KR20150065272A - Removing agent of green tides and red tides - Google Patents

Abstract

The present invention relates to a removing agent composition for a red tide and a green tide using a by-product plentifully containing CaO, and more specifically, to a composition which is capable of reducing the amount of red clay which is a cause of destroying an ecosystem by using the by-product plentifully containing the CaO which does a sterilizing action, and of replacing the red clay. According to the present invention, the removing agent composition for a red tide and a green tide includes 5 to 300 parts by weight of an alkaline reagent with greater than or equal to 50% of calcium oxide (CaO) content, with respect to 100 parts by weight of incinerator bottom ash with greater than or equal to 40% of the calcium oxide (CaO) content, wherein the alkaline reagent is quicklime or dolomite plaster.

Description

Technical Field [0001] The present invention relates to a composition for removing red tides and green tones using byproducts containing a large amount of CaO,

The present invention relates to a red tide and algae removing composition using a byproduct containing a large amount of CaO. More particularly, the present invention relates to a red tide and algae removing composition using a byproduct containing a large amount of CaO, And a red tide and algae removing agent capable of replacing them.

Domestic dam reservoirs are experiencing difficulties in water resource management due to the occurrence of algae due to massive proliferation of cyanobacillus algae every year. Green algae from upstream of the reservoir are moved to the downstream and become stagnant for a long time, , Adverse effects on aquatic ecosystems, and landscape problems. The existing green algae abatement technology has many difficulties such as low efficiency, high cost and adverse effects on ecosystem as well as low throughput to be applied directly to the field water of the dam reservoir. Therefore, it can be used for effective management of water resources and water quality There is a limit to the environmental technology that can be achieved.

In addition, in recent years, large-scale aquaculture fish have been killed every year by red tide in the southern coast of Korea. As it is known that yellow loess is effective in the control of red tide, it began to spread a lot of loess since 1996 to prevent the spread of red tide and to reduce the damage of fish farms.

In Korea, some of the methods that have been attempted for the anti-foaming film control and harmful algae control are mostly physical / chemical technologies. Among these methods, when sedimentation is caused by loess, which is the most widely used due to economical efficiency, harmful algal creatures that have settled down in the waterfall are re-decayed, which deteriorates the natural self-purification ability, In the case of separating on the surface of the water, it is inefficient because it can be treated only in a locally limited area in a stopped place.

Methods for removing harmful algae from freshwater lakes and coastal waters off the coast of the world include sooting with soot and soils using loess, separating them on the surface of water, decomposing the harmful algae composed of organic matter using a heat source, A precaution for preventing and preventing the occurrence of harmful algae is used to prevent a vicious cycle of the bird.

Generally, physical control such as aquatic aeration, electromagnetic wave, and shielding film, chemical control using oxidant, coagulant, and biological control using bacteria, natural creatures, etc. are utilized for controlling harmful algae.

The chemical treatment method is widely used in domestic and overseas as a method to control harmful algae in a short time and mainly clay, quicklime, lime, coagulant, copper sulfate, chlorine and ozone are used.

It is necessary to develop such a solution, high-efficiency, low-cost, and environment-friendly red tide and greenhouse reduction technology.

DISCLOSURE OF THE INVENTION It is an object of the present invention to overcome the above-mentioned problems, and it is an object of the present invention to provide a method of reducing or eliminating the amount of yellow clay that causes destruction of an ecosystem by using a byproduct containing a large amount of CaO, Red tide and algae removers.

In order to solve the above technical problems, the red tide and algae eliminator composition according to the present invention is characterized in that an alkaline agent having a calcium oxide (CaO) content of 50% or more is added to 100 parts by weight of incineration residue having a calcium oxide (CaO) By weight, and the alkali agent is calcium oxide or dolomite plaster.

It is preferable that the incineration residue is any one or a mixture of two or more selected from the group consisting of coal ash, biomass incineration residue, paper sludge incineration residue, sewage sludge incineration residue, petro coke incineration residue, RDF incineration residue and RPF incineration residue.

The flocculant may further comprise 5 to 100 parts by weight of a flocculant based on 100 parts by weight of the incineration residue, wherein the flocculant is selected from the group consisting of starch, slaked lime, alum, aluminum sulfate, aluminum chloride, iron (III) It is preferable to use either one or a mixture of two or more.

Further, it is preferable that 10 to 1,000 parts by weight of precipitating agent is further added to 100 parts by weight of the incineration residue, and the sedimentation agent is any one or a mixture of two or more selected from the group consisting of loess, clay and sea clay.

The adsorbent may further contain 10 to 1,000 parts by weight of an adsorbent per 100 parts by weight of the incineration residue, and the adsorbent may be a steelmaking slag dust having a CaO content of 40% or more and an iron oxide (Fe ₂ O ₃ ) content of 10% Steel slag dust, KR dust, or a mixture of two or more thereof.

According to the present invention, it is possible to improve the problem of ecosystem destruction due to a large amount of clay spraying and the ineffective problem in controlling red tide and green tide when red tide and green tide are generated.

In particular, the present invention provides a low-priced high-performance red tanning agent capable of drastically reducing red tide and green algae by using a by-product containing a large amount of CaO that can greatly reduce or replace the amount of yellow clay, .

Hereinafter, the red tide and algae removing composition according to the present invention will be described in detail.

First, the components and action of the red tide and algae removing agent according to the present invention will be described.

The red tide and algae removing agent according to the present invention comprises 5 to 300 parts by weight of an alkali agent having a calcium oxide (CaO) content of 50% or more, based on 100 parts by weight of incineration residues having a calcium oxide (CaO) content of 40% or more. The alkali agent further includes at least one of burnt lime and dolomite plaster.

Yellow loess that is sprayed for red tide and green tide control can be deposited on the surface of the sea bed to promote acidification and to form a tough film layer in the bottom to block the supply of oxygen, thereby creating an anaerobic environment and inducing secondary pollution. In this way, it is expected that the incineration residue containing a large amount of calcium oxide in the sea devastated by the yellow clay spraying, and quicklime and dolomite plaster can be sprayed on the marine environment.

The interactions between the calcium oxide component and the contaminated marine environment indicate that Mg ions are contained in 1,300 ppm (0.13%) in seawater, so that Ca ions substitute for Mg ions to form magnesium hydroxide [Mg (OH) ₂ ] The dissolved Mg (OH) ₂ has an extremely low solubility of about 0.01 g / L and is hardly eluted in seawater. Therefore, Mg (OH) ₂ covers the sea surface and inhibits the action of sulfate-reducing bacteria.

CaO + H ₂ O - > Ca (OH) ₂

Ca (OH) ₂ - > Ca ^{2 +} + 2OH ^-

Ca ^{2 +} + ² OH ^- + Mg ^{2 +} -> Mg (OH) ₂ + Ca ^{2 +}

On the other hand, the undissolved calcium hydroxide (Ca (OH) ₂ ) slowly undergoes carbonation with carbon dioxide in the water.

Ca (OH) ₂ + CO ₂ -> CaCO ₃ + H ₂ O

Therefore, magnesium hydroxide (Mg (OH) ₂ ) and calcium carbonate (CaCO ₃ ) are produced after a lapse of time after spraying them.

In the case of large - scale incineration residues and calcium oxide (CaO) - rich residues and lime deposits in a long - term contaminated watershed, it may be worried that the pH will rise and affect the habitat of marine organisms. However, OH ^- Becomes insoluble Mg (OH) ₂ attached to Mg ions, so that the pH rise is extremely small.

In addition, phosphorus (P) ion and calcium (Ca) ion in the seawater reacted to form a white precipitate of calcium phosphate Ca ₂ (PO ₄ ) ₂ or calcium hydroxysilicate Ca ₅ (OH) (PO ₄ ) ₃ , .

3Ca ² + 2PO ₄ ^{2 -} -> Ca (PO ₄ ) ₂ ↓

5Ca ² + OH ^- + 3PO ₄ ^{3 -} -> Ca ₅ (OH) (PO ₄ ) ₃ ↓

The red tide and algae removing agent according to the present invention can minimize the damage caused by the generally used yellow clay spraying and can greatly reduce the amount of industrial chemicals such as expensive lime and dolomite plaster.

It is preferable that the incineration residue is any one or a mixture of two or more selected from the group consisting of coal ash, biomass incineration residue, paper sludge incineration residue, sewage sludge incineration residue, petro coke incineration residue, RDF incineration residue and RPF incineration residue.

Although the coal combustion fly ash produced in the coal-fired power plant generally has a CaO content of only 5%, it is not recycled as a concrete admixture because it has no exothermic and absorptive effect. However, the incineration residues containing a large amount of calcium oxide as described above are absorbed, And it is impossible to use it as a concrete admixture material. In the Korean Industrial Standard (KS), there is no standard for incineration residues with a high content of calcium oxide.

In the present invention, the incineration residue is preferably 40% or more of calcium oxide, and if it is less than 40%, the phosphorus adsorption capacity is lowered and the effect of removing red tide and green tide is insufficient. Incineration residues containing more than 40% of calcium oxide cause incineration residues with high calcium oxide content when incinerating sludge containing a large amount of limestone or a fluidized bed boiler of an in-bed desulfurization system that combines limestone.

In addition, the red tide and algae removing agent according to the present invention is characterized in that the calcium oxide (CaO) content is 50% or more to improve the ability to remove harmful algae such as red tide and green tide with respect to 100 parts by weight of incineration residue having a calcium oxide (CaO) It is preferable to further include at least one of quick lime and dolomite plaster which are alkaline agents.

The quicklime is a product obtained by calcining limestone at a high temperature and decarboxylating it and then processing the product into a powder of a predetermined particle size. It is generally obtained in the market and has a CaO content of 80% or more.

The dolomite plaster is a product obtained by calcining dolomite at a high temperature and decarboxylating it and then processing it into a powder having a predetermined particle size, which is generally obtained in the market, and CaO + MgO content is 80% or more.

The amount of the quicklime and the dolomite plaster is preferably 5 to 300 parts by weight based on 100 parts by weight of the incineration residue. If the amount is less than 5 parts by weight, the effect of removing red tide and green tide is insufficient. If the amount is more than 300 parts by weight, It is not economical.

The flocculant may be selected from the group consisting of starch, calcium hydroxide, alum, aluminum sulfate, aluminum chloride, iron (III) sulfate and iron (II) sulfate to enhance the flocculation effect of the red tide and algal remover. It is preferable that the flocculant is further contained in an amount of 5 to 100 parts by weight based on 100 parts by weight of the incineration residue.

When the amount of the flocculant is less than 5 parts by weight, the flocculant effect of the red tide and the green algae is not exhibited properly. If the flocculant is more than 100 parts by weight, the flocculant is excessively flocculated.

In addition, it is preferable that the sedimentation agent is further included to raise the sedimentation effect of the red tide and algal remover. The sedimentation agent may be any one selected from the group consisting of loess, general clay, and sea clay, It is preferable that 10 to 1,000 parts by weight of the precipitating agent is further included.

When the amount is less than 10 parts by weight, the adsorption and sedimentation effects of red tide and green algae are not exhibited properly. If it exceeds 1,000 parts by weight, adsorption of red tide and green algae is not performed properly and sedimentation rate is too fast.

In addition, it is preferable to further include an adsorbent for increasing the adsorption and sedimentation effect of the red tidy remover, wherein the adsorbent has a CaO content of at least 40% and an iron oxide (Fe ₂ O ₃ ) content of at least 10% , Steelmaking dust, KR (Kanvara Reactor) slag dust, and KR (Kanvara Reactor) dust are preferably included in an amount of 10 to 1,000 parts by weight based on 100 parts by weight of the incineration residue.

When the content of calcium oxide (CaO) is less than 40%, the adsorbing ability is lowered and the effect of removing red tide and green algae is insufficient and the content of iron oxide (Fe ₂ O ₃ ) is reduced to 10% , The specific gravity is low and sedimentation effect is lowered.

When the amount is less than 10 parts by weight, the adsorption and sedimentation effects of red tide and green algae are not exhibited properly. If the amount exceeds 1,000 parts by weight, adsorption of red tide and green algae is not performed properly and sedimentation rate is too fast.

Hereinafter, the performance and the performance of the red tide and algae removing agent according to the present invention are compared and analyzed.

Example  One

First, with respect to 100 parts by weight of Petro Coke incineration residues having a calcium oxide (CaO) content of 64% and a sulfuric acid (SO ₃ ) content of 23% generated in a fluidized-

And 20 parts by weight of quicklime having a calcium oxide component of 83% were uniformly mixed to prepare a red tide and algae removing agent.

50g was added to a 100L experimental tank containing red tide samples, and the mixture was gradually stirred for 1 minute to spread evenly. After 5 minutes, the supernatant was collected immediately after the precipitation was completed and the number of Cochlodinium polykrikoides remaining in the supernatant was confirmed.

Comparative Example  One

Yellow loess which is used for red tide control was obtained, dried, and ground to a particle size of 1 mm or less to prepare red tide and algae removers.

500 g was added to a 100 L experimental tank containing red tide samples, and the mixture was gradually stirred for 1 minute to spread evenly. After 5 minutes, the supernatant was collected immediately after the precipitation was completed and the number of Cochlodinium polykrikoides remaining in the supernatant was confirmed.

Example  2

With respect to 100 parts by weight of the paper sludge incineration residue having a calcium oxide (CaO) content of 48% generated in a furnace desulfurization type fluidized bed boiler,

The calcium oxide is 83% of dolomite, gypsum, 20 parts by weight, sulfuric acid Alumina 10 parts by weight, particle size plain clay 20 parts by weight of calcium oxide (CaO) content of 1mm or less 62%, iron oxide (Fe ₂ O ₃₎ content of 23% And 50 parts by weight of phosphorus steel dust were uniformly mixed to prepare a red tide and algae removing agent.

50g was added to a 100L experimental tank containing red tide samples, and the mixture was gradually stirred for 1 minute to spread evenly. After 5 minutes, the supernatant was collected immediately after the precipitation was completed and the number of Cochlodinium polykrikoides remaining in the supernatant was confirmed.

Comparative Example  2

First, 100 parts by weight of coal ash having a calcium oxide (CaO) content of 3.5% discharged from a general thermal power plant having a separate desulfurization unit was uniformly mixed with 100 parts by weight of ordinary clay having a particle diameter of 1 mm or less to prepare a red tide and algae removing agent Respectively.

500 g was added to a 100 L experimental tank containing red tide samples, and the mixture was gradually stirred for 1 minute to spread evenly. After 5 minutes, the supernatant was collected immediately after the precipitation was completed and the number of Cochlodinium polykrikoides remaining in the supernatant was confirmed.

Performance test methods and results

As shown in the table below, when the samples according to the examples and the comparative examples were prepared, the rate of bioremediation was 1/10 as compared with that of Comparative Example 1, but the rate of bioremediation was 3 times or more superior And the pH was 10 or more.

It is analyzed that the petrocoke incineration residue with high calcium oxide content and the rapid rise of pH and heat from the hydration of quicklime are the main mechanism of redox death. It is also analyzed that it has the advantage of fixing the nutrients that feed on red tide creatures and improving the acidified sea bed.

In Example 2, the dosage was 1/10 of that of Comparative Example 2, but the effect of blooming biodegradation was 5 times or more superior and the pH was 10 or more.

It was analyzed that the effect of coagulation and sedimentation was further accelerated by addition of hydrated sulfuric acid, general clay and steel dust as well as hydration heat and pH synergistic effect in Example 2.

In Comparative Example 2, it was found that when the coal ash and the clay having a low calcium oxide content of 3.5% were used for hydration, there was no release heat and the pH was not increased.

Sample type Input (g / L) Maximum disappearance rate (%) PH of supernatant Example 1 0.5 81.6 10.2 Comparative Example 1 10 26.4 6.8 Example 2 0.5 100.0 10.3 Comparative Example 2 10 18.2 7.0

Claims (5)

And 5 to 300 parts by weight of an alkali agent having a calcium oxide (CaO) content of 50% or more based on 100 parts by weight of the incineration residue having a calcium oxide (CaO) content of 40%
Wherein the alkaline agent is quicklime or dolomite plaster.
The method according to claim 1,
Characterized in that the incineration residue is any one or a mixture of two or more selected from the group consisting of coal ash, biomass incineration residue, paper sludge incineration residue, sewage sludge incineration residue, petro coke incineration residue, RDF incineration residue and RPF incineration residue And an antioxidant composition.
The method according to claim 1,
Further comprising 5 to 100 parts by weight of a flocculant based on 100 parts by weight of the incineration residue,
Wherein the coagulant is any one or a mixture of two or more selected from the group consisting of starch, lime, alum, aluminum sulfate, aluminum chloride, iron oxide (III) and iron sulfate (II).
The method according to claim 1,
Further comprising 10 to 1,000 parts by weight of a precipitating agent based on 100 parts by weight of the incineration residue,
Wherein the sedimentation accelerator is any one or a mixture of two or more selected from the group consisting of loess, clay, and sea clay.
The method according to claim 1,
Further comprising 10 to 1,000 parts by weight of an adsorbent per 100 parts by weight of the incineration residue,
The adsorbent may be any one selected from the group consisting of steel-making slag dust having a calcium oxide (CaO) content of 40% or more and iron oxide (Fe ₂ O ₃ ) content of 10% or more, steel making dust, KR slag dust, KR dust, ≪ / RTI > by weight of the composition.