KR100339884B1 - modifier for precipitate and method for preparing it - Google Patents

modifier for precipitate and method for preparing it Download PDF

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KR100339884B1
KR100339884B1 KR1020000018888A KR20000018888A KR100339884B1 KR 100339884 B1 KR100339884 B1 KR 100339884B1 KR 1020000018888 A KR1020000018888 A KR 1020000018888A KR 20000018888 A KR20000018888 A KR 20000018888A KR 100339884 B1 KR100339884 B1 KR 100339884B1
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precipitate
less
present
magnesium hydroxide
weight
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KR1020000018888A
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KR20010099527A (en
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최병용
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신승근
주식회사 포스렉
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B65CONVEYING; PACKING; STORING; HANDLING THIN OR FILAMENTARY MATERIAL
    • B65HHANDLING THIN OR FILAMENTARY MATERIAL, e.g. SHEETS, WEBS, CABLES
    • B65H75/00Storing webs, tapes, or filamentary material, e.g. on reels
    • B65H75/02Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks
    • B65H75/34Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables
    • B65H75/38Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables involving the use of a core or former internal to, and supporting, a stored package of material
    • B65H75/44Constructional details
    • B65H75/4481Arrangements or adaptations for driving the reel or the material
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B60VEHICLES IN GENERAL
    • B60PVEHICLES ADAPTED FOR LOAD TRANSPORTATION OR TO TRANSPORT, TO CARRY, OR TO COMPRISE SPECIAL LOADS OR OBJECTS
    • B60P3/00Vehicles adapted to transport, to carry or to comprise special loads or objects
    • B60P3/22Tank vehicles
    • B60P3/224Tank vehicles comprising auxiliary devices, e.g. for unloading or level indicating
    • B60P3/2265Arrangements for hoses, tubes, or reels
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B65CONVEYING; PACKING; STORING; HANDLING THIN OR FILAMENTARY MATERIAL
    • B65HHANDLING THIN OR FILAMENTARY MATERIAL, e.g. SHEETS, WEBS, CABLES
    • B65H75/00Storing webs, tapes, or filamentary material, e.g. on reels
    • B65H75/02Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks
    • B65H75/34Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables
    • B65H75/38Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables involving the use of a core or former internal to, and supporting, a stored package of material
    • B65H75/40Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables involving the use of a core or former internal to, and supporting, a stored package of material mobile or transportable
    • B65H75/42Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables involving the use of a core or former internal to, and supporting, a stored package of material mobile or transportable attached to, or forming part of, mobile tools, machines or vehicles
    • B65H75/425Cores, formers, supports, or holders for coiled, wound, or folded material, e.g. reels, spindles, bobbins, cop tubes, cans, mandrels or chucks specially adapted or mounted for storing and repeatedly paying-out and re-storing lengths of material provided for particular purposes, e.g. anchored hoses, power cables involving the use of a core or former internal to, and supporting, a stored package of material mobile or transportable attached to, or forming part of, mobile tools, machines or vehicles attached to, or forming part of a vehicle, e.g. truck, trailer, vessel
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B65CONVEYING; PACKING; STORING; HANDLING THIN OR FILAMENTARY MATERIAL
    • B65HHANDLING THIN OR FILAMENTARY MATERIAL, e.g. SHEETS, WEBS, CABLES
    • B65H2402/00Constructional details of the handling apparatus
    • B65H2402/40Details of frames, housings or mountings of the whole handling apparatus
    • B65H2402/42Mobile apparatus, i.e. mounted on mobile carrier such as tractor or truck
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B65CONVEYING; PACKING; STORING; HANDLING THIN OR FILAMENTARY MATERIAL
    • B65HHANDLING THIN OR FILAMENTARY MATERIAL, e.g. SHEETS, WEBS, CABLES
    • B65H2701/00Handled material; Storage means
    • B65H2701/30Handled filamentary material
    • B65H2701/33Hollow or hose-like material

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  • Engineering & Computer Science (AREA)
  • Health & Medical Sciences (AREA)
  • Public Health (AREA)
  • Transportation (AREA)
  • Mechanical Engineering (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

본 발명은 해수, 강, 수산양식어장에서 침전물을 개선하여 수질오염을 방지하는 약제에 관한 것으로, 그 목적은 수산물과 저서생 생물의 폐사 없이 양식어장의 수질을 정화하고 또한, 적조를 방지할 수 있는 침전물 개선제와 그 제조방법을 제공함에 있다.The present invention relates to a medicament for preventing water pollution by improving sediment in seawater, rivers, and fish farms. The object of the present invention is to purify the water quality of fish farms without death of aquatic products and benthic organisms, and to prevent red tide. The present invention provides a sediment improver and a method for preparing the same.

상기 목적을 달성하기 위한 본 발명은,The present invention for achieving the above object,

활성도 200이하의 활성수산화칼슘: 5중량%이하, 수용성 철분:0.1-1중량%, 나머지 활성도가 100이하의 활성수산화 마그네슘과 기타 불가피한 불순물로 조성되는 침전물 개선재; 그리고, 해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리를 탈수하는 단계;Activated calcium hydroxide with an activity of 200 or less: 5% by weight or less, water-soluble iron: 0.1-1% by weight, and a precipitate improving material composed of active magnesium hydroxide and other unavoidable impurities having a remaining activity of 100 or less; Dehydrating the magnesium hydroxide slurry generated in the seawater magnesium production process;

탈수한 원료를 진공성형하여 입자로 만드는 단계;Vacuum molding the dehydrated raw material into particles;

성형된 입자를 건조하는 단계;를 포함하여 이루어지는 침전물개선제의 제조방법에 관한 것을 그 기술적요지로 한다.Drying the molded particles; It relates to the technical subject of the method for producing a precipitate improver comprising a.

Description

침전물 개선제와 그 제조방법{modifier for precipitate and method for preparing it}Sediment modifier and its preparation method {modifier for precipitate and method for preparing it}

본 발명은 해수, 강, 수산양식어장에서 침전물을 개선하여 수질오염을 방지하는 약제에 관한 것으로, 보다 상세하게는 수산생물, 미생물의 폐사 없이 양식어장의 수질오염원을 제거할 수 있는 침전물 개선제에 관한 것이다.The present invention relates to a medicament for preventing water pollution by improving sediment in seawater, rivers, and fish farms, and more particularly, to a sediment improver capable of removing water pollution sources of fish farms without the death of aquatic organisms and microorganisms. will be.

근래들어 생활하수, 분뇨, 공장배출수, 비료와 농약 등의 육상오염물이 무분별하게 바다나 강으로 유입되고, 또한, 양식장에서 발생하는 각종 사료찌꺼기, 양식 수산물의 배설물 등이 육상오염물과 함께 해수나 강의 저부에 축적되면서 이들이 박테리아에 의해 부패됨에 따라 수산양식장, 내만의 환경이 악화되고 있다.In recent years, land sewage such as living sewage, manure, factory discharge water, fertilizers and pesticides are indiscriminately introduced into the sea or rivers, and various food wastes and aquaculture products excreted from aquaculture farms, along with land pollution, As they accumulate at the bottom, they are decayed by bacteria, deteriorating the environment inside the fish farm.

이들 축적물질들이 부패될 때는 수산생물에 독성을 주는 황화수소와 미생물의 영양염류인 질소와 인을 공급하여 녹조 또는 적조를 발생시켜서 수중의 용존산소를 감소시킨다. 또한, 독성 플랑크톤을 발생시켜 양식어장의 어패류, 해조류 등 양식 수산물을 고사시키고 수산물 생산성을 감소시키며, 더 나아가 인명피해 및 환경을 파괴하여 많은 피해를 준다. 물론, 영양염류를 포함한 오폐수 유입을 엄격히 규제하고 또한, 양식 수산물의 먹의 찌꺼기와 배설물을 제거하면 그 피해를 줄일 수 있지만, 이는 현실적으로 어렵다.When these accumulators decay, hydrogen sulfide and nutrients of microorganisms, nitrogen and phosphorus, which are toxic to aquatic organisms, are supplied to produce green algae or red algae to reduce dissolved oxygen in water. In addition, by generating toxic plankton, aquaculture products such as fish and shellfish and algae in aquaculture farms are killed, and aquatic product productivity is reduced. Furthermore, it causes a lot of damages by destroying human life and environment. Of course, strict restrictions on the inflow of wastewater, including nutrients, and removal of food waste and excreta from aquaculture can reduce the damage, but this is practically difficult.

이러한 피해를 줄이기 위한 차원에서 저부의 축절물질을 제거하거나 저질개선제를 살포하고 있다. 저질개선제로는 석회, 황토, 고토계 물질, 수산화마그네슘이 주로 이용되고 있다.In order to reduce such damage, the bottoms are removed or sprayed with quality improvers. As the quality improvement agent, lime, loess, clay type, magnesium hydroxide are mainly used.

석회(CaO)를 살포하면 수중의 황산이온(SO4 -)이 석고(CaSO4,2H2O)로 된다. 생성물인 석고가 해저표면에 치밀막을 형성하여 수중의 용존산소를 차단하여 그 석고막 하부에서 서식하는 조개류 및 수산생물을 질실시켜 어장이 황폐화되는 문제점이 있다. 또한, 축적물질에서 발생되는 황화수소, 암모니아, 인을 제거하기 위해 살포한 약제의 반응을 차단함으로써 어장의 황폐화를 가중시킨다. 황토는 유화물질 등을 흡착시켜 바닥으로 침전시키지만 이 침전물이 막을 형성하여 석회살포와 같은 문제가 발생한다. 고토계 물질은 살포되면 마그네슘과 생석회로 해리되는데, 이들은 수중에서 용해도가 낮아 석회와 같은 문제를 일으킨다.Spraying lime (CaO) turns gypsum (CaSO 4 , 2H 2 O) into sulfate ions (SO 4 ) in water. Gypsum, a product, forms a dense film on the bottom of the sea to block dissolved oxygen in the water, causing the shellfish and aquatic organisms to inhabit the lower part of the gypsum film, causing fisheries to be devastated. In addition, the degradation of fisheries is aggravated by blocking the reaction of the sprayed agent to remove hydrogen sulfide, ammonia and phosphorus generated from the accumulation material. Ocher adsorbs emulsifiers and settles to the bottom, but these deposits form a film and cause problems such as lime spraying. High soils dissociate into magnesium and quicklime when sprayed, which causes low solubility in water, causing problems like lime.

본 발명은 수산물과 저서생 생물의 폐사 없이 양식어장의 수질을 정화하고 또한, 적조를 방지할 수 있는 침전물 개선제와 그 제조방법을 제공함에 있다.The present invention provides a sediment improving agent and a method for producing the same that can purify the water quality of aquaculture fisheries and prevent red tide without the death of aquatic products and benthic organisms.

도 1은 해수에서 침전물개선제의 화학조성 변화와 외관변화를 알아보기 위해 적용된 실험장치의 일례도1 is an example of an experimental apparatus applied to find out the change in chemical composition and appearance of the sediment improver in seawater

상기 목적을 달성하기 위한 본 발명의 침전물 개선제는, 활성도 200이하의 활성수산화칼슘: 5중량%이하, 수용성 철분:0.1-1중량%, 나머지 활성도가 100이하의 활성수산화 마그네슘과 기타 불가피한 불순물로 조성된다.Sediment improver of the present invention for achieving the above object is composed of active calcium hydroxide of less than 200 activity: less than 5% by weight, water-soluble iron: 0.1-1% by weight, active magnesium hydroxide of the remaining activity of less than 100 and other unavoidable impurities .

또한, 본 발명의 침전물 개선제의 제조방법은,In addition, the method for producing a precipitate improving agent of the present invention,

해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리를 탈수하는 단계;Dehydrating the magnesium hydroxide slurry generated in the seawater magnesium production process;

탈수한 원료를 진공성형하여 입자를 얻는 단계;Vacuum molding the dehydrated raw material to obtain particles;

성형된 입자를 건조하는 단계;를 포함하여 구성된다.It is configured to include; drying the shaped particles.

이하, 본 발명을 상세히 설명한다.Hereinafter, the present invention will be described in detail.

본 발명에서는 해수나 강 저부 표면에 막을 형성하지 않도록 개선제 성분의 배합비를 조절하면서 높은 반응속도에 의해 오염물과의 빠른 반응으로 제거효율을 높이기 위해 활성화처리한 개선제를 사용하는데, 그 주요한 특징이 있다.In the present invention, the active agent is used to improve the removal efficiency by fast reaction with contaminants by controlling the compounding ratio of the improver component so as not to form a film on the surface of the sea water or the river bottom.

본 발명의 침전물 개선제는, 수산화마그네슘, 수산화칼슘, 수용성철분을 주요성분으로 하는데, 수산화마그네슘과 수산화칼슘은 활성화도가 높은 것을 사용한다.The precipitate improver of the present invention includes magnesium hydroxide, calcium hydroxide, and water-soluble iron, and magnesium hydroxide and calcium hydroxide are those having high activation.

수산화마그네슘은 유해물질중 수생생물에 독성을 주는 황화수소, 암모니아 등을 제거하는 유효한 작용을 하나, 수중에서의 용해도는 약 0.009%로 난용해성물질이다. 따라서, 본 발명에서는 수산화마그네슘의 반응속도를 높이기 위해서 활성화도가 100이하의 것을 사용한다. 활성화도가 100을 넘는 경우에는 침전물중의 T-S(Total-Sulphur;황화물)의 제거량이 크지 않다.Magnesium hydroxide is effective in removing harmful substances such as hydrogen sulfide and ammonia, which are toxic to aquatic organisms, but its solubility in water is about 0.009%. Therefore, in the present invention, in order to increase the reaction rate of magnesium hydroxide, one having an activation degree of 100 or less is used. If the activation degree exceeds 100, the removal amount of T-S (Total-Sulphur) in the precipitate is not large.

수산화칼슘은 유해물질과 반응하여 침전물을 개선하나 그 첨가량이 너무 많아지면 수중의 황산이온과 반응하여 황산칼슘(CaSO4·2H2O;석고)을 생성시켜 오히려 수면저부를 콘크리트화하여 저생생물을 고사시킬 가능성이 높아지므로 5중량%이하로 하는 것이 바람직하다. 수산화칼슘 또한 오염물의 제거효율을 높이기 위해 활성화도 200이하의 것을 사용하는 것이 바람직하다.Calcium hydroxide reacts with harmful substances to improve the precipitate, but when the amount is too high, it reacts with sulfate ions in water to produce calcium sulfate (CaSO 4 · 2H 2 O; gypsum). Since it will become high, it is preferable to set it as 5 weight% or less. Calcium hydroxide is also preferably used less than 200 to increase the efficiency of removing contaminants.

본 발명에서 수용성철분은 모든 수생생물의 필수 영양소로서 0.1중량%이상 되어야 물고기, 조개류 등에게 유효한 작용을 기대할 수 있으며, 1중량%를 넘으면 수중의 황화물과 반응하여 독성물질을 생성시켜 수생생물에게 독성을 주어 침전물개선에 방해가 된다.In the present invention, water-soluble iron should be at least 0.1% by weight as an essential nutrient of all aquatic organisms, and can be expected to be effective for fish, shellfish, etc., and if it exceeds 1% by weight, it reacts with sulfides in water to produce toxic substances, which is toxic to aquatic organisms. To hinder sediment improvement.

본 발명의 침전물개선제는, 수산화마그네슘, 수산화칼슘, 수용성철분의 원료를 배합하여 사용할 수 있다. 이때, 수산화마그네슘, 수산화칼슘을 각각 활성화처리하여 배합할 수도 있고, 이들을 배합한 다음에 활성화처리 할 수도 있다. 활성수산화마그네슘으로서는 천연 마그네시아 사이트, 브루싸이트(Brucite), 돌로마이트의 가소물을 원료로 하여 활성시킨 것을 예로 들 수 있다. 활성산화칼슘은 석회석을 소성하여 만든 생석회, 소석회 또한 조개껍질, 굴껍질을 소성한 것을 원료로 하여 활성시킨 것을 예로 들 수 있다.The precipitate improving agent of this invention can mix | blend the raw material of magnesium hydroxide, calcium hydroxide, and water-soluble iron powder. At this time, magnesium hydroxide and calcium hydroxide may be activated and blended, respectively, or may be blended and then activated. Examples of active magnesium hydroxide include those activated by using natural magnesia sites, brucite and dolomite as plastic raw materials. Examples of activated calcium oxide include quicklime made by calcining limestone, calcareous lime, and calcined shellfish and oyster shells.

본 발명에서는 해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리를 탈수, 진공성형, 건조의 공정으로 처리함으로써 본 발명의 침전물 개선제 조성물을 얻는데도, 큰 특징이 있다.In the present invention, the magnesium hydroxide slurry generated in the seawater magnesia production process is treated by dehydration, vacuum forming, and drying to obtain the precipitate improver composition of the present invention.

보통 해수마그네시아는 정제된 해수와 생성회(CaO)를 반응시켜 수산화마그네슘 슬러리를 만들고, 이 수산화마그네슘 슬러리를 건조하여 소성하여 얻어진다. 수산화마그네슘 슬러리의 조성의 대표적인 예가 아래 표 1에 나타나 있다.Normally, seawater magnesia is obtained by reacting purified seawater with produced ash (CaO) to form a magnesium hydroxide slurry, and drying and firing the magnesium hydroxide slurry. Representative examples of the composition of the magnesium hydroxide slurry are shown in Table 1 below.

화학성분(중량%)Chemical composition (% by weight) MgOMgO CaOCaO SiO2 SiO 2 F32O3+Al2O3 F3 2 O 3 + Al 2 O 3 Ig-LossIg-Loss 92-9892-98 0.6-2.00.6-2.0 0.2-3.00.2-3.0 1.0-3.01.0-3.0 1.0이하1.0 or less

표 1에서 알 수 있듯이, 해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리에는 MgO의 함량이 높고, CaO의 함량이 5%이내이면서 수용성 철분이 함유되어 있어 본 발명의 개선제로 유용하게 사용될 수 있음을 알 수 있다.As can be seen from Table 1, the magnesium hydroxide slurry generated in the seawater magnesia manufacturing process has a high content of MgO, CaO content of less than 5% while containing water-soluble iron, it can be seen that it can be usefully used as an improving agent of the present invention Can be.

본 발명에서는 해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리를 활성화하여 본 발명의 침전물 개선제를 제조한다. 활성화처리는 슬러리를 입자화할 때 비표면적을 높여서 반응속도를 확보하는 것으로, 진공성형공정과 건조공정의 조건를 제어하여 얻어진다.In the present invention, to activate the magnesium hydroxide slurry generated in the seawater magnesia manufacturing process to prepare a precipitate improver of the present invention. The activation treatment is to obtain a reaction rate by increasing the specific surface area when the slurry is granulated, and is obtained by controlling the conditions of the vacuum forming process and the drying process.

먼저, 본 발명에 따라 해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리(이하 간단히 '수산화마그네슘 슬러리'라 함)를 탈수하는데, 이때의 탈수는 슬러리의 수분함량이 28-32%가 되도록 하는 것이 바람직하다. 이는 슬러리의 수분함량이 이 범위를 만족하여야 성형성이 가장 좋기 때문이다. 슬러리의 수분함량이 28%미만의 경우에는 성형이 어려울 수 있으며, 32%를 넘는 경우에는 성형이 가능해도 진공성형과정에서 미세기공의 형성이 어렵다. 만일 탈수로서 수분함량을 32%이내로 조절할 수 없는 경우에는 건조를 통해 관리범위로 조절하는 것도 가능하다.First, the magnesium hydroxide slurry (hereinafter referred to simply as 'magnesium hydroxide slurry') generated in the seawater magnesium production process according to the present invention is dewatered, and the dehydration at this time is preferably such that the water content of the slurry is 28-32%. . This is because the water content of the slurry must satisfy this range for the best formability. If the water content of the slurry is less than 28%, it may be difficult to mold, and if it is more than 32%, it may be difficult to form micropores in the vacuum forming process. If the water content cannot be controlled within 32% due to dehydration, it is possible to adjust the control range through drying.

적절한 수분함량을 갖는 수산화마그네슘 슬러리를 진공성형기에서 성형한다. 진공성형은 성형물에 미세기공 즉, 일종의 미세한 균열을 만들어 성형물의 비표면적을 높이는 기술로서 정수기의 부품인 세라믹필터의 제조에 이용되고 있다. 본 발명에서는 탈수한 슬러리를 바람직하게는 6-7kg/㎤ 의 진공압력으로 성형하여 원하는 비표면적을 갖도록 하여 활성도를 확보한다. 진공압력이 6kg/㎤ 미만의 경우에는 표면에 미세기공의 형성이 부족하여 원하는 활성도를 확보할 수 없으며, 진공압력이 7kg/㎤를 넘는 경우에는 너무 진공압력이 높아서 표면에 미세기공은 높아지나 상대적으로 내부기공이 적어져서 원하는 활성도를 확보하기가 어렵다.Magnesium hydroxide slurry having appropriate moisture content is molded in a vacuum molding machine. Vacuum molding is a technique for increasing the specific surface area of moldings by forming micropores, that is, a kind of fine cracks in moldings, and is used in the manufacture of ceramic filters, which are components of water purifiers. In the present invention, the dehydrated slurry is preferably formed at a vacuum pressure of 6-7 kg / cm 3 to have a desired specific surface area to ensure activity. If the vacuum pressure is less than 6kg / cm3, the formation of micropores on the surface is insufficient to ensure the desired activity. If the vacuum pressure is more than 7kg / cm3, the vacuum pressure is so high that the micropores on the surface are high. It is difficult to secure the desired activity due to less internal pores.

진공으로 성형할때 입자의 크기는 2-10mm로 하는 것이 바람직한다. 이 정도의 입자크기는 대충 겉보기 비중이 약 1.5-2.0g/㎠으로, 입자의 크기가 2mm 보다 작으면 해수나 강의 바닥에 근접하기 전에 용해되어 침전물과의 직접적인 반응을 유도하기가 어려우며 10mm이상 커지면 용해에 너무 많은 시간이 소요되는 문제가 있다.When forming in vacuum, the particle size is preferably 2-10 mm. This particle size is roughly 1.5-2.0 g / cm2 in apparent apparent density. If the particle size is smaller than 2mm, it is difficult to dissolve before approaching the bottom of seawater or river, and it is difficult to induce a direct reaction with the precipitate. There is a problem that takes too much time to dissolve.

적정한 크기로 성형한 입자를 건조하는데, 이때의 건조조건도 활성도에 직접적인 영향을 미친다. 건조조건은 100-180℃의 온도에서 60-180분으로 하는데, 건조온도가 100℃미만이거나 건조시간이 180분 보다 커지는 경우에는 건조시간이 길어져서 생산비가 커지고, 건조온도가 180℃보다 높아지는 경우에는 수산화물인 마그네슘 및 칼슘이 산화물(MgO, CaO)로 분해되어서 수중에서 유해물질 제거작용을 할 수 없게 된다.Drying the shaped particles to the appropriate size, the drying conditions also directly affect the activity. Drying conditions are 60-180 minutes at the temperature of 100-180 ℃, if the drying temperature is less than 100 ℃ or drying time is longer than 180 minutes, the drying time is longer, the production cost increases, the drying temperature is higher than 180 ℃ Magnesium and calcium, which are hydroxides, are decomposed into oxides (MgO, CaO), which prevents the removal of harmful substances in water.

이하, 본 발명을 실시예를 통하여 보다 구체적으로 설명한다.Hereinafter, the present invention will be described in more detail with reference to Examples.

[실시예 1]Example 1

종래의 침전물개선제인 수산화마그네슘, 고토계물질, 생석회와 본 발명의 침전물 개선제(활성도 150의 수산화칼슘:3중량%, 수용성철분:1중량%, 활성도 90의 수산화마그네슘:90중량%과 나머지 기타 불가피한 불순물)를 도 1과 같은 해수와 접촉시켜 해수의 화학조성, 외관의 변화 그리고 시료 접시에 남은 미용해 물질의 량을 조사한 다음, 그 결과를 표 2에 나타내었다. 시료의 중량변화와 화학조성은 7일 경과후 시료를 꺼내어 화학분석을 하였다. 방치후 생성물은 X선회절분석, Mg, Ca는 킬레이트 적정법, SO4는 크롬산바륨 비색법으로 분석하였다.Conventional sediment improvers magnesium hydroxide, clay soil material, quicklime and sediment improving agent of the present invention (calcium hydroxide of activity 150: 3% by weight, water-soluble iron: 1% by weight, magnesium hydroxide of activity 90: 90% by weight and other unavoidable impurities ) Was contacted with seawater as shown in FIG. 1 to investigate the chemical composition of the seawater, the change in appearance and the amount of undissolved substances remaining in the sample dish, and the results are shown in Table 2. The weight change and chemical composition of the sample were taken out after 7 days for chemical analysis. After standing, the product was analyzed by X-ray diffraction analysis, Mg, Ca for chelate titration, and SO4 for barium chromate colorimetric method.

시료sample 상부조직분석Upper tissue analysis 화학적성분Chemical composition 시료잔분(%)Sample Residue (%) 10일10 days 20일20 days 30일30 days 발명재Invention 분상Powder Mg2+, Ca2+ Mg 2+ , Ca 2+ 55 00 00 종래재Conventional 수산화마그네슘Magnesium hydroxide 분상-입상Figurine-Figurine Mg(OH)2, CaCO3 Mg (OH) 2 , CaCO 3 4040 3535 3535 고토계Goto system 분상-판상, 침상Bed-plate, couch Mg(OH)2, CaCO3,CaSO4·2H2OMg (OH) 2 , CaCO 3 , CaSO 4 2H 2 O 4040 4545 4545 생석회quicklime 분상-입상Figurine-Figurine CaCO3, CaSO4, 2H2OCaCO 3 , CaSO 4 , 2H 2 O 3030 3535 3535

표 2로 부터 알 수 있듯이, 본 발명재는 활성성분으로 되어 있어 단시일내 반응을 하여 같은 30일내 잔분인 미용해 물질이 남아 있지 않은데 반해, 종래의 개선제는 판상막 또는 입상막으로 미용해 물질이 30일후에도 남아 있어 저서생물을 고사시켜 어장을 황폐화시키고 있다.As can be seen from Table 2, the present invention is an active ingredient and reacts within a short period of time, so that the undissolved substance remaining in the same 30 days remains, whereas the conventional improver is a platelet or granular membrane. It remains even later, killing benthic creatures and ruining fisheries.

[실시예 2]Example 2

활성도 150의 수산화칼슘과 활성도 90의 수산화마그네슘의 배합비를 아래 표 2와 같이 조절하여 침전물의 중량변화를 알아 보았다. 이때, 수용성 철분은 3%이었고, 나머지는 기타 불가피한 불순물이었다. T-S량이 1.52ppm인 침전물에 대하여 침전물의 중량변화를 변화를 시험하였다.By adjusting the mixing ratio of the calcium hydroxide of activity 150 and the magnesium hydroxide of activity 90 as shown in Table 2 below, the weight change of the precipitate was examined. At this time, the water-soluble iron was 3%, the rest were other unavoidable impurities. The change in weight of the precipitate was tested for the precipitate having a T-S content of 1.52 ppm.

구분division 1One 22 33 44 55 66 수산화마그네슘 함량(중량%)Magnesium hydroxide content (% by weight) 8080 8585 9090 9393 9595 9898 수산화칼슘의 함량(중량%)Calcium hydroxide content (% by weight) 1010 55 33 3.53.5 44 1One 침전물 중량Sediment weight 5.25.2 4.94.9 4.54.5 4.44.4 4.254.25 4.104.10

표 3에서 알 수 있듯이, 수산화칼슘의 양이 5중량%이하로 하면 침전물의 양이 적어짐을 알 수 있다.As can be seen from Table 3, when the amount of calcium hydroxide is less than 5% by weight it can be seen that the amount of precipitate is less.

[실시예 3]Example 3

수산화칼슘:3중량%, 수용성철분:1중량%, 수산화마그네슘:90중량%과 나머지 기타 불가피한 불순물로 조성되는 침전물 개선제에 있어, 수산화칼슘과 수산화마그네슘의 활성도 변화에 따른 침전물중의 T-S변화를 알아보았다.In the precipitate improver composed of 3% by weight of calcium hydroxide, 1% by weight of water-soluble iron, 90% by weight of magnesium hydroxide and the rest of the unavoidable impurities, the T-S changes in the precipitates with the changes in the activity of calcium hydroxide and magnesium hydroxide were investigated.

구분division 1One 22 33 44 55 66 수산화칼슘의 활성도Calcium Hydroxide Activity -- 100100 150150 200200 250250 300300 수산화마그네슘의 활성도Activity of Magnesium Hydroxide -- 7070 9090 100100 120120 150150 침전물중의 T-S의 양(ppm)Amount of T-S in the precipitate (ppm) 1.521.52 1.491.49 1.491.49 1.501.50 1.511.51 1.511.51 진공성형조건과 건조조건Vacuum forming condition and drying condition 7kg/㎤-100℃×180분7kg / cm3-100 ℃ × 180 minutes 7kg/㎤-150℃×100분7kg / cm3-150 ℃ × 100 minutes 7kg/㎤-180℃×60분7kg / cm3-180 ℃ × 60 minutes 9kg/㎤-200℃×50분9kg / cm3-200 ℃ × 50 minutes 9kg/㎤-250℃×40분9kg / cm3-250 ℃ × 40 minutes

표 4에서 알 수 있듯이, 수산화칼슘의 활성도가 1200이하, 수산화마그네슘의 활성도가 100이하에서 침전물중의 T-S변화가 커짐을 알 수 있다.As can be seen from Table 4, it can be seen that the T-S change in the precipitate increases when the calcium hydroxide activity is 1200 or less and the magnesium hydroxide activity is 100 or less.

[실시예 4]Example 4

본 발명의 침전물 개선제를 실해역 현장(수심 10m)에 살포하여 환경영향 변화와 수질의 화학적 변화를 표 5에 나타내었다. 이때 사용된 침전물 개선제는 활성화도 90인 수산화마그네슘:90중량%, 활성화도 150인 수산화칼슘:3중량%, 수용성철분:3중량%, 나머지 불가피한 불순물로 조성되는 것을 이용하였다. 이 침전물 개선제는 수산화마그네슘 슬러리를 탈수한 다음에, 7kg/㎤의 진공압에서 직경 5mm이고 길이가 10mm인 원기둥상의 입자로 성형하고 이를 150℃에서 100분 동안 건조한 것이다.The sediment improver of the present invention was sprayed on the actual sea water field (depth of 10 m) to show the environmental impact change and the chemical change of the water quality in Table 5. At this time, the precipitate improving agent used was magnesium hydroxide having an activation degree of 90: 90% by weight, calcium hydroxide having an activation degree of 150: 3% by weight, water-soluble iron: 3% by weight, and used as an inevitable impurity. The precipitate improver is to dehydrate the magnesium hydroxide slurry and then to form cylindrical particles 5 mm in diameter and 10 mm in length at a vacuum pressure of 7 kg / cm 3 and dried at 150 ° C. for 100 minutes.

구분division 살포량(g/㎡)Spray amount (g / ㎡) 저부층Bottom layer 축적물의T-S(ppm)Accumulated T-S (ppm) 온도(℃)Temperature (℃) DO(ppm)DO (ppm) pHpH 발명재Invention 살포전Before spraying 200200 21.121.1 4.204.20 6.796.79 1.521.52 살포 40일후40 days after spraying 24.824.8 4.324.32 8.508.50 1.001.00 살포 55일후55 days after spraying 28.328.3 5.405.40 9.519.51 0.520.52 고토계Goto system 살포전Before spraying 200200 21.121.1 4.204.20 6.796.79 1.521.52 살포 40일후40 days after spraying 24.824.8 4.114.11 7.017.01 1.491.49 살포 55일후55 days after spraying 28.328.3 4.104.10 7.117.11 1.351.35 생석회quicklime 살포전Before spraying 800800 21.121.1 4.204.20 6.796.79 1.521.52 살포 40일후40 days after spraying 24.824.8 4.594.59 9.209.20 1.351.35 살포 55일후55 days after spraying 28.328.3 4.804.80 8.218.21 1.621.62 대조구역(침전물 개선제 적용안함)Control zone (no sediment improver applied) 살포전Before spraying 살포 안함Do not spray 21.121.1 4.204.20 6.796.79 1.521.52 살포 40일후40 days after spraying 24.824.8 4.104.10 6.726.72 1.501.50 살포 55일후55 days after spraying 28.328.3 4.054.05 6.706.70 1.531.53

표 5에서 알 수 있듯이, 본 발명재는 환경에 미치는 유해한 영향은 없으며, 오히려 저부층의 수질을 정화하고 축적물의 황화물(T-S;Total Sulphur, 오염측도를 나타냄)은 시일이 지남에 따라 감소되는 것으로 나타났다.As can be seen from Table 5, the present invention has no detrimental effect on the environment, rather it purifies the water quality of the bottom layer and shows that the sulfides of the deposits (TS: Total Sulfur, indicating pollution measure) decrease with time. .

상술한 바와 같이, 본 발명은 연안어장이나 강 또는 호수 등의 저부표면에 막을 형성하지 않기 때문에 저부에서 서식하는 수산생물의 고사 없고, 저부의 축적물이 부패로 인한 오염물질을 제거하고 수질을 정화하는 효과가 있는 것이다. 녹조 또는 적조방지를 지속적으로 효과를 발휘할 수 있고 그러한 효과를 발휘할 수 있도록 개선제의 성분을 활성화를 갖을 수 있는 제조방법의 특징이다.As described above, since the present invention does not form a film on the bottom surface of a coastal fishery, a river or a lake, there is no death of aquatic organisms living in the bottom, and the accumulation of the bottom removes contaminants due to decay and purifies the water quality. It is effective. It is a feature of the manufacturing method that can continuously exert the green algae or red tide preventive effect and have the activation of the components of the improver to exert such an effect.

Claims (6)

활성도 200이하의 활성수산화칼슘: 5중량%이하, 수용성 철분:0.1-1중량%, 나머지 활성도가 100이하의 활성수산화 마그네슘과 기타 불가피한 불순물로 조성되는 침전물 개선재.Active calcium hydroxide with an activity of 200 or less: 5% by weight or less, water-soluble iron: 0.1-1% by weight, a precipitate improving material composed of active magnesium hydroxide and other unavoidable impurities having a remaining activity of 100 or less. 해수마그네시아 제조공정에서 발생하는 수산화마그네슘 슬러리를 탈수하는 단계;Dehydrating the magnesium hydroxide slurry generated in the seawater magnesium production process; 탈수한 원료를 진공성형하여 입자로 만드는 단계;Vacuum molding the dehydrated raw material into particles; 성형된 입자를 건조하는 단계;를 포함하여 이루어지는 침전물 개선제의 제조방법.Drying the molded particles; Method of producing a precipitate improver comprising a. 제 2항에 있어서, 상기 탈수는 슬러리의 수분함량을 28-32%로 하는 것을 특징으로 하는 침전물 개선제의 제조방법.3. The method of claim 2, wherein the dehydration is a water content of the slurry of 28-32%. 제 2항에 있어서, 상기 진공성형은 6-7kg/㎤의 진공압으로 행함을 특징으로 하는 침전물 개선제의 제조방법.3. The method of claim 2, wherein the vacuum forming is performed at a vacuum pressure of 6-7 kg / cm < 3 >. 제 2항에 있어서, 상기 진공성형은 입자의 크기를 2-10mm로 하는 것을 특징으로 하는 침전물 개선제의 제조방법.The method of claim 2, wherein the vacuum forming is characterized in that the particle size of 2-10mm. 제 2항에 있어서, 상기 건조는 100-180℃의 온도에서 60-180분 동안 행함을 특징으로 하는 침전물 개선제의 제조방법.The method of claim 2, wherein the drying is performed for 60-180 minutes at a temperature of 100-180 ℃.
KR1020000018888A 2000-04-11 2000-04-11 modifier for precipitate and method for preparing it KR100339884B1 (en)

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