들과 쉽게 치환될 수 있는 것이다.Clinotillolite applied to the present invention is a natural zeolite rich in reserves in Korea, the zeolite total content is 70% or more and has the characteristics that the cation substitution capacity is more than 200 meq / 100g due to the development of crystals and pores. In the clinoptillolite, Si 4+ is partially substituted with Al 3+ in the (Si, Al) O 4 tetrahedron, and thus the balance of negative and positive charges is broken, resulting in structurally negative electrical appliances. In this way, the surface is replaced with a positive (+) household state by substituting a cation for the negative (-) household. The cations on this surface can be easily substituted with other cations around.

본 발명에 적용된 조암광물은 석영, 백운모 및 장석과 같이 비중이 크면서도 수생생태계에 무해한 광물로서, 응집물의 비중을 증가시켜 침전을 유도하고, 특히 백운모는 정균작용(靜菌作用)을 하여 침전된 퇴적물에서 조류가 재번성하는 것을 방지하는 역할 또한 수행한다. 석영, 백운모 및 장석은 각각 단독 또는 2종 이상 조합하여 사용할 수 있다. 바람직하게는 석영, 백운모 및 장석을 함께 사용하는 것이 것이며, 이들의 중량비는 5-8:3-7:1-5인 것이 응집물의 형성 및 침전 속도를 효과적으로 조절할 수 있어 더 좋다.Crude minerals applied to the present invention are minerals such as quartz, dolomite and feldspar, which are large and harmless to aquatic ecosystems, and induce precipitation by increasing the specific gravity of aggregates. Particularly, dolomite is precipitated by bacteriostatic action. It also plays a role in preventing algal blooms from reproducing. Quartz, dolomite and feldspar can be used individually or in combination of 2 or more types, respectively. Preferably it is to use a combination of quartz, dolomite and feldspar, the weight ratio thereof is 5-8: 3-7: 1-5 is better to effectively control the formation and precipitation rate of the aggregate.

본 발명의 고CEC점토광물은 점토광물 중에서도 양이온치환능력(CEC, Cation Exchange Capcity)이 뛰어난 광물로서, 버미큘라이트(vermiculite), 몬모릴로나이트(montmorillonite) 및 일라이트(illite)로 이루어진 군으로부터 선택된 1종 이상인 것이 바람직하다. 이들 점토광물 또한 정균작용을 하여 침전된 퇴적물에서 조류가 재번성하는 것을 방지한다.The high CEC clay mineral of the present invention is a mineral excellent in cation exchange capacity (CEC) among clay minerals, and is at least one selected from the group consisting of vermiculite, montmorillonite and illite. desirable. These clay minerals also act as bacteriostatics to prevent algae from thriving in the sediment.

본 발명에 적용된 화산재는 중성인 안산암질 특성을 가지고 많은 기공이 형성되어 있으며 다량의 알루미늄과 규소를 함유하고 있는 것으로서, 예를 들면 일본 큐슈지방의 고 알루미늄 화산재를 사용할 수 있다.The volcanic ash applied to the present invention is neutral andesite, has a lot of pores and contains a large amount of aluminum and silicon, for example, a high aluminum volcanic ash of the Kyushu region of Japan can be used.

본 발명에 적용된 돌로마이트(dolomite)는 탄산염광물로서, 처리수의 pH를 안정적으로 유지하는 역할을 수행한다.Dolomite (dolomite) applied to the present invention is a carbonate mineral, serves to maintain a stable pH of the treated water.

이러한 구성요소를 가지는 본 발명의 친환경 활성 천연광물 수질개선제는 분말상으로 가공된다. 구체적으로, 구성요소 각각을 300메시(mesh) 체를 통과하는 300메시 이하의 입경을 갖는 분말로 분쇄하고, 분쇄된 분말들을 전술한 혼합비로 혼합하여 혼합분말을 구성한 후, 가열장치가 부착된 레이몬드밀과 같은 장치를 이용하여 혼합분말을 150℃로 가열하면서 10분간 재분쇄하여 제조한다.Environment-friendly active natural mineral water improver of the present invention having such a component is processed into a powder form. Specifically, each component is pulverized into a powder having a particle size of 300 mesh or less passing through a 300 mesh sieve, and the pulverized powders are mixed at the above-described mixing ratio to form a mixed powder, followed by Raymond with a heating device. It is prepared by regrinding for 10 minutes while heating the mixed powder to 150 ℃ using a device such as a mill.

이와 같이, 분말상으로 가공된 본 발명의 수질개선제는 처리대상 수역에 직접 살포되거나 희석된 후 분사되어 부유 오염물을 응집, 침전 및 분해시킴으로써 수질을 개선하게 되며, 천연광물 등을 주재로 한 것으로서 수생생물의 서식환경을 파괴하지 않는 특징이 있다.As such, the water quality improving agent of the present invention processed into a powder form is directly sprayed or diluted in the water to be treated and then sprayed to improve water quality by agglomeration, sedimentation and decomposition of suspended pollutants, and is mainly aquatic organisms. It does not destroy the habitation environment.

상기한 바와 같이, 본 발명의 수질개선제는 저수지, 하천, 자연 호소(湖沼), 지하수의 녹조, 적조 및 각종 오탁물로 오염된 수질을 개선할 수 있으며, 근해 해수 양식장, 예를 들어 김양식장과 같은 해양 오염의 개선에도 적용 가능하다.As described above, the water quality improving agent of the present invention can improve water quality contaminated with reservoirs, rivers, natural appeals, green algae, red tide, and various soils of groundwater, and offshore seawater farms, for example, The same applies to the improvement of marine pollution.

이하, 본 발명의 이해를 돕기 위하여 바람직한 실시예를 제시하나, 하기 실시예는 본 발명을 예시하는 것일 뿐 본 발명의 범주 및 기술사상 범위 내에서 다양 한 변경 및 수정이 가능함은 당업자에게 있어서 명백한 것이며, 이러한 변형 및 수정이 첨부된 특허청구범위에 속하는 것도 당연한 것이다.Hereinafter, preferred examples are provided to aid the understanding of the present invention, but the following examples are merely for exemplifying the present invention, and various changes and modifications within the scope and spirit of the present invention are apparent to those skilled in the art. Naturally, such modifications and variations fall within the scope of the appended claims.

[실시예]EXAMPLE

실시예 1-7Example 1-7

하기 표 1에 나타낸 조성비로 클리높틸로라이트, 조암광물, 고CEC점토광물, 화산재 및 돌로마이트를 혼합하여 수질개선제를 제조하였다.In the composition ratio shown in Table 1 below, clinotillolite, crude rock mineral, high CEC clay mineral, volcanic ash, and dolomite were mixed to prepare a water quality improver.

각각의 구성요소를 300메시(mesh) 이하의 입경을 갖는분말로 분쇄하고, 하기 표 1의 조성비로 혼합 및 교반하여 혼합분말을 구성하였다. 이어서, 혼합분말을 가열장치가 부착된 레이몬드밀에 투입하여 150℃로 가열하면서 10분간 재분쇄하여 수질개선제를 제조하였다.Each component was ground into a powder having a particle size of 300 mesh or less, and mixed and stirred at a composition ratio of Table 1 to form a mixed powder. Subsequently, the mixed powder was put in a raymond mill with a heating device and regrind for 10 minutes while heating at 150 ° C. to prepare a water quality improver.

구분division 클리높틸로라이트 (중량%)Clinotillolite (wt%) 조암광물(중량%)Crude mineral (wt%) 고CEC점토광물(중량%)High CEC Clay Minerals (wt%) 화산재 (중량%)Ash (% by weight) 돌로 마이트 (중량%)Dolomite (wt%) 석영quartz 백운모muscovite 장석feldspar 버미큘라이트Vermiculite 일라이트Illite 몬모릴로나이트Montmorillonite 실시예1Example 1 6565 77 55 33 33 55 -- 1010 22 실시예2Example 2 6565 77 55 33 33 33 22 1010 22 실시예3Example 3 6767 77 66 -- 33 55 -- 1010 22 실시예4Example 4 6767 88 -- 55 33 55 -- 1010 22 실시예5Example 5 6767 -- 88 55 33 55 -- 1010 22 실시예6Example 6 6565 77 55 33 33 -- 55 1010 22 실시예7Example 7 6565 77 55 33 -- 55 33 1010 22

[실험예] Experimental Example

전술한 실시예 1을 통하여 제조된 수질개선제를 인공연못에 살포하여 탁도를 개선하였다. The turbidity was improved by spraying the water improver prepared in Example 1 to the artificial pond.

실험예 1 - 인공연못의 탁수 정화처리Experimental Example 1-Treatment of Turbidity in Artificial Ponds

실험대상은 경상북도 포항시 송라면 소재 송라제니스골프장 내 연못으로서, 이 지역의 기반암은 이암으로 구성된 연일층으로 탁수를 유발하는 미립점토광물이 다량 함유되어 있는 바, 처리전 탁도가 186NTU에 달할 정도로 탁하였다. 실험대상 인공연못의 저수량은 약 5,000㎥로서 총 250㎏의 수질개선제를 수면에 고르게 살포하였고 48시간 경과 후 탁도가 1.2NTU로 개선되었다. 도 2에 나타낸 인공연못의 수질개선제로 처리하기 전(a), (c) 및 처리한 후(b), (d)의 동일지점의 사진을 통하여도 탁도가 개선된 것을 확인할 수 있었다. The subject was a pond in Songra Zenith Golf Course, Song Ramen, Song Ramen, Pohang, Gyeongsangbuk-do. The water storage volume of the artificial pond was about 5,000㎥, and a total of 250㎏ of water-improving agent was evenly sprayed on the surface, and the turbidity was improved to 1.2 NTU after 48 hours. Turbidity was also improved through photographs of the same spot before (a), (c) and after treatment (b) and (d) before treatment with the artificial pond water quality improving agent shown in FIG.

실험예 2 - 인공탁수 정화처리 및 일본송사리에 대한 독성시험Experimental Example 2-Artificial turbidity purification and toxicity test

수질개선제의 탁수 처리능력 및 수생생물에 대한 독성을 시험하기 위하여, 탈염소처리된 수돗물인 원수(原水), 수질개선제, 및 오탁물이 개별 또는 혼합되어 적재된 수조에 일본송사리(Oryzias latipes)를 각각 10마리씩 투입한 후 관찰하였다. 인위적으로 탁수를 형성하기 위하여 시험구3에 투입된 오탁물은 백토로서, 탁도가 1020NTU가 되도록 투입하였다.In order to test the turbidity and aquatic toxicity of the water-improving agent, Oryzias latipes were placed in a tank loaded with dechlorinated tap water, raw water, water-improving agent, and soil . 10 animals were added and observed. In order to artificially form turbid water, soil contained in Test Piece 3 was white clay, and the turbidity was added to 1020 NTU.

실험에 사용된 수조별 시험액의 조성은 하기 표 2에 나타낸 바와 같으며, 각 수조에 투입된 일본송사리의 제원은 하기 표 3에 나타낸 바와 같다. 실험에 사용된 수조는 대조구 및 각 시험구 공히 12ℓ용량의 유리수조이고, 실험은 실내 자연광 하에서 96시간 동안 실시되었으며, 실험중 먹이는 일절 공급하지 않았다.The composition of the test solution for each tank used for the experiment is as shown in Table 2, and the specifications of the Japanese pine fish in each tank are shown in Table 3 below. The water tank used in the experiment was a control tank and a glass tank having a capacity of 12 L for each test, and the experiment was conducted for 96 hours under indoor natural light, and no food was supplied during the experiment.

구분division 단위unit 대조구Control 시험구1Test Zone 1 시험구2Test 2 시험구3Test Sphere 3 시험액 조성Test solution composition 원수enemy 원수 +수질개선제Raw Water + Water Quality Improvement Agent 원수 +수질개선제Raw Water + Water Quality Improvement Agent 원수+오탁물 +수질개선제Raw Water + Soil + Water Quality Enhancer 시험액 량Test amount 1010 좌동Left 좌동Left 좌동Left 수질개선제 농도Water improver concentration ㎎/ℓMg / l -- 2020 4040 4040

개체 순번Object sequence number 대조구Control 시험구1Test Zone 1 시험구2Test 2 시험구3Test Sphere 3 전장(㎝)Full length (cm) 중량(g)Weight (g) 전장(㎝)Full length (cm) 중량(g)Weight (g) 전장(㎝)Full length (cm) 중량(g)Weight (g) 전장(㎝)Full length (cm) 중량(g)Weight (g) 1One 3.23.2 0.270.27 3.23.2 0.400.40 3.03.0 0.300.30 3.23.2 0.370.37 22 3.03.0 0.280.28 2.62.6 0.160.16 3.03.0 0.330.33 3.23.2 0.430.43 33 3.53.5 0.390.39 3.23.2 0.350.35 3.23.2 0.290.29 3.73.7 0.360.36 44 3.03.0 0.340.34 3.33.3 0.340.34 3.03.0 0.310.31 3.23.2 0.310.31 55 3.13.1 0.390.39 3.23.2 0.290.29 3.53.5 0.410.41 3.03.0 0.360.36 66 3.33.3 0.320.32 3.23.2 0.290.29 3.23.2 0.350.35 3.23.2 0.250.25 77 3.33.3 0.400.40 2.52.5 0.190.19 3.03.0 0.290.29 3.23.2 0.360.36 88 3.13.1 0.310.31 2.82.8 0.300.30 2.52.5 0.220.22 3.23.2 0.290.29 99 3.43.4 0.350.35 2.82.8 0.300.30 3.33.3 0.320.32 3.13.1 0.380.38 1010 3.03.0 0.310.31 3.23.2 0.310.31 3.43.4 0.340.34 3.13.1 0.430.43 평균Average 3.23.2 0.340.34 3.03.0 0.290.29 3.13.1 0.320.32 3.23.2 0.350.35

실험결과 대조구, 시험구1, 시험구2 및 시험구3에서 일본송사리의 폐사는 공히 관찰되지 않았으며, 도 3의 (a) 및 (b)에 나타낸 바와 같이, 지속적인 폭기가 이루어졌음에도 불구하고 시험구3에서는 탁도가 상당수준 개선되었음을 확인할 수 있다. 즉, 실험 초기 탁수로 인하여 시험어를 확인할 수조차 없던 시험구3이 실험 종료시에는 수조 바닥의 침전물을 확인할 수 있을 정도로 탁도가 개선되었다. 이와 같이, 본 발명의 수질개선제를 적용하면 수생생물에 대한 독성작용을 나타내지 않으면서도 오탁물 등에 의하여 오염된 수질을 개선할 수 있다. Experimental results No mortality of Japanese squid was observed in the control, test 1, test 2 and test 3, despite the continuous aeration as shown in (a) and (b) of FIG. In Test 3, it can be seen that the turbidity was significantly improved. In other words, the turbidity was improved enough to be able to check the sediment at the bottom of the tank at the end of the experiment when Test 3, which could not even confirm the test words due to the initial turbidity. As such, by applying the water-improvement agent of the present invention, it is possible to improve the water quality contaminated by soil and the like without exhibiting toxic effects on aquatic organisms.

실험예 3 - 일본 이키사댐의 수질정화Experimental Example 3-Water Purification of Ikisa Dam, Japan

실험대상은 일본의 마쓰우라가와수계 이키사카와 상부류에 위치한 중력식 콘크리트 댐으로서, 이 지역은 댐 저수지 내의 퇴적물로부터 용출하는 부식물질, 또는 부식물질과 철이 착체를 형성하여 ‘사사니고리’라는 물의 착색 현상과 다량으로 발생한 부식물질로 인해 오히려 규조류 등의 식물성 플라크톤의 이상 번식 현상이 장기간 발생하고 있었다. 실험대상 댐의 유효 저수량은 약 1,660,000㎥로서 ℓ당 40㎎이 되도록 총 66톤의 수질개선제를 약 3.5일 기간 동안 수면에 고르게 살포하였다.The test subject was a gravity concrete dam located in the upper part of Ikisawa, Matsuura River, Japan. This area is a corrosive material that elutes from sediments in the dam reservoir, or a complex of corrosive materials and iron forms a color of water called 'Sasanigori'. Due to the phenomenon and the large amount of corrosive substances, abnormal propagation of phytoplankton such as diatoms occurred for a long time. A total of 66 tons of water-improving agent was evenly sprayed on the water surface for about 3.5 days so that the effective reservoir of dam was about 1,660,000m3.

수질개선제를 살포하기 전 및 살포하여 1개월 경과한 후의 물의 외관 상태를 비교한 결과를 하기 표 4에 나타내었다. Table 4 shows the results of comparing the appearance state of the water before and after spraying the water improver after one month.

항목Item 처리전Before treatment 처리 1개월 후1 month after treatment 수면 물색Sleep shopping 갈색(붉은색)Brown (red) 연푸른 물색Light blue shopping 물의 외관색Exterior color of water 담황색buff 무색 투명transparent 댐 투명도Dam transparency 2.8m2.8m 8.0m8.0m

또한, 수질개선제를 살포하기 전의 1개월 평균 수질 분석값과 수질개선제를 살포하고 1개월 및 13개월 경과한 후의 각각의 수질 분석값을 측정하고, 그 비교 결과를 하기 표 5에 나타내었다. In addition, 1 month average water quality analysis value and the water quality analysis value after 1 month and 13 months after spraying the water quality improvement agent before the water quality improvement agent was measured, and the comparison result is shown in Table 5 below.

항목Item 처리전Before treatment 처리 1개월Treatment one month 처리 13개월13 months treatment 분석값Analysis value 분석값Analysis value 비율(저감율)Rate (low rate) 분석값Analysis value 비율(저감율)Rate (low rate) COD(㎎/ℓ)COD (mg / L) 1.71.7 1.21.2 71%(29%)71% (29%) 1.21.2 71%(29%)71% (29%) SS(㎎/ℓ)SS (mg / l) 33 1미만Less than 1 40%(60%)40% (60%) 1One 40%(60%)40% (60%) T-N(㎎/ℓ)T-N (mg / L) 0.400.40 0.270.27 68%(32%)68% (32%) 0.330.33 83%(17%)83% (17%) T-P(㎎/ℓ)T-P (mg / l) 0.0220.022 0.0060.006 28%(72%)28% (72%) 0.0100.010 47%(53%)47% (53%) 색도(도)Chromaticity (degrees) 10.510.5 4.74.7 45%(55%)45% (55%) 3.93.9 37%(63%)37% (63%) 탁도(도)Turbidity (degrees) 3.13.1 0.90.9 30%(70%)30% (70%) 1.11.1 36%(64%)36% (64%)

상기 표 4 및 5에 나타낸 바와 같이, 수질개선제를 살포하여 처리하면 물의 수면 및 외관적인 색상이 변화되어 투명도가 개선되었으며, 특히 색도 및 탁도의 경우 분석시 저감율이 55-70%로 효과가 우수하였다. 동시에, 오탁물 중의 각종 유기물도 분해되어 식물성 플라크톤의 이상 번식 현상, 녹조 및 담수적조 등의 원인이 되는 부영양화도 방지할 수 있으며, 수질의 지표가 되는 COD, SS, T-N, T-P 등도 개선되었다. 또한, 댐 저수지 및 하류 하천의 수생생물을 조사한 결과, 어류나 갑각류의 폐사나 이상행동은 확인되지 않았다.As shown in Tables 4 and 5, when the water treatment was applied by spraying the water-improving agent, the water surface and the external color of the water were changed to improve transparency, and in particular, in the case of chromaticity and turbidity, the reduction rate was 55-70%. . At the same time, various organic matters in the soil are also decomposed to prevent eutrophication, which causes abnormal propagation of phytoplankton, green algae and freshwater red tide, and also improves COD, SS, T-N, and T-P, which are indicators of water quality. In addition, as a result of examining aquatic organisms in dam reservoirs and downstream streams, no death or abnormal behavior of fish or crustaceans was confirmed.

이키사댐과 이키사댐의 방류부인 미카에리 폭포의 수질개선제를 살포하여 처리하기 전(a), 처리 직후(b), 처리 1개월 후(c) 및 처리 13개월 후(d)의 동일지점의 사진을 각각 도 4 및 5에 나타내었다. 도 4 및 5에 나타낸 바와 같이, 처리 전에는 투명도가 2-3m 정도로 물은 담황색을 나타내고 댐의 표면은 약간 갈색을 나타내고 있었으며, 수질개선제 처리 직후에는 물의 색상이 코발트 블루와 같은 색상을 띠면서 시간이 경과함에 따라 그 색이 서서히 연하게 변하였고, 1개월 후에는 투명도가 8m 정도가 되어 물이 맑고 투명한 상태가 되었다. 이키사 댐의 경우, 처리 13개월 후(도 4d)에는 처리 1개월 후(도 4c)와 비교하여 물의 색상이 약간 녹색을 나타내고 있으나 투명도는 4.3m 정도로 처리 전보다 높고 착색 현상은 없었다. 미카에리 폭포의 경우에도 13개월 후(도 5d)에는 처리 1개월 후(도 5c)와 비교하여 약간 녹색을 나타내고 있으나 별도의 착색 현상은 없으며 바닥의 바위를 명확하게 확인할 수 있을 정도의 투명도를 나타내었다. 이러한 현상은 댐으로 계속적으로 유입되고 유출되는 수질의 상태, 강우량 및 오랜 기간동안 댐에 존재하고 있던 퇴적물의 계속적인 용출에 의한 것으로 판단되며, 자연적 요인을 고려하면 본 발명의 친환경 활성 천연광물 수질개선제는 충분한 장기적인 효과를 갖는 것으로 기대된다. Photo of the same spot before (a), immediately after treatment (b), after one month of treatment (c) and after 13 months of treatment (d) before spraying water treatment of Mikaeri Falls, the discharge of Ikisa Dam and Iki Dam Are shown in FIGS. 4 and 5, respectively. As shown in Figures 4 and 5, the water was pale yellow and the surface of the dam was slightly brown and the surface of the dam was slightly brown before the treatment, and the color of the water had the same color as the cobalt blue immediately after treatment. As time passed, the color gradually changed to light, and after one month, the transparency became about 8m and the water became clear and transparent. In the case of the Ikisa dam, after 13 months of treatment (FIG. 4D), the color of water was slightly greener than that of 1 month of treatment (FIG. 4C), but the transparency was higher than that of the treatment at 4.3 m, and there was no coloring phenomenon. In the case of Mikaeri Falls, after 13 months (Fig. 5D), it is slightly green compared to after 1 month of treatment (Fig. 5C), but there is no coloring phenomenon and the transparency enough to clearly identify the rock on the bottom. It was. This phenomenon is judged by the condition of water quality continuously flowing into and out of the dam, rainfall and continuous elution of the sediments that existed in the dam for a long time, and considering the natural factors, the eco-friendly active natural mineral water quality improving agent of the present invention. Is expected to have a sufficient long-term effect.

상기한 바와 같이, 본 발명의 친환경 활성 천연광물 수질개선제는 녹조, 적조 및 각종 오탁물로 오염된 저수지, 하천, 자연 호소(湖沼), 지하수뿐만 아니라 근해 해수 양식장과 같은 해양의 수질을 개선하는데 적용 가능하다. As described above, the environment-friendly active natural mineral water quality improvement agent of the present invention is applied to improve the water quality of the marine, such as reservoirs, rivers, natural appeal, groundwater contaminated with green algae, red tide and various soils, as well as offshore seawater farms. It is possible.

도 1은 본 발명의 수질개선제의 오탁물 응집원리를 설명한 도면이고,1 is a view illustrating the principle of flocculant aggregation of the water quality improving agent of the present invention,

도 2는 본 발명의 수질개선제로 처리하기 전(a), (c) 및 처리한 후(b), (d)의 인공연못의 사진이며,Figure 2 is a photograph of the artificial pond before (a), (c) and after treatment (b), (d) treatment with the water quality improving agent of the present invention,

도 3은 본 발명의 수질개선제로 인공탁수 정화처리 및 일본송사리에 대한 독성시험 개시한 직후(a) 및 종료시(b)의 사진이고,3 is a photograph of immediately after (a) and at the end (b) of the artificial turbidity purification treatment and toxicity test for Japanese squid with water quality improving agent of the present invention,

도 4는 본 발명의 수질개선제로 처리하기 전(a), 처리 직후(b), 처리 1개월 후(c) 및 처리 13개월 후(d)의 이키사댐의 사진이며,4 is a photograph of Ikisa dam before (a), immediately after treatment (b), after one month of treatment (c) and after 13 months of treatment (d) before treatment with the water quality improving agent of the present invention.

도 5는 본 발명의 수질개선제로 처리하기 전(a), 처리 직후(b), 처리 1개월 후(c) 및 처리 13개월 후(d)의 이키사댐의 방류부인 미카에리 폭포의 사진이다.Fig. 5 is a photograph of Mikaeri Falls which is the discharge part of the Ikisa Dam before (a), immediately after treatment (b), after one month of treatment (c) and after 13 months of treatment (d) of the present invention.

Claims (5)

천연광물이 혼합된 분말상의 수질개선제로서, 클리높틸로라이트(clinoptilolite) 60 내지 80중량%, 조암광물(造巖鑛物) 7 내지 15중량%, 고CEC점토광물(高 Cation Exchange Capcity 粘土鑛物) 5 내지 10중량%, 화산재 5 내지 10중량% 및 돌로마이트 2 내지 6중량%로 구성됨을 특징으로 하는 친환경 활성 천연광물 수질개선제.Powder-like water-improving agent mixed with natural minerals, 60 to 80% by weight of clinoptilolite, 7 to 15% by weight of crude rock minerals, high CEC Exchange Minerals 5 Eco-friendly active natural mineral water quality improvement, characterized in that consisting of 10 to 10% by weight, 5 to 10% by weight of volcanic ash and 2 to 6% by weight of dolomite. 제1항에 있어서, 고CEC점토광물은 버미큘라이트(vermiculite), 몬모릴로나이트(montmorillonite) 및 일라이트(illite)로 이루어진 군으로부터 선택된 1종 이상임을 특징으로 하는 친환경 활성 천연광물 수질개선제.The method of claim 1, wherein the high CEC clay mineral is an environmentally friendly natural mineral water improver, characterized in that at least one selected from the group consisting of vermiculite, montmorillonite and illite. 제2항에 있어서, 고CEC점토광물은 버미큘라이트(vermiculite), 일라이트(illite) 또는 이들의 혼합물인 것임을 특징으로 하는 친환경 활성 천연광물 수질개선제. The environmentally friendly natural mineral water improver of claim 2, wherein the high CEC clay mineral is vermiculite, illite, or a mixture thereof. 제1항에 있어서, 조암광물(造巖鑛物)은 석영, 백운모 및 장석으로 이루어진 군으로부터 선택된 1종 이상임을 특징으로 하는 친환경 활성 천연광물 수질개선제. The environmentally friendly active natural mineral water improver according to claim 1, wherein the crude rock mineral is one or more selected from the group consisting of quartz, dolomite and feldspar. 제1항 내지 제4항 중 어느 한 항의 수질개선제를 제조하는 방법으로서,A method for producing the water quality improving agent according to any one of claims 1 to 4, 클리높틸로라이트(clinoptilolite), 조암광물(造巖鑛物), 고CEC점토광물(高 Cation Exchange Capcity 粘土鑛物), 화산재 및 돌로마이트를 각각 300메시(mesh) 체를 통과하는 입경의 분말로 분쇄하는 단계;Crushing clinoptilolite, coarse minerals, high CEC exchange minerals, volcanic ash and dolomite into powder with a particle diameter of 300 mesh ; 분쇄된 분말들을 혼합하여 혼합분말을 구성하는 단계; 및 Mixing the ground powder to form a mixed powder; And 혼합분말을 150℃로 가열하면서 다시 분쇄하는 단계로 이루어짐을 특징으로 하는 친환경 활성 천연광물 수질개선제의 제조방법.Method for producing an eco-friendly active natural mineral water improver, characterized in that the step of pulverizing again while heating the mixed powder to 150 ℃.
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