WO2025127527A1 - Manufacturing material of sodium bicarbonate and gypsum and manufacturing method for sodium bicarbonate and gypsum using same - Google Patents
Manufacturing material of sodium bicarbonate and gypsum and manufacturing method for sodium bicarbonate and gypsum using same Download PDFInfo
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- WO2025127527A1 WO2025127527A1 PCT/KR2024/019098 KR2024019098W WO2025127527A1 WO 2025127527 A1 WO2025127527 A1 WO 2025127527A1 KR 2024019098 W KR2024019098 W KR 2024019098W WO 2025127527 A1 WO2025127527 A1 WO 2025127527A1
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D7/00—Carbonates of sodium, potassium or alkali metals in general
- C01D7/18—Preparation by the ammonia-soda process
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/46—Sulfates
Definitions
- the present invention relates to a raw material for manufacturing sodium bicarbonate and gypsum containing sodium sulfate, an impurity dissolution inhibitor, and impurities, and a method for manufacturing sodium bicarbonate and gypsum therefrom.
- Sodium bicarbonate ( NaHCO3 ) is used for various purposes such as glass manufacturing, water treatment, and food additives, and is also used to remove harmful gases such as sulfur oxides (SOx) emitted from various factories, thermal power plants, and incinerators.
- SOx sulfur oxides
- sintering plants of steel mills use sodium bicarbonate as an adsorbent to remove sulfur oxides, and the amount of sodium bicarbonate used is increasing every year to meet stricter environmental regulations.
- industrial sodium bicarbonate is imported from overseas, there is a problem that the price of sodium bicarbonate imports also varies greatly depending on overseas economic conditions.
- the present invention has been devised in consideration of the above circumstances, and can provide a method for manufacturing sodium bicarbonate and gypsum, which suppresses the generation of carbon dioxide and recycles sodium sulfate.
- the present invention can provide a raw material for manufacturing sodium bicarbonate and gypsum, in which the elution of impurities such as mercury and lead is suppressed, and a method for manufacturing sodium bicarbonate and gypsum using the raw material.
- the raw materials for manufacturing sodium bicarbonate and gypsum according to one embodiment of the present invention include sodium sulfate (Na 2 SO 4 ), an impurity dissolution inhibitor, and impurities.
- the above raw material may contain an impurity release inhibitor in an amount of 0.01 wt% to 5 wt% based on the total weight of the raw material.
- the above impurity release inhibitor may contain a sulfur-containing substance in an amount of 10 wt% or more and 90 wt% or less based on the total weight of the impurity release inhibitor.
- the above sulfur-containing material may be one selected from sodium bisulfide, sodium sulfide, and ICX (Sodium Cellulose Xanthate).
- the above impurities may include at least one selected from the group consisting of lead (Pb), copper (Cu), arsenic (As), mercury (Hg), cadmium (Cd), chromium (Cr), cyanide (CN), potassium (K), calcium (Ca), iron (Fe), and chlorine (Cl).
- a method for producing sodium bicarbonate and gypsum includes the steps of producing sodium bicarbonate (NaHCO 3 ) by carbonating a raw material including sodium sulfate (Na 2 SO 4 ), an impurity release inhibitor, and impurities; and the step of producing gypsum (CaSO 4 ) using a waste liquid generated in the step of producing the sodium bicarbonate, wherein the impurity release inhibitor includes a sulfur (S)-containing substance.
- the above raw material may contain an impurity release inhibitor in an amount of 0.01 wt% to 5 wt% based on the total weight of the raw material.
- the above impurity release inhibitor may contain a sulfur-containing substance in an amount of 10 wt% or more and 90 wt% or less based on the total weight of the impurity release inhibitor.
- the above sulfur-containing material may be one selected from sodium bisulfide, sodium sulfide, and ICX (Sodium Cellulose Xanthate).
- the above impurities may include at least one selected from the group consisting of lead (Pb), copper (Cu), arsenic (As), mercury (Hg), cadmium (Cd), chromium (Cr), cyanide (CN), potassium (K), calcium (Ca), iron (Fe), and chlorine (Cl).
- the step of manufacturing the above-mentioned sodium bicarbonate may include a step of manufacturing a mixture by dissolving desulfurization waste in water and then adding an impurity dissolution inhibitor; a step of obtaining a raw material by separating the mixture into solid/liquid; and a step of manufacturing the sodium bicarbonate by carbonating the raw material by adding ammonia water and carbon dioxide to the raw material.
- the step of manufacturing the gypsum may include a step of adding a calcium-containing material to the waste liquid to obtain a slurry; a step of removing ammonia from the slurry and then adding an acidic solution to obtain a second mixture; and a step of separating the second mixture into solid/liquid to manufacture the gypsum.
- the method for manufacturing sodium bicarbonate and gypsum using the sodium bicarbonate and gypsum manufacturing raw materials of the present invention it is possible to have the effect of preventing impurities such as mercury (Hg) and lead (Pb) from being eluted from waste generated in the process of manufacturing sodium bicarbonate and gypsum. Accordingly, since designated waste can be treated as general waste, a reduction in waste disposal costs can be expected.
- impurities such as mercury (Hg) and lead (Pb)
- Figure 1 is a flow chart schematically illustrating a method for manufacturing sodium bicarbonate and gypsum according to one embodiment of the present invention.
- the present invention relates to a method for producing sodium bicarbonate and gypsum from a raw material containing sodium sulfate and an impurity dissolution inhibitor.
- Flue gases from steel mills and sintering plants contain sulfur oxides (SOx), and when desulfurization treatment is performed using sodium bicarbonate to remove the sulfur oxides, waste desulfurization agents are generated.
- SOx sulfur oxides
- This desulfurization method using sodium bicarbonate has the advantage of increasing desulfurization efficiency and reducing chemical costs, as one H2O and one CO2 are released from two sodium bicarbonate units by the heat of the flue gas, thereby activating them into Na2CO3 , which has a larger contact area.
- Mangcho contains sodium, it is possible to produce sodium bicarbonate from Mangcho, and since the pH is relatively high, it is easy to dissolve carbon dioxide ( CO2 ) required in the sodium bicarbonate production process.
- CO2 carbon dioxide
- the solubility of impurities including mercury and lead according to temperature is shown in Table 1.
- the solubility shown in Table 1 represents the mass (g) of the substance dissolved per 100 mL of water.
- mercury chloride and lead chloride have high solubility. Mercury is classified as designated waste when it is dissolved at 0.005 mg/L or more, and lead is classified as designated waste when it is dissolved at 3 mg/L or more.
- mercury sulfide and lead sulfide have very low solubility and are hardly dissolved.
- the content of mercury and lead inside the waste desulfurizer is in ppm, and the amount of sulfide ion injected is also small.
- the injected sulfide ion to react well with the mercury ion (Hg 2+ ) and lead ion (Pb 2+ ) present in the solution, it is necessary to inject sulfide ion when dissolving the waste desulfurizer, or to inject it mixed with other substances in the raw material.
- the method for producing sodium bicarbonate and gypsum of the present invention comprises the steps of producing sodium bicarbonate (NaHCO 3 ) by carbonating a raw material including sodium sulfate (Na 2 SO 4 ), an impurity dissolution inhibitor, and impurities; and the step of producing gypsum (CaSO 4 ) by using a waste liquid generated in the step of producing the sodium bicarbonate.
- the desulfurization waste including the desulfurization agent and the nitrate can be dissolved in a dissolving agent to manufacture a solution.
- the dissolving agent can be water ( H2O ).
- mercuric chloride and lead chloride with high solubility can exist in the solution in the form of ions of mercury (Hg2 + ) and lead (Pb2 + ).
- an impurity release inhibitor can be added to the solution and stirred.
- the impurity release inhibitor includes a sulfur (S)-containing substance.
- sulfur-containing substances contain sulfide ions (S 2- )
- an impurity dissolution inhibitor is added to the solution, mercury sulfide and lead sulfide may be generated.
- the solution must be alkaline for the above-mentioned mercury sulfide and lead sulfide generation reaction to occur easily.
- the waste desulfurization agent is alkaline (pH>9), which provides good conditions for generating mercury sulfide and lead sulfide.
- the above raw material contains sodium sulfate (Na 2 SO 4 ), an impurity dissolution inhibitor, and impurities.
- the above impurity release inhibitor may contain 10 wt% or more and 100 wt% or less of a sulfur (S)-containing substance.
- the above sulfur-containing material may be one selected from sodium bisulfide, sodium sulfide, and ICX (Sodium Cellulose Xanthate).
- Sulfide ions can exist in various forms. Considering the purity of sodium bisulfide, sodium bisulfide (NaHS), sodium sulfide (Na 2 S), and ICX (Sodium Cellulose Xanthate) have the advantage of being able to use sodium ions as a sodium bisulfide raw material.
- the above impurities may include at least one selected from the group consisting of sodium sulfate ( Na2SO4 ), lead (Pb), copper (Cu), arsenic (As), mercury (Hg), cadmium (Cd), chromium (Cr), cyanide (CN), potassium (K), calcium (Ca), iron (Fe), and chlorine (Cl).
- the method for producing sodium bicarbonate and gypsum of the present invention includes a step of carbonating a raw material to produce sodium bicarbonate (NaHCO 3 ).
- Ammonia water and carbon dioxide can be added to the raw material, reacted in a carbonation reactor to obtain a slurry, and the slurry can be separated into solid and liquid to obtain a solid and a waste liquid.
- the solid can be washed and dried to produce sodium bicarbonate.
- the purity of the sodium bicarbonate produced from the step of producing the sodium bicarbonate of the present invention can be 97% or more, and the yield of the sodium bicarbonate can be 75% or more.
- primary waste containing 3 mg/L or less of the above-mentioned impurities may be generated.
- the impurity content in the primary waste is 3 mg/L or less, the leakage of toxic metals harmful to the human body can be suppressed, and the cost of waste disposal can be reduced.
- secondary waste containing the impurities of 1.1 mg/L or less may be generated.
- the impurity content in the secondary waste is 1.1 mg/L or less, the leakage of toxic metals harmful to the human body can be suppressed, and the cost of waste disposal can be reduced.
- the method for producing sodium bicarbonate and gypsum of the present invention includes a step of producing gypsum (CaSO 4 ) using waste liquid generated in the step of producing the sodium bicarbonate.
- the step of manufacturing the gypsum may include a step of adding a calcium-containing material to the waste liquid to obtain a slurry.
- the calcium-containing material may be quicklime.
- an acidic solution may be added and stirred to obtain a second mixture.
- the acidic solution may be a sulfuric acid aqueous solution.
- the slurry may be separated into solid and liquid to obtain a second solid and a second waste liquid.
- the second solid may be mixed again, and then a sulfuric acid aqueous solution may be added and stirred to obtain a third mixture. Thereafter, the second mixture or the third mixture may be separated into solid and liquid to obtain gypsum and waste water.
- the purity of the gypsum manufactured from the step of manufacturing the gypsum of the present invention can be 95% or more, and the yield of the gypsum can be 75% or more.
- a solution was prepared by adding 99.93 g of desulfurized waste and 200 mL of water and stirring at 40°C for 1 hour.
- sodium sulfide ( Na2S ) was added as an impurity dissolution inhibitor, and 0.7 g of sodium sulfide ( Na2S ) was added so that the weight ratio of sodium sulfide was 0.7 wt% based on the sum of the masses of the desulfurized waste and sodium sulfide, and additional stirring was performed at 40°C for 1 hour. After stirring, the mixture was separated into solid and liquid to obtain solid desulfurized waste (primary waste) and raw material (sodium dissolution solution).
- the raw material manufacturing process was repeated until 100 g of primary waste was obtained.
- the amount of lead (Pb) in the residue was confirmed using the ICP (Inductively Coupled Plasma) method, and the amount of mercury (Hg) was confirmed using the AA (Atomic Absorption) method.
- the results of the mercury (Hg) and lead (Pb) extraction experiments for 100 g of primary waste are shown in Table 2.
- the yield and purity of the sodium bicarbonate are shown in Table 3.
- the yield of the sodium bicarbonate was calculated based on the Na + mol of the waste desulfurizer and the produced sodium bicarbonate.
- the purity of the sodium bicarbonate was measured using ICP equipment and XRD (X-ray Powder Diffraction) equipment.
- the above second waste liquid was heated to 80°C and aerated using an inert gas to recover NH3 within the slurry.
- the second waste liquid from which NH3 was removed by aeration was mixed with the second solid obtained after the solid/liquid separation, and 110 g of a 30 wt% sulfuric acid aqueous solution was added and stirred. Thereafter, solid/liquid separation was performed to obtain gypsum and waste water.
- the yield and purity of gypsum are shown in Table 4.
- the gypsum yield was calculated based on the SO 4 2- mol of the waste desulfurizer and the produced gypsum.
- the gypsum yield was measured by ICP, and the purity of gypsum was measured by XRD.
- the amount of lead (Pb) in the residue was confirmed using the ICP method, and the amount of mercury (Hg) was confirmed using the AA method.
- the results of the mercury (Hg) and lead (Pb) elution experiments for 100 g of secondary waste are shown in Table 5.
- Sodium bicarbonate and gypsum were manufactured in the same manner as in Example 1, except that 98.7, 98, 97.7, and 96.7 g of desulfurized waste were added, respectively, and 1.3, 2.0, 2.3, and 3.3 g of sodium sulfide were added, respectively.
- Sodium bicarbonate and gypsum were manufactured in the same manner as in Example 1, except that 100 g of desulfurized waste was added and sodium sulfide was not added.
- mercury is detected at 0.005 mg/L or less and lead is detected at 3 mg/L or less in the primary wastes of Examples 1 to 5.
- Example 1 0.7 98.3 80
- Example 2 1.3 98.2 79
- Example 3 2.0 97.9 81
- Example 4 2.3 98.1 78
- Example 5 3.3 99.1 77
- Example 1 Na 2 S (wt%) Hg (mg/L) Pb (mg/L) Comparative Example 1 0.0 0.0623 2.7922 Example 1 0.7 0.0122 1.0022 Example 2 1.3 0.0015 0.0556 Example 3 2.0 Not detected Not detected Example 4 2.3 Not detected Not detected Example 5 3.3 Not detected Not detected
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Abstract
Description
본 발명은 황산나트륨, 불순물 용출억제제 및 불순물을 포함하는 중조 및 석고의 제조 원료 및 이로부터 중조 및 석고를 제조하는 방법에 관한 것이다.The present invention relates to a raw material for manufacturing sodium bicarbonate and gypsum containing sodium sulfate, an impurity dissolution inhibitor, and impurities, and a method for manufacturing sodium bicarbonate and gypsum therefrom.
중조(탄산수소 나트륨, NaHCO3)는 유리제조, 수처리, 식품 첨가제등으로 다양한 용도로 사용되고 있으며, 각종 공장, 화력발전소, 소각장에서 배출되는 황산화물(SOx)과 같은 유해가스 제거시에도 사용되고 있다. 현재 제철소 소결공장에서는 황산화물을 제거하기 위하여 중조를 흡착제로 사용하고 있으며, 매년 엄격해지는 환경 규제를 맞추기 위하여 중조의 사용양도 늘어나고 있는 추세이다. 산업용 중조를 해외에서 수입하는 경우 해외 경제 상황에 따라서 중조 수입 가격 또한 큰 폭으로 변화하는 문제가 있다.Sodium bicarbonate ( NaHCO3 ) is used for various purposes such as glass manufacturing, water treatment, and food additives, and is also used to remove harmful gases such as sulfur oxides (SOx) emitted from various factories, thermal power plants, and incinerators. Currently, sintering plants of steel mills use sodium bicarbonate as an adsorbent to remove sulfur oxides, and the amount of sodium bicarbonate used is increasing every year to meet stricter environmental regulations. When industrial sodium bicarbonate is imported from overseas, there is a problem that the price of sodium bicarbonate imports also varies greatly depending on overseas economic conditions.
중조를 활용하여 황산화물을 제거하는 반응에서는 이산화탄소 및 망초(황산나트륨, Na2SO4)가 발생하는데, 현재 이를 그대로 매립하고 있어 처리 비용 및 2차 환경 문제가 야기되고 있다. 따라서 망초 재생에 관한 기술 개발이 시급한 상황이다.In the reaction that removes sulfur oxides using sodium bicarbonate, carbon dioxide and sodium sulfate (sodium sulfate, Na2SO4 ) are generated, and currently, they are being buried as they are , causing disposal costs and secondary environmental problems. Therefore, the development of technology for sodium sulfate regeneration is urgent.
망초 폐기물을 중조로 재생시키면 일부 폐기물이 발생되며 내부에는 수은(Hg) 및 납(Pb)등 불순물이 존재한다. 공정 중 발생하는 폐기물은 추가적인 처리를 거치지 않으면 지정폐기물로 분류된다. 현재 시행되고 있는 폐기물 관리법에 따르면 공정시험법 기준 수은은 0.005 mg/L 이하, 납은 3 mg/L 이하로 용출되어야 일반 폐기물로 분류된다. 이들은 인체에 유해한 작용을 일으키는 독성 금속으로 누출을 억제시켜야 하며, 용해도가 낮은 물질로 전환하여 매립 및 보관해야 한다.When the waste from the smelting process is regenerated, some waste is generated, and impurities such as mercury (Hg) and lead (Pb) exist inside. The waste generated during the process is classified as designated waste if it is not further processed. According to the current waste management law, mercury must be dissolved at 0.005 mg/L or less and lead must be dissolved at 3 mg/L or less according to the process test method to be classified as general waste. These are toxic metals that cause harmful effects on the human body, so leakage must be prevented, and they must be converted to substances with low solubility and buried and stored.
본 발명은 상기와 같은 실정을 감안하여 안출된 것으로, 이산화탄소의 발생을 억제하고, 망초(황산나트륨)를 재활용하는, 중조 및 석고 제조방법을 제공할 수 있다.The present invention has been devised in consideration of the above circumstances, and can provide a method for manufacturing sodium bicarbonate and gypsum, which suppresses the generation of carbon dioxide and recycles sodium sulfate.
본 발명은 수은 및 납 등의 불순물의 용출이 억제된, 중조 및 석고 제조 원료 및 이를 이용한 중조 및 석고 제조방법을 제공할 수 있다.The present invention can provide a raw material for manufacturing sodium bicarbonate and gypsum, in which the elution of impurities such as mercury and lead is suppressed, and a method for manufacturing sodium bicarbonate and gypsum using the raw material.
본 발명의 일 구현예에 따른 중조 및 석고의 제조 원료는 황산나트륨(Na2SO4), 불순물 용출억제제 및 불순물을 포함한다.The raw materials for manufacturing sodium bicarbonate and gypsum according to one embodiment of the present invention include sodium sulfate (Na 2 SO 4 ), an impurity dissolution inhibitor, and impurities.
상기 원료는 원료 전체 중량을 기준으로 불순물 용출억제제를 0.01 중량% 이상 5 중량% 이하를 포함할 수 있다.The above raw material may contain an impurity release inhibitor in an amount of 0.01 wt% to 5 wt% based on the total weight of the raw material.
상기 불순물 용출억제제는 불순물 용출억제제 전체 중량을 기준으로 황 함유 물질을 10 중량% 이상 90 중량% 이하를 포함할 수 있다.The above impurity release inhibitor may contain a sulfur-containing substance in an amount of 10 wt% or more and 90 wt% or less based on the total weight of the impurity release inhibitor.
상기 황 함유물질은 황화수소나트륨, 황화나트륨 및 ICX(Sodium Cellulose Xanthate) 중에서 선택된 1종일 수 있다.The above sulfur-containing material may be one selected from sodium bisulfide, sodium sulfide, and ICX (Sodium Cellulose Xanthate).
상기 불순물은 납 (Pb), 구리(Cu), 비소(As), 수은 (Hg), 카드뮴(Cd), 크롬(Cr), 시안(CN), 칼륨 (K), 칼슘 (Ca), 철 (Fe), 염소 (Cl)로 이루어진 그룹으로부터 선택되는 적어도 1종을 포함할 수 있다.The above impurities may include at least one selected from the group consisting of lead (Pb), copper (Cu), arsenic (As), mercury (Hg), cadmium (Cd), chromium (Cr), cyanide (CN), potassium (K), calcium (Ca), iron (Fe), and chlorine (Cl).
본 발명의 다른 구현예에 따른 중조 및 석고의 제조방법은 황산나트륨(Na2SO4), 불순물 용출억제제 및 불순물을 포함하는 원료를 탄산화하여 중조(NaHCO3)를 제조하는 단계; 및 상기 중조를 제조하는 단계에서 발생하는 폐액을 이용하여 석고(CaSO4)를 제조하는 단계를 포함하고, 상기 불순물 용출억제제는 황(S) 함유 물질을 포함한다.According to another embodiment of the present invention, a method for producing sodium bicarbonate and gypsum includes the steps of producing sodium bicarbonate (NaHCO 3 ) by carbonating a raw material including sodium sulfate (Na 2 SO 4 ), an impurity release inhibitor, and impurities; and the step of producing gypsum (CaSO 4 ) using a waste liquid generated in the step of producing the sodium bicarbonate, wherein the impurity release inhibitor includes a sulfur (S)-containing substance.
상기 원료는 원료 전체 중량을 기준으로 불순물 용출억제제를 0.01 중량% 이상 5 중량% 이하를 포함할 수 있다.The above raw material may contain an impurity release inhibitor in an amount of 0.01 wt% to 5 wt% based on the total weight of the raw material.
상기 불순물 용출억제제는 불순물 용출억제제 전체 중량을 기준으로 황 함유 물질을 10 중량% 이상 90 중량% 이하를 포함할 수 있다.The above impurity release inhibitor may contain a sulfur-containing substance in an amount of 10 wt% or more and 90 wt% or less based on the total weight of the impurity release inhibitor.
상기 황 함유물질은 황화수소나트륨, 황화나트륨 및 ICX(Sodium Cellulose Xanthate) 중에서 선택된 1종일 수 있다.The above sulfur-containing material may be one selected from sodium bisulfide, sodium sulfide, and ICX (Sodium Cellulose Xanthate).
상기 불순물은 납 (Pb), 구리(Cu), 비소(As), 수은 (Hg), 카드뮴(Cd), 크롬(Cr), 시안(CN), 칼륨 (K), 칼슘 (Ca), 철 (Fe), 염소 (Cl)로 이루어진 그룹으로부터 선택되는 적어도 1종을 포함할 수 있다.The above impurities may include at least one selected from the group consisting of lead (Pb), copper (Cu), arsenic (As), mercury (Hg), cadmium (Cd), chromium (Cr), cyanide (CN), potassium (K), calcium (Ca), iron (Fe), and chlorine (Cl).
상기 중조를 제조하는 단계에서, 상기 불순물을 3 mg/L 이하 포함하는 1차 폐기물이 발생할 수 있다.In the step of manufacturing the above-mentioned sodium bicarbonate, primary waste containing 3 mg/L or less of the above-mentioned impurities may be generated.
상기 석고를 제조하는 단계에서, 상기 불순물을 1.1 mg/L 이하 포함하는 2차 폐기물이 발생할 수 있다.In the step of manufacturing the above plaster, secondary waste containing 1.1 mg/L or less of the above impurities may be generated.
상기 중조를 제조하는 단계는, 탈황 폐기물을 물에 용해한 뒤 불순물 용출억제제를 투입하여 혼합물을 제조하는 단계; 혼합물을 고/액 분리하여 원료를 얻는 단계; 및 원료에 암모니아수 및 이산화탄소를 투입하여 원료를 탄산화하여 중조를 제조하는 단계를 포함할 수 있다.The step of manufacturing the above-mentioned sodium bicarbonate may include a step of manufacturing a mixture by dissolving desulfurization waste in water and then adding an impurity dissolution inhibitor; a step of obtaining a raw material by separating the mixture into solid/liquid; and a step of manufacturing the sodium bicarbonate by carbonating the raw material by adding ammonia water and carbon dioxide to the raw material.
상기 석고를 제조하는 단계는, 상기 폐액에 칼슘 함유 물질을 투입하여 슬러리를 얻는 단계; 상기 슬러리에서 암모니아를 제거한 후, 산성 용액을 추가하여 제2 혼합물을 얻는 단계; 및 제2 혼합물을 고/액 분리하여 석고를 제조하는 단계를 포함할 수 있다.The step of manufacturing the gypsum may include a step of adding a calcium-containing material to the waste liquid to obtain a slurry; a step of removing ammonia from the slurry and then adding an acidic solution to obtain a second mixture; and a step of separating the second mixture into solid/liquid to manufacture the gypsum.
본 발명의 중조 및 석고 제조 원료를 사용한 중조 및 석고 제조방법에 따르면, 중조 및 석고를 제조하는 과정에서 발생한 폐기물에 수은(Hg) 및 납(Pb)등의 불순물이 용출되지 않는 효과를 가질 수 있다. 이에, 지정 폐기물을 일반폐기물로 처리 가능해짐에 따라, 폐기물 처리 비용 절감 효과를 기대 할 수 있다.According to the method for manufacturing sodium bicarbonate and gypsum using the sodium bicarbonate and gypsum manufacturing raw materials of the present invention, it is possible to have the effect of preventing impurities such as mercury (Hg) and lead (Pb) from being eluted from waste generated in the process of manufacturing sodium bicarbonate and gypsum. Accordingly, since designated waste can be treated as general waste, a reduction in waste disposal costs can be expected.
도 1은 본 발명의 일 실시예에 따른 중조 및 석고의 제조방법을 개략적으로 나타낸 흐름도이다.Figure 1 is a flow chart schematically illustrating a method for manufacturing sodium bicarbonate and gypsum according to one embodiment of the present invention.
이하, 다양한 실시예를 참조하여 본 발명의 바람직한 실시 형태를 설명한다. 그러나, 본 발명의 실시 형태는 여러 가지 다른 형태로 변형될 수 있으며, 본 발명의 범위가 이하 설명하는 실시 형태로 한정되는 것은 아니다.Hereinafter, preferred embodiments of the present invention will be described with reference to various examples. However, the embodiments of the present invention may be modified in various other forms, and the scope of the present invention is not limited to the embodiments described below.
본 발명은 황산나트륨 및 불순물 용출억제제를 포함하는 원료로부터 중조 및 석고를 제조하는 방법에 관한 것이다.The present invention relates to a method for producing sodium bicarbonate and gypsum from a raw material containing sodium sulfate and an impurity dissolution inhibitor.
제철소 소결공장의 배가스 등에는 황산화물(SOx) 성분이 포함되어 있으며, 상기 황산화물을 제거하기 위하여 중조를 이용하여 탈황처리 할 경우 폐탈황제가 발생한다. 이와 같은 중조를 이용한 탈황 방식은 배가스의 열에 의해 2개의 중조에서 1개의 H2O와 1개의 CO2가 빠져나가면서 더 많은 접촉 면적을 갖는 Na2CO3로 활성화되어 탈황효율의 증가와 약품비용의 절감효과를 얻을 수 있는 장점이 있다.Flue gases from steel mills and sintering plants contain sulfur oxides (SOx), and when desulfurization treatment is performed using sodium bicarbonate to remove the sulfur oxides, waste desulfurization agents are generated. This desulfurization method using sodium bicarbonate has the advantage of increasing desulfurization efficiency and reducing chemical costs, as one H2O and one CO2 are released from two sodium bicarbonate units by the heat of the flue gas, thereby activating them into Na2CO3 , which has a larger contact area.
2NaHCO3 (s) a Na2CO3 (s) + CO2 (g) + H2O (g)2NaHCO 3 (s) a Na 2 CO 3 (s) + CO 2 (g) + H 2 O (g)
Na2CO3 (s) + SO2 (g) + 1/2O2 (g) a Na2SO4 (s) + CO2 (g)Na 2 CO 3 (s) + SO 2 (g) + 1/2O 2 (g) a Na 2 SO 4 (s) + CO 2 (g)
다만, 중조를 이용한 탈황 방식에서는 상기 반응식에 나타낸 것과 같이, 이산화탄소가 배출된다. 또한, 중조를 이용하여 황산화물을 제거하면 망초(황산나트륨, Na2SO4)로 전환된 폐기물이 발생된다.However, in the desulfurization method using sodium bicarbonate, carbon dioxide is emitted as shown in the reaction formula above. In addition, when sulfur oxides are removed using sodium bicarbonate, waste converted to sodium sulfate (sodium sulfate, Na 2 SO 4 ) is generated.
망초는 나트륨을 함유하고 있어 망초로부터 중조 생산이 가능하며, pH가 상대적으로 높아 중조 생산 과정에서 필요한 이산화탄소(CO2)를 용해시키기도 용이하다. 이와 같이 망초 폐기물을 활용하여 중조를 재생시키게 되면 폐기물 발생양 최소화, 이산화탄소 저감을 통한 탄소 중립, 중조 내부 순환을 통한 조업 안정화 등 다양한 문제들을 한 번에 해결할 수 있다.Since Mangcho contains sodium, it is possible to produce sodium bicarbonate from Mangcho, and since the pH is relatively high, it is easy to dissolve carbon dioxide ( CO2 ) required in the sodium bicarbonate production process. By utilizing Mangcho waste to regenerate sodium bicarbonate in this way, various problems can be solved at once, such as minimizing waste generation, achieving carbon neutrality through carbon dioxide reduction, and stabilizing operations through internal circulation of sodium bicarbonate.
폐탈황제 내부에는 수은(Hg) 및 납(Pb)이 존재하고 있으며, 중조 및 석고 생산 공정 중 발생되는 폐기물 내부에는 염화수은(HgCl2) 및 염화납(PbCl2) 형태로 존재하고 있다. 수은 및 납을 포함하는 불순물 물질의 온도에 따른 용해도를 표 1에 나타내었다. 표 1에 나타난 용해도는 물 100 mL 당 용해되는 물질의 질량(g)을 나타낸다.Mercury (Hg) and lead (Pb) exist inside the waste desulfurizer, and they exist in the form of mercury chloride (HgCl 2 ) and lead chloride (PbCl 2 ) in the waste generated during the sodium bicarbonate and gypsum production processes. The solubility of impurities including mercury and lead according to temperature is shown in Table 1. The solubility shown in Table 1 represents the mass (g) of the substance dissolved per 100 mL of water.
표 1에서 확인할 수 있는 것과 같이, 염화수은 및 염화납은 용해도가 높다. 수은은 0.005 mg/L 이상, 납은 3 mg/L 이상 용출되는 경우 지정폐기물로 분류된다.As can be seen in Table 1, mercury chloride and lead chloride have high solubility. Mercury is classified as designated waste when it is dissolved at 0.005 mg/L or more, and lead is classified as designated waste when it is dissolved at 3 mg/L or more.
한편, 표 1에서 확인할 수 있는 것과 같이, 황화수은 및 황화납은 용해도가 매우 낮아 거의 용출되지 않는다.Meanwhile, as can be seen in Table 1, mercury sulfide and lead sulfide have very low solubility and are hardly dissolved.
폐탈황제 내부에 존재하는 수은 및 납의 함량은 ppm 단위이며, 투입되는 황화이온의 양도 소량이다. 투입되는 황화이온이 용액에 존재하는 수은 이온(Hg2+) 및 납 이온(Pb2+)과 잘 반응할 수 있게 하기 위해서는, 폐탈황제 용해 시 황화이온을 투입하거나, 원료에 기타 물질과 섞어 투입할 필요가 있다.The content of mercury and lead inside the waste desulfurizer is in ppm, and the amount of sulfide ion injected is also small. In order for the injected sulfide ion to react well with the mercury ion (Hg 2+ ) and lead ion (Pb 2+ ) present in the solution, it is necessary to inject sulfide ion when dissolving the waste desulfurizer, or to inject it mixed with other substances in the raw material.
본 발명의 중조 및 석고의 제조방법은 황산나트륨(Na2SO4), 불순물 용출억제제 및 불순물을 포함하는 원료를 탄산화하여 중조(NaHCO3)를 제조하는 단계; 및 상기 중조를 제조하는 단계에서 발생하는 폐액을 이용하여 석고(CaSO4)를 제조하는 단계를 포함한다.The method for producing sodium bicarbonate and gypsum of the present invention comprises the steps of producing sodium bicarbonate (NaHCO 3 ) by carbonating a raw material including sodium sulfate (Na 2 SO 4 ), an impurity dissolution inhibitor, and impurities; and the step of producing gypsum (CaSO 4 ) by using a waste liquid generated in the step of producing the sodium bicarbonate.
상기 원료를 제조하기 위해서는, 먼저 폐탈황제 및 망초를 포함하는 탈황 폐기물을 용출제에 용해시켜 용액을 제조할 수 있다. 상기 용출제는 물(H2O)일 수 있다. 탈황 폐기물을 물에 용해시키면, 용해도가 높은 염화수은 및 염화납은 수은(Hg2+) 및 납(Pb2+)의 이온형태로 용액에 존재할 수 있다.In order to manufacture the above raw material, first, the desulfurization waste including the desulfurization agent and the nitrate can be dissolved in a dissolving agent to manufacture a solution. The dissolving agent can be water ( H2O ). When the desulfurization waste is dissolved in water, mercuric chloride and lead chloride with high solubility can exist in the solution in the form of ions of mercury (Hg2 + ) and lead (Pb2 + ).
그 후 용액에 불순물 용출억제제를 투입하여 교반할 수 있다. 불순물 용출억제제는 황(S) 함유 물질을 포함한다.After that, an impurity release inhibitor can be added to the solution and stirred. The impurity release inhibitor includes a sulfur (S)-containing substance.
황 함유 물질은 황화 이온(S2-)을 포함하기 때문에, 용액에 불순물 용출억제제를 투입하면 황화수은 및 황화납이 생성될 수 있다. 용액이 염기성을 띄어야 상기 황화수은 및 황화납 생성 반응이 쉽게 일어난다. 폐탈황제는 염기성(pH>9)을 띄어 황화수은 및 황화납을 생성하기에 좋은 조건을 가지고 있다.Since sulfur-containing substances contain sulfide ions (S 2- ), if an impurity dissolution inhibitor is added to the solution, mercury sulfide and lead sulfide may be generated. The solution must be alkaline for the above-mentioned mercury sulfide and lead sulfide generation reaction to occur easily. The waste desulfurization agent is alkaline (pH>9), which provides good conditions for generating mercury sulfide and lead sulfide.
교반 종료 후 혼합물을 고/액 분리하여 고체 탈황 폐기물(1차 폐기물)과 원료(나트륨 용출 용액)를 얻을 수 있다.After stirring, the mixture is separated into solid and liquid to obtain solid desulfurization waste (primary waste) and raw material (sodium extraction solution).
상기 원료는 황산나트륨(Na2SO4), 불순물 용출억제제 및 불순물을 포함한다.The above raw material contains sodium sulfate (Na 2 SO 4 ), an impurity dissolution inhibitor, and impurities.
상기 불순물 용출억제제는 황(S) 함유 물질을 10 중량% 이상 100 중량% 이하 포함할 수 있다. 본 발명의 불순물 용출억제제를 활용하면, 공정 중 발생한 폐기물에서 수은 및 납 등이 용출되지 않으며, 이에 지정폐기물을 일반 폐기물로 처리 가능해짐에 따라 폐기물 처리 비용 절감 효과를 기대 할 수 있다.The above impurity release inhibitor may contain 10 wt% or more and 100 wt% or less of a sulfur (S)-containing substance. By utilizing the impurity release inhibitor of the present invention, mercury and lead, etc. are not released from waste generated during the process, and thus designated waste can be treated as general waste, thereby reducing waste disposal costs.
상기 황 함유물질은 황화수소나트륨, 황화나트륨 및 ICX(Sodium Cellulose Xanthate) 중에서 선택된 1종일 수 있다. 황화 이온은 여러가지 형태로 존재할 수 있다. 중조 순도를 고려할 때, 황화수소나트륨(NaHS), 황화나트륨(Na2S) 및 ICX(Sodium Cellulose Xanthate)은 나트륨 이온을 중조 원료로 쓸 수 있다는 장점이 있다.The above sulfur-containing material may be one selected from sodium bisulfide, sodium sulfide, and ICX (Sodium Cellulose Xanthate). Sulfide ions can exist in various forms. Considering the purity of sodium bisulfide, sodium bisulfide (NaHS), sodium sulfide (Na 2 S), and ICX (Sodium Cellulose Xanthate) have the advantage of being able to use sodium ions as a sodium bisulfide raw material.
상기 불순물은 황산나트륨 (Na2SO4), 납 (Pb), 구리(Cu), 비소(As), 수은 (Hg), 카드뮴(Cd), 크롬(Cr), 시안(CN), 칼륨 (K), 칼슘 (Ca), 철 (Fe), 염소 (Cl)로 이루어진 그룹으로부터 선택되는 적어도 1종을 포함할 수 있다.The above impurities may include at least one selected from the group consisting of sodium sulfate ( Na2SO4 ), lead (Pb), copper (Cu), arsenic (As), mercury (Hg), cadmium (Cd), chromium (Cr), cyanide (CN), potassium (K), calcium (Ca), iron (Fe), and chlorine (Cl).
본 발명의 중조 및 석고의 제조방법은 원료를 탄산화하여 중조(NaHCO3)를 제조하는 단계를 포함한다.The method for producing sodium bicarbonate and gypsum of the present invention includes a step of carbonating a raw material to produce sodium bicarbonate (NaHCO 3 ).
원료에 암모니아수 및 이산화탄소를 투입하여, 탄산화 반응기에서 반응시켜 슬러리를 얻은 뒤, 슬러리를 고/액 분리하여 고형물과 폐액을 얻을 수 있다. 상기 고형물을 수세하고, 건조하여, 중조를 제조할 수 있다.Ammonia water and carbon dioxide can be added to the raw material, reacted in a carbonation reactor to obtain a slurry, and the slurry can be separated into solid and liquid to obtain a solid and a waste liquid. The solid can be washed and dried to produce sodium bicarbonate.
본 발명의 중조를 제조하는 단계로부터 제조된 중조의 순도는 97% 이상일 수 있고, 중조의 수율은 75% 이상일 수 있다.The purity of the sodium bicarbonate produced from the step of producing the sodium bicarbonate of the present invention can be 97% or more, and the yield of the sodium bicarbonate can be 75% or more.
상기 중조를 제조하는 단계에서, 상기 불순물을 3 mg/L 이하 포함하는 1차 폐기물이 발생할 수 있다. 1차 폐기물에 불순물 함량이 3 mg/L 이하인 경우, 인체에 유해한 독성 금속의 누출을 억제할 수 있고, 폐기물 처리 비용을 절감할 수 있다.In the step of manufacturing the above-mentioned sodium bicarbonate, primary waste containing 3 mg/L or less of the above-mentioned impurities may be generated. When the impurity content in the primary waste is 3 mg/L or less, the leakage of toxic metals harmful to the human body can be suppressed, and the cost of waste disposal can be reduced.
상기 석고를 제조하는 단계에서, 상기 불순물을 1.1 mg/L 이하 포함하는 2차 폐기물이 발생할 수 있다. 2차 폐기물에 불순물 함량이 1.1 mg/L 이하인 경우, 인체에 유해한 독성 금속의 누출을 억제할 수 있고, 폐기물 처리 비용을 절감할 수 있다.In the step of manufacturing the above plaster, secondary waste containing the impurities of 1.1 mg/L or less may be generated. When the impurity content in the secondary waste is 1.1 mg/L or less, the leakage of toxic metals harmful to the human body can be suppressed, and the cost of waste disposal can be reduced.
본 발명의 중조 및 석고의 제조방법은, 상기 중조를 제조하는 단계에서 발생하는 폐액을 이용하여 석고(CaSO4)를 제조하는 단계를 포함한다.The method for producing sodium bicarbonate and gypsum of the present invention includes a step of producing gypsum (CaSO 4 ) using waste liquid generated in the step of producing the sodium bicarbonate.
상기 석고를 제조하는 단계는, 상기 폐액에 칼슘 함유 물질을 투입하여, 슬러리를 얻는 단계를 포함할 수 있다. 상기 칼슘 함유 물질은 생석회일 수 있다. 상기 슬러리에서 암모니아를 제거한 후, 산성 용액을 추가하여 교반하여 제2 혼합물을 얻을 수 있다. 상기 산성 용액은 황산 수용액일 수 있다. 또는, 상기 슬러리를 고/액 분리하여 제2 고형물과 제2 폐액을 얻을 수 있다. 상기 제2 폐액에 폭기를 진행하여 암모니아를 제거한 후, 상기 제2 고형물을 다시 혼합한 뒤 황산 수용액을 추가하여 교반하여 제3 혼합물을 얻을 수 있다. 그 후 제2 혼합물 또는 제3 혼합물을 고/액 분리하여 석고와 폐수를 얻을 수 있다.The step of manufacturing the gypsum may include a step of adding a calcium-containing material to the waste liquid to obtain a slurry. The calcium-containing material may be quicklime. After removing ammonia from the slurry, an acidic solution may be added and stirred to obtain a second mixture. The acidic solution may be a sulfuric acid aqueous solution. Alternatively, the slurry may be separated into solid and liquid to obtain a second solid and a second waste liquid. After aeration is performed on the second waste liquid to remove ammonia, the second solid may be mixed again, and then a sulfuric acid aqueous solution may be added and stirred to obtain a third mixture. Thereafter, the second mixture or the third mixture may be separated into solid and liquid to obtain gypsum and waste water.
중조를 제조하는 단계에서 발생하는 폐액을 이용하여 석고를 제조하는 경우, 원료를 재활용하여 석고 생산 비용을 절감하고, 폐기물의 배출양을 저감시켜 환경오염을 방지할 수 있는 장점이 있다.When producing gypsum using waste liquid generated during the manufacturing process of sodium bicarbonate, there are advantages in that the cost of producing gypsum can be reduced by recycling raw materials, and the amount of waste discharged can be reduced, thereby preventing environmental pollution.
본 발명의 석고를 제조하는 단계로부터 제조된 석고의 순도는 95% 이상일 수 있고, 석고의 수율은 75%이상일 수 있다.The purity of the gypsum manufactured from the step of manufacturing the gypsum of the present invention can be 95% or more, and the yield of the gypsum can be 75% or more.
실시예Example
이하, 본 발명을 실시예를 들어 보다 구체적으로 설명한다. 이하의 실시예는 본 발명을 보다 구체적으로 설명하기 위한 것으로서, 이에 의해 본 발명이 한정되는 것은 아니다.Hereinafter, the present invention will be described more specifically with reference to examples. The following examples are intended to more specifically explain the present invention, but the present invention is not limited thereto.
실시예 1Example 1
중조 제조를 제조하는 단계Steps for manufacturing a bicarbonate
탈황 폐기물 99.93 g 및 물 200 mL를 투입하여 40 ℃에서 1시간동안 교반하여 용액을 제조하였다. 상기 용액에 불순물 용출억제제로 황화나트륨(Na2S)을, 탈황 폐기물과 황화나트륨의 질량의 합을 기준으로 하였을 때 황화나트륨의 중량비는 0.7 중량%가 되도록, 황화나트륨(Na2S) 0.7 g을 투입하여 40 ℃에서 1시간동안 추가 교반을 진행하였다. 교반 종료 후 혼합물을 고/액 분리하여 고체 탈황 폐기물(1차 폐기물)과 원료(나트륨 용출 용액)를 얻었다.A solution was prepared by adding 99.93 g of desulfurized waste and 200 mL of water and stirring at 40°C for 1 hour. To the solution, sodium sulfide ( Na2S ) was added as an impurity dissolution inhibitor, and 0.7 g of sodium sulfide ( Na2S ) was added so that the weight ratio of sodium sulfide was 0.7 wt% based on the sum of the masses of the desulfurized waste and sodium sulfide, and additional stirring was performed at 40°C for 1 hour. After stirring, the mixture was separated into solid and liquid to obtain solid desulfurized waste (primary waste) and raw material (sodium dissolution solution).
1차 폐기물을 100 g 얻을 때까지 원료 제조를 반복하였다.The raw material manufacturing process was repeated until 100 g of primary waste was obtained.
1차 폐기물 100 g 및 물 1 L를 투입하였다. 염산을 사용하여 pH가 5.8과 6.3 사이에 있도록 조절하였다. 상온, 상압에서 6시간동안 교반한 후, 필터링(Glass filter GF-B 1μm)하여 여액을 얻었다.100 g of primary waste and 1 L of water were added. The pH was adjusted to between 5.8 and 6.3 using hydrochloric acid. After stirring at room temperature and pressure for 6 hours, the solution was filtered (Glass filter GF-B 1 μm) to obtain a filtrate.
여액에 대해 ICP (Inductively Coupled Plasma)법을 활용하여 납(Pb)의 양을 확인하였고, AA (Atomic Absorption)법을 활용하여 수은(Hg)의 양을 확인하였다. 1차 폐기물 100 g에 대한 수은(Hg) 및 납(Pb) 용출 실험 결과를 표 2에 나타내었다.The amount of lead (Pb) in the residue was confirmed using the ICP (Inductively Coupled Plasma) method, and the amount of mercury (Hg) was confirmed using the AA (Atomic Absorption) method. The results of the mercury (Hg) and lead (Pb) extraction experiments for 100 g of primary waste are shown in Table 2.
한편, 상기 원료 500 g에, 25 내지 30 중량%의 암모니아수 90 g 및 이산화탄소 100 g을 투입하여, 탄산화 반응기에서 반응시켜 슬러리를 얻었다. 슬러리를 고/액 분리하여 고형물과 폐액을 얻었다.Meanwhile, 90 g of ammonia water having a concentration of 25 to 30 wt% and 100 g of carbon dioxide were added to 500 g of the above raw material and reacted in a carbonation reactor to obtain a slurry. The slurry was separated into solid and liquid to obtain solids and waste liquid.
상기 제1 고형물을 수세한 후 50 ℃ 오븐에서 12시간 이상 건조하여 중조를 얻었다.After washing the above first solid, it was dried in an oven at 50°C for more than 12 hours to obtain sodium bicarbonate.
중조의 수율 및 순도를 표 3에 나타내었다. 중조 수율은 폐탈황제 및 생산된 중조의 Na+ mol 기준으로 계산하였다. 중조의 순도를ICP장비 및 XRD (X-ray Powder Diffraction) 장비를 활용하여 측정하였다.The yield and purity of the sodium bicarbonate are shown in Table 3. The yield of the sodium bicarbonate was calculated based on the Na + mol of the waste desulfurizer and the produced sodium bicarbonate. The purity of the sodium bicarbonate was measured using ICP equipment and XRD (X-ray Powder Diffraction) equipment.
석고를 제조하는 단계Steps in making plaster
상기 중조 제조 단계에서 얻은 폐액 500 g에, 25% 생석회 슬러리 350 g을 투입하여 1시간 동안 교반하였다. 교반이 완료된 슬러리를 고/액 분리하여 제2 고형물과 제2 폐액을 얻었다.To 500 g of the waste liquid obtained in the above-mentioned step of manufacturing the sodium bicarbonate, 350 g of 25% quicklime slurry was added and stirred for 1 hour. After stirring, the slurry was separated into solid and liquid to obtain a second solid and a second waste liquid.
상기 제2 폐액을 80 ℃로 가열하고 비활성 가스를 활용하여 슬러리 내부에 있는 NH3를 회수하기 위해 폭기를 진행하였다. 폭기를 진행하여 NH3가 제거된 제2 폐액과 상기 고/액 분리 후 얻은 제2 고형물을 다시 혼합한 뒤 30 중량%의 황산 수용액 110 g을 추가하여 교반하였다. 그 후 고/액 분리하여 석고와 폐수를 얻었다.The above second waste liquid was heated to 80°C and aerated using an inert gas to recover NH3 within the slurry. The second waste liquid from which NH3 was removed by aeration was mixed with the second solid obtained after the solid/liquid separation, and 110 g of a 30 wt% sulfuric acid aqueous solution was added and stirred. Thereafter, solid/liquid separation was performed to obtain gypsum and waste water.
석고의 수율 및 순도를 표 4에 나타내었다. 석고 수율은 폐탈황제 및 생산된 석고의 SO4 2- mol 기준으로 계산하였다. 석고의 수율은 ICP로 측정하고, 석고의 순도는 XRD 로 측정하였다.The yield and purity of gypsum are shown in Table 4. The gypsum yield was calculated based on the SO 4 2- mol of the waste desulfurizer and the produced gypsum. The gypsum yield was measured by ICP, and the purity of gypsum was measured by XRD.
상기 석고 제조 단계에서 얻은 폐수 1000 g에 대하여 온도 80 ℃ 이상, 압력 0.1 bar 이하에서 1시간 동안 증발농축을 진행하여, 2차 폐기물을 얻었다.For 1000 g of wastewater obtained in the above plaster manufacturing step, evaporation and concentration were performed for 1 hour at a temperature of 80°C or higher and a pressure of 0.1 bar or lower to obtain secondary waste.
2차 폐기물 폐기물 100 g 및 물 1 L를 투입하였다. 염산을 사용하여 pH가 5.8과 6.3 사이에 있도록 조절하였다. 상온, 상압에서 6시간동안 교반한 후, 필터링(Glass filter GF-B 1μm)하여 여액을 얻었다.100 g of secondary waste and 1 L of water were added. The pH was adjusted to between 5.8 and 6.3 using hydrochloric acid. After stirring at room temperature and pressure for 6 hours, the solution was filtered (Glass filter GF-B 1 μm) to obtain a filtrate.
여액에 대해 ICP법을 활용하여 납(Pb)의 양을 확인하였고, AA법을 활용하여 수은(Hg)의 양을 확인하였다. 2차 폐기물 100 g에 대한 수은(Hg) 및 납(Pb) 용출 실험 결과를 표 5에 나타내었다.The amount of lead (Pb) in the residue was confirmed using the ICP method, and the amount of mercury (Hg) was confirmed using the AA method. The results of the mercury (Hg) and lead (Pb) elution experiments for 100 g of secondary waste are shown in Table 5.
실시예 2 내지 5Examples 2 to 5
탈황 폐기물을 각각 98.7, 98, 97.7, 96.7 g 투입하고, 황화나트륨을 각각 1.3, 2.0, 2.3, 3.3 g 투입한 것 이외에는 실시예 1과 동일한 방법으로 중조 및 석고를 제조하였다.Sodium bicarbonate and gypsum were manufactured in the same manner as in Example 1, except that 98.7, 98, 97.7, and 96.7 g of desulfurized waste were added, respectively, and 1.3, 2.0, 2.3, and 3.3 g of sodium sulfide were added, respectively.
비교예 1Comparative Example 1
탈황 폐기물을 100 g 투입하고, 황화나트륨을 투입하지 않은 것 이외에는 실시예 1과 동일한 방법으로 중조 및 석고를 제조하였다.Sodium bicarbonate and gypsum were manufactured in the same manner as in Example 1, except that 100 g of desulfurized waste was added and sodium sulfide was not added.
실험예 Experimental example
실시예 2 내지 5 및 비교예 1의 1차 폐기물에 대한 여액에 대해 ICP 법을 활용하여 납(Pb)의 양을 확인하였고, AA 법을 활용하여 수은(Hg)의 양을 확인하였다. 1차 폐기물 100 g에 대한 수은(Hg) 및 납(Pb) 용출 실험 결과를 표 2에 나타내었다.The amount of lead (Pb) in the filtrate of the primary wastes of Examples 2 to 5 and Comparative Example 1 was confirmed using the ICP method, and the amount of mercury (Hg) was confirmed using the AA method. The results of the mercury (Hg) and lead (Pb) elution experiments for 100 g of primary waste are shown in Table 2.
실시예 1 내지 5의 1차 폐기물에서는 수은이 0.005 mg/L 이하, 납이 3 mg/L 이하로 검출되는 것을 확인할 수 있다.It can be confirmed that mercury is detected at 0.005 mg/L or less and lead is detected at 3 mg/L or less in the primary wastes of Examples 1 to 5.
실시예 2 내지 5 및 비교예 1의 중조의 수율 및 순도를 표 3에 나타내었다.The yield and purity of the sodium bicarbonate of Examples 2 to 5 and Comparative Example 1 are shown in Table 3.
비교예 1과 실시예 1 내지 5의 중조 순도 및 수율에는 차이가 없는 것을 확인할 수 있다. 황화나트륨 투입 유무는 중조 순도 및 수율에 영향을 미치지 않는 것을 확인할 수 있다.It can be confirmed that there is no difference in the purity and yield of the sodium bicarbonate in Comparative Example 1 and Examples 1 to 5. It can be confirmed that the presence or absence of sodium sulfide does not affect the purity and yield of the sodium bicarbonate.
실시예 2 내지 5 및 비교예 1의 석고의 수율 및 순도를 표 4에 나타내었다.The yield and purity of the gypsum of Examples 2 to 5 and Comparative Example 1 are shown in Table 4.
비교예 1과 실시예 1 내지 5의 석고 순도 및 수율에는 차이가 없는 것을 확인할 수 있다. 황화나트륨 투입 유무는 석고 순도 및 수율에 영향을 미치지 않는 것을 확인할 수 있다.It can be confirmed that there is no difference in the purity and yield of gypsum between Comparative Example 1 and Examples 1 to 5. It can be confirmed that the presence or absence of sodium sulfide does not affect the purity and yield of gypsum.
실시예 2, 3 및 비교예 1의 2차 폐기물에 대한 여액에 대해 ICP (Inductively Coupled Plasma)법을 활용하여 납(Pb)의 양을 확인하였고, AA (Atomic Absorption)법을 활용하여 수은(Hg)의 양을 확인하였다. 2차 폐기물 100 g에 대한 수은(Hg) 및 납(Pb) 용출 실험 결과를 표 5에 나타내었다.The amount of lead (Pb) in the filtrates of the secondary wastes of Examples 2 and 3 and Comparative Example 1 was confirmed using the ICP (Inductively Coupled Plasma) method, and the amount of mercury (Hg) was confirmed using the AA (Atomic Absorption) method. The results of the mercury (Hg) and lead (Pb) elution experiments for 100 g of secondary waste are shown in Table 5.
실시예 1 및 2의 폐기물에서는 수은이 0.005 mg/L 이하, 납이 3 mg/L 이하로 검출되는 것을 확인할 수 있다.It was confirmed that mercury was detected at 0.005 mg/L or less and lead was detected at 3 mg/L or less in the waste of Examples 1 and 2.
이상에서 본 발명의 실시예에 대하여 상세하게 설명하였지만 본 발명의 권리범위는 이에 한정되는 것은 아니고, 청구범위에 기재된 본 발명의 기술적 사상을 벗어나지 않는 범위 내에서 다양한 수정 및 변형이 가능하다는 것은 당 기술분야의 통상의 지식을 가진 자에게는 자명할 것이다.Although the embodiments of the present invention have been described in detail above, the scope of the present invention is not limited thereto, and it will be apparent to those skilled in the art that various modifications and variations are possible within a scope that does not depart from the technical spirit of the present invention described in the claims.
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| KR20150130151A (en) * | 2014-05-13 | 2015-11-23 | 주식회사 유니코정밀화학 | COMPOSITION FOR REMOVING SOx IN EXHAUSTED GAS AND METHOD FOR REMOVING Sox IN EXHAUSTED GAS |
| KR20160000480A (en) * | 2014-06-24 | 2016-01-05 | 순천대학교 산학협력단 | Method and apparatus of NaHCO3 production from filtered solution of desulfurized crude waste |
| CN107364878A (en) * | 2016-05-11 | 2017-11-21 | 江苏井神盐化股份有限公司 | A kind of high-purity soda ash of low calcium and its production method by the production of sodium sulfate type ore deposit halogen |
| KR20200059639A (en) * | 2018-11-21 | 2020-05-29 | 주식회사 포스코 | GYPSUM PRODUCTION METHOD USING DE-SOx DUST TREATED WITH NaHCO3 |
| KR20200061649A (en) * | 2018-11-26 | 2020-06-03 | 현대제철 주식회사 | Method for regeneration of sodium biocarbonate particles using desulphurization by-products |
| KR20230167593A (en) * | 2022-06-02 | 2023-12-11 | 재단법인 포항산업과학연구원 | Method for manufacturing sodium bicarbonate and gypsum using sodium sulfate |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| KR20150130151A (en) * | 2014-05-13 | 2015-11-23 | 주식회사 유니코정밀화학 | COMPOSITION FOR REMOVING SOx IN EXHAUSTED GAS AND METHOD FOR REMOVING Sox IN EXHAUSTED GAS |
| KR20160000480A (en) * | 2014-06-24 | 2016-01-05 | 순천대학교 산학협력단 | Method and apparatus of NaHCO3 production from filtered solution of desulfurized crude waste |
| CN107364878A (en) * | 2016-05-11 | 2017-11-21 | 江苏井神盐化股份有限公司 | A kind of high-purity soda ash of low calcium and its production method by the production of sodium sulfate type ore deposit halogen |
| KR20200059639A (en) * | 2018-11-21 | 2020-05-29 | 주식회사 포스코 | GYPSUM PRODUCTION METHOD USING DE-SOx DUST TREATED WITH NaHCO3 |
| KR20200061649A (en) * | 2018-11-26 | 2020-06-03 | 현대제철 주식회사 | Method for regeneration of sodium biocarbonate particles using desulphurization by-products |
| KR20230167593A (en) * | 2022-06-02 | 2023-12-11 | 재단법인 포항산업과학연구원 | Method for manufacturing sodium bicarbonate and gypsum using sodium sulfate |
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