KR100960151B1 - Coagulant composition and manufacturing method thereof - Google Patents
Coagulant composition and manufacturing method thereof Download PDFInfo
- Publication number
- KR100960151B1 KR100960151B1 KR1020090085393A KR20090085393A KR100960151B1 KR 100960151 B1 KR100960151 B1 KR 100960151B1 KR 1020090085393 A KR1020090085393 A KR 1020090085393A KR 20090085393 A KR20090085393 A KR 20090085393A KR 100960151 B1 KR100960151 B1 KR 100960151B1
- Authority
- KR
- South Korea
- Prior art keywords
- parts
- weight
- aqueous solution
- reacting
- polyamine
- Prior art date
Links
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
Landscapes
- Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
본 발명은 아민이 혼합된 폴리염화알루미늄칼슘을 함유하는 응집제 조성물 및 그 제조방법에 관한 것이다. The present invention relates to a flocculant composition containing polyaluminum calcium chloride in which an amine is mixed and a method for producing the same.
응집제는 무기 응집제와 유기 응집제로 분류되며, 무기 응집제 중 고분자 응집제는 단분자 응집제에 비하여 응집효율이 높고 불순물을 침전시키는 속도가 우수하여 널리 사용되었다. 특히 수처리용으로 화학 변종이 생길 수 있는 알루미늄 응집제들이 주로 사용되는데, 모노머인 알루미늄이온을 중합하여 고분자로 합성하여 사용한다. 대표적으로 황산알루미늄(aluminium sulfate, LAS), 폴리염화알루미늄(poly aluminum chloride, PAC), 폴리염화규산알루미늄(poly aluminum chloride silicate, PACS) 및 폴리염화알루미늄칼슘(poly aluminum chloride calcium, PACC)등이 있다. Coagulants are classified into inorganic coagulants and organic coagulants, and polymer coagulants among inorganic coagulants have been widely used because of their high cohesive efficiency and superior rate of precipitation of impurities compared to single molecule coagulants. In particular, aluminum flocculants, which can generate chemical variants for water treatment, are mainly used. Polymerized monomers are used to polymerize aluminum ions. Typical examples include aluminum sulfate (LAS), poly aluminum chloride (PAC), poly aluminum chloride silicate (PACS), and poly aluminum chloride calcium (PACC). .
그러나 이러한 알루미늄 무기응집제들을 단독으로 사용할 경우 유기물 제거 효과 및 탁도 개선 효과가 충분하지 않으며, 수처리 후 잔류하는 알루미늄 이온이 알츠하이머병(Alzheimer's disease) 등의 뇌질환을 유발시킬 수 있는 것으로 보고되면서 무기응집제 사용에 대한 문제점들이 제기되고 있다. However, when these aluminum inorganic coagulants are used alone, the effect of removing organic matters and improving turbidity is not sufficient, and it is reported that aluminum ions remaining after water treatment can cause brain diseases such as Alzheimer's disease. Problems have been raised.
또한 기존의 무기응집제들은 탁도 및 pH에 의해서 유기물 처리 효율과 응집제의 안정성이 크게 좌우됨으로써 고탁도 및 고염기도에서는 부유물의 제거 효율이나 안정성이 크게 떨어지는 문제점이 있었다. 이러한 문제점은 특히 우리나라와 같이 계절에 따라 물의 성질이 변하는 경우에는 갈수기인 11월과 3월 사이에는 조류의 생성으로 인하여 pH 높아지고, 우수기인 6월과 9월 사이에는 고탁도가 되는 경우 부유물의 제거 효율의 변동이 큰 폭으로 나타나게 되어 사계절용 수처리에 적용되는 응집제의 개발이 필요하다. In addition, the conventional inorganic coagulants have a problem that the efficiency of removing organic matters and stability of the flocculant are greatly reduced by high turbidity and pH and the stability of organic matter treatment efficiency and coagulant greatly depends. This problem is especially high in Korea when the water properties change with seasons, such as in Korea, between the November and March seasons, due to the formation of algae, and when the turbidity is reached between the June and September seasons. The fluctuations in efficiency are so great that it is necessary to develop a flocculant that is applied to water treatment for four seasons.
이에 본 발명자들은 아민이 혼합된 폴리염화알루미늄칼슘이 저염기성 알루미늄계 무기응집제가 가지고 있는 단점인 제품의 불안정성 및 사계절용으로 맞지 않는 문제점들을 개선하고 염기도가 70% 이상에서도 안정성을 가지고 사계절용 수처리에 적용될 수 있음을 밝혀 본 발명을 완성하였다.Therefore, the present inventors have improved the instability of the product, which is a disadvantage of the low-basic aluminum-based inorganic coagulant, which is a disadvantage of the low basic aluminum-based inorganic coagulant, and it is not suitable for the four seasons. It has been found that it can be applied to complete the present invention.
삭제delete
본 발명의 다른 측면에 따르면, 본 발명은 (a) 수산화알루미늄(Al2O3) 및 염산(HCl)을 혼합하여 반응시킨 후 황산(H2SO4)을 첨가하여 추가 반응시키는 단계, (b) 단계 (a)의 반응물에 탄산칼슘(CaCO3)수용액을 혼합 및 교반하여 반응시키는 단계, (c) 단계 (b)의 반응물에 탄산나트륨 수용액 및 폴리아민계유기응결제인 에피클로로히드린 디메틸아민 폴리아민 수용액을 첨가하여 교반하는 단계를 포함하는 응집제의 제조방법을 제공하는 것을 목적으로 한다.According to another aspect of the present invention, the present invention comprises the steps of (a) reacting by mixing aluminum hydroxide (Al 2 O 3 ) and hydrochloric acid (HCl) and then further by adding sulfuric acid (H 2 SO 4 ), (b A) reacting the reactant of step (a) by mixing and stirring an aqueous solution of calcium carbonate (CaCO 3 ); It is an object to provide a method for producing a flocculant comprising the step of adding and stirring.
본 발명의 다른 측면에 따르면, 본 발명은 상기 방법에 의해 제조되는 수처리용 응집제인 아민이 혼합된 폴리염화알루미늄칼슘을 제공하는 것을 목적으로 한다.According to another aspect of the present invention, an object of the present invention is to provide a polyaluminum calcium chloride mixed with an amine which is a flocculant for water treatment produced by the above method.
본 발명의 다른 측면에 따르면, 본 발명은 (a) 수산화알루미늄(Al2O3) 및 염산(HCl)을 혼합하여 반응시킨 후 황산(H2SO4)을 첨가하여 추가 반응시키는 단계, (b) 단계 (a)의 반응물에 탄산칼슘(CaCO3)수용액을 혼합 및 교반하여 반응시키는 단계, (c) 단계 (b)의 반응물에 탄산나트륨 수용액 및 폴리아민계유기응결제인 에피클로로히드린 디메틸아민 폴리아민 수용액을 첨가하여 교반하는 단계를 포함하는 응집제의 제조방법을 제공한다. According to another aspect of the present invention, the present invention comprises the steps of (a) reacting by mixing aluminum hydroxide (Al 2 O 3 ) and hydrochloric acid (HCl) and then further by adding sulfuric acid (H 2 SO 4 ), (b A) reacting the reactant of step (a) by mixing and stirring an aqueous solution of calcium carbonate (CaCO 3 ); It provides a method for producing a flocculant comprising the step of adding and stirring.
삭제delete
삭제delete
이하, 본 발명을 보다 상세하게 설명한다. Hereinafter, the present invention will be described in more detail.
본 발명의 응집제 조성물은 아민이 혼합된 폴리염화알루미늄칼슘인 것을 특징으로 한다.The flocculant composition of this invention is characterized by being polyaluminum calcium chloride mixed with amine.
본 발명의 아민이 혼합된 폴리염화알루미늄칼슘은 폴리염화알루미늄(PAC)을 고염기화한 후 유기응결제를 첨가하여 고분자화한 것으로써, 아민이 혼합된 폴리염화알루미늄칼슘을 포함하는 수처리용 응집제는 넓은 범위의 pH, 탁도 및 수온에서 우수한 응집 성능을 보인다. 기존의 황산알루미늄(LAS) 또는 폴리염화알루미늄(PAC)과는 달리 중화제를 필요로 하지 않으며, 알루미늄 제거율 또한 99%의 효율로 매우 우수하고 6개월 이상의 안정성을 나타낸다. 아민이 혼합된 폴리염화알루미늄칼슘은 수처리시 미세 플록(floc) 입자가 가교 흡착 작용하여 흡착 활성도를 증대시키며 고분자 체인과 유기 응결제의 작용으로 응집 효율이 높다. 수처리시 아민이 혼합된 폴리염화알루미늄칼슘의 농도는 바람직하게 30-70ppm, 더욱 바람직하게는 30-55ppm, 더욱 바람직하게는 40-55ppm이다.The polyaluminum calcium chloride mixed with the amine of the present invention is polymerized by adding the organic coagulant after high basicizing the polyaluminum chloride (PAC), and the coagulant for water treatment containing polyaluminum calcium chloride mixed with the amine is broad. It exhibits good cohesive performance in the range of pH, turbidity and water temperature. Unlike conventional aluminum sulphate (LAS) or polyaluminum chloride (PAC), it does not require a neutralizing agent, and the aluminum removal rate is also very good with an efficiency of 99% and shows stability over 6 months. The polyaluminum calcium chloride mixed with amine increases the adsorption activity by cross-adsorption of fine floc particles during water treatment, and has high coagulation efficiency due to the action of polymer chain and organic coagulant. The concentration of the polyaluminum calcium chloride mixed with the amine in the water treatment is preferably 30-70 ppm, more preferably 30-55 ppm, more preferably 40-55 ppm.
본 발명의 일 실시예에서는 탁도 8.2NTU 및9.00의 pH에서 아민이 혼합된 폴리염화알루미늄칼슘의 응집력을 확인하였으며, 처리후 황산알루미늄(LAS) 및 폴리염화알루미늄(PAC)이 각각1.8NTU 및 1.3NTU를 나타낸 반면, 본 발명의 아민이 혼합된 폴리염화알루미늄칼슘은 0.40 NTU를 나타내어 우수한 응집력을 확인하였다.In one embodiment of the present invention, the cohesion of the polyaluminum chloride mixed with the amine at the pH of turbidity 8.2NTU and 9.00 was confirmed, and aluminum sulfate (LAS) and polyaluminum chloride (PAC) were 1.8 NTU and 1.3 NTU, respectively. On the other hand, polyaluminum calcium chloride mixed with the amine of the present invention exhibited 0.40 NTU, confirming excellent cohesion.
본 발명은 The present invention
(a) 수산화알루미늄(Al2O3) 및 염산(HCl)을 혼합하여 반응시킨 후 황산(H2SO4)을 첨가하여 추가 반응시키는 단계, (a) reacting by mixing aluminum hydroxide (Al 2 O 3 ) and hydrochloric acid (HCl) and then adding sulfuric acid (H 2 SO 4 ) to further react,
(b) 단계 (a)의 반응물에 탄산칼슘(CaCO3)수용액을 혼합 및 교반하여 반응시 키는 단계, (b) reacting the reactant of step (a) with a mixture of calcium carbonate (CaCO 3 ) solution and stirring the mixture;
(c) 단계 (b)의 반응물에 탄산나트륨 수용액 및 폴리아민계유기응결제인 에피클로로히드린 디메틸아민 폴리아민 수용액을 첨가하여 교반하는 단계를 포함하는 응집제의 제조방법을 제공한다. (c) providing a method of preparing a flocculant comprising adding and stirring an aqueous solution of sodium carbonate and an aqueous solution of epichlorohydrin dimethylamine polyamine, which is a polyamine organic coagulant, to the reaction product of step (b).
단계 (a)는 중축합 반응을 통하여 중합도를 높히고 고분자화하여 응집력 향상과 저장 안정성을 높여주는 공정으로써, 바람직하게 수산화알루미늄(Al2O3)은 80-120 중량부, 염산(HCl)은 150-250 중량부이고 황산(H2SO4)은 2-3 중량부이다. Step (a) is a process of increasing polymerization degree and polymerizing through polycondensation reaction to improve cohesion and storage stability. Preferably, aluminum hydroxide (Al 2 O 3 ) is 80-120 parts by weight and hydrochloric acid (HCl) is 150 -250 parts by weight and sulfuric acid (H 2 SO 4 ) is 2-3 parts by weight.
수산화알루미늄(Al2O3) 및 염산(HCl)의 반응으로 생성된 [Al2(OH)nCl6-n〕m 은 황산(H2SO4)과의 중축합 반응을 통하여 안정성 및 응집력이 향상된다. 바람직하게는 황산이온이 0.2~3%가 되도록 하며, 황산뿐만 아니라 황산나트륨, 황산알루미늄(LAS), 황산마그네슘 등의 황산이온이 첨가된 임의의 화합물을 사용할 수 있다. 더욱 바람직하게 단계 (a)는 온도 130-190℃ 및 압력 5kg/cm3의 조건에서 반응하며, 염산(HCl) 및 수산화알루미늄(Al2O3)을 3-7시간, 황산을 첨가하여 추가로 3-7시간 동안 교반하여 반응시킨다. [Al2 (OH) nCl6-n] m produced by the reaction of aluminum hydroxide (Al 2 O 3 ) and hydrochloric acid (HCl) has improved stability and cohesion through polycondensation with sulfuric acid (H 2 SO 4 ). Preferably, the sulfate ion is 0.2 to 3%, and any compound to which sulfuric acid ions such as sodium sulfate, aluminum sulfate (LAS) and magnesium sulfate are added, as well as sulfuric acid, may be used. More preferably, step (a) is reacted under conditions of a temperature of 130-190 ° C. and a pressure of 5 kg / cm 3, hydrochloric acid (HCl) and aluminum hydroxide (Al 2 O 3 ) for 3-7 hours, sulfuric acid is added to further 3 The reaction is stirred for -7 hours.
단계 (b)는 탄산칼슘 수용액과 단계 (a)에서 생성된 반응액의 반응으로 CO2가 발생되면서 고염기화(염기도 70%)되는 공정으로써, 바람직하게는 탄산칼슘수용액이 75-85 중량부이다. 바람직하게는 온도 50-70℃, 더욱 바람직하게는 60℃에서 150-300rpm으로 1-4시간 교반하고, 탄산칼슘의 용해 효율성 및 균질화를 위해 고속 혼합기를 사용하여 반응시키며, 반응식은 하기와 같다. Step (b) is a process in which CO 2 is generated and the base is highly basicized (70% base) with the reaction of the aqueous solution of calcium carbonate and the reaction solution produced in step (a). Preferably, the aqueous solution of calcium carbonate is 75-85 parts by weight. Preferably it is stirred for 1-4 hours at a temperature of 50-70 ℃, more preferably at 60-150 ℃ 150-300rpm, and reacted using a high speed mixer for dissolution efficiency and homogenization of calcium carbonate, the reaction scheme is as follows.
〔Al2(OH)nCl6-n-2K(SO4)K〕+ CaCO3 + H2O [Al 2 (OH) nCl 6-n-2K (SO 4 ) K ] + CaCO 3 + H 2 O
→ Al x(OH) yCl z(SO4)K + CaCl2 ↓ → Al x (OH) y Cl z (SO 4 ) K + CaCl 2 ↓
여기서 n은 2.5-4.5이고 0≤K≤4 이다. Where n is 2.5-4.5 and 0 ≦ K ≦ 4.
단계 (c)에서 바람직하게 탄산나트륨 수용액은 140-180 중량부이고, 폴리아민계유기응결제인 에피클로로히드린 디메틸아민 폴리아민 수용액은 16-27 중량부이다. 더욱 바람직하게는 온도 30-80℃를 유지하면서 1500-200rpm으로 1-3시간동안 교반한다. 탄산나트륨 수용액은 완전한 고 염기화를 위한 것이고, 폴리아민계유기응결제인 에피클로로히드린-디메틸아민 폴리아민 수용액은 물, 유.무기 응집제 혼합함으로써 처리수 탁도를 양호하게 하며 플록(Floc) 강도 및 흡착 활성도를 증대시키고, 슬러지의 압축성을 개선시킨다. 또한 소량으로도 우수한 응집 효율을 나타냄으로써 정수처리 시 응집제 사용량이 절감되고, 응집 적용 범위를 더욱 넓게 하는 효과를 가져온다. In step (c) preferably the aqueous sodium carbonate solution is 140-180 parts by weight, and the polyamine-based organic coagulant epichlorohydrin dimethylamine polyamine aqueous solution is 16-27 parts by weight. More preferably, the temperature is stirred at 1500-200 rpm for 1-3 hours while maintaining the temperature of 30-80 ° C. The aqueous solution of sodium carbonate is for complete high basicization, and the aqueous solution of epichlorohydrin-dimethylamine polyamine, which is a polyamine organic coagulant, improves turbidity of treated water by mixing water and organic / inorganic flocculant and improves floc strength and adsorption activity. Increase and improve the compressibility of the sludge. In addition, by showing excellent flocculation efficiency even in a small amount, the amount of flocculant used during water purification is reduced, and the effect of broadening the flocculation range is brought.
본 발명의 수처리용 응집제인 아민이 혼합된 폴리염화알루미늄칼슘은 적은 용량으로 다양한 pH, 탁도 등의 조건에서 우수한 응집 기능을 나타내며, 특히 높은 pH 및 고탁도에서도 기존의 황산알루미늄(LAS)이나 폴리염화알루미늄(PAC)등의 응집제보다 고효율의 응집효능을 나타내는 것으로 확인되어, 염기도가 70% 이상에서도 안정성을 가지면서 사계절용 수처리에도 이용할 수 있다.Polyaluminum aluminum chloride mixed with amine, which is a flocculant for water treatment of the present invention, exhibits excellent flocculation function at various pH, turbidity, etc. with a small capacity, and in particular, existing aluminum sulfate (LAS) or polychloride at high pH and It is confirmed that it exhibits a higher efficiency of coagulation efficiency than a coagulant such as aluminum (PAC), and it can be used for water treatment for four seasons with stability even at a basicity of 70% or more.
하기 제조예 및 실시예에서 아민이 혼합된 폴리염화알루미늄칼슘의 제조방법 및 수처리용 응집제로서의 이용을 개시하였으나, 이에 한정되는 것은 아니고, 당업자가 쉽게 생각할 수 있는 범위의 제조방법 및 사용범위를 포함한다. In the following Preparation Examples and Examples, a method of preparing polyaluminum chloride mixed with an amine and a flocculant for water treatment have been disclosed, but are not limited thereto, and include a range of methods and ranges of use that can be easily considered by those skilled in the art. .
제조예 1. 아민이 혼합된 폴리염화알루미늄칼슘 응집제의 제조 Preparation Example 1 Preparation of Polyaluminum Calcium Chloride Coagulant Mixed with Amines
염산 200kg, 수산화알루미늄 100kg을 160℃의 온도 및 5kg/cm3 의 압력에서 5시간 동안 교반하여 반응시킨 후, 황산 이온이 1%가 되도록 황산 2.5kg을 첨가하여 같은 온도 및 압력에서 2시간 동안 추가로 교반하였다. 그 다음 탄산칼슘 수용액(탄산칼슘 7kg 및 물 72kg)을 넣고 60℃에서 200rpm으로 2시간 동안 교반하고, 탄산나트륨 수용액(탄산나트륨 40kg 및 물 120kg) 및 폴리아민계유기응결제인 에피클로로히드린 디메틸아민 폴리아민 수용액(응결제 1.5kg 및 물 20kg)을 투입하여 50℃에서 150-200rpm으로 2시간동안 추가로 교반하여 아민이 혼합된 폴리염화알루미늄칼슘 응집제를 제조하였다. After 200 kg of hydrochloric acid and 100 kg of aluminum hydroxide were stirred for 5 hours at a temperature of 160 ° C. and a pressure of 5 kg / cm 3, 2.5 kg of sulfuric acid was added so that 1% of sulfate ions were added, followed by an additional 2 hours at the same temperature and pressure. Stirred. Then, add an aqueous calcium carbonate solution (7 kg of calcium carbonate and 72 kg of water), stir at 200 rpm at 60 ° C. for 2 hours, an aqueous sodium carbonate solution (40 kg of sodium carbonate and 120 kg of water) and an aqueous solution of epichlorohydrin dimethylamine polyamine as a polyamine organic coagulant ( 1.5 kg of coagulant and 20 kg of water) were added thereto, and further stirred at 150-200 rpm at 50 ° C. for 2 hours to prepare a polyaluminum calcium chloride coagulant mixed with amine.
제조예 1에 따라 제조된 아민이 혼합된 폴리염화알루미늄칼슘 응집제의 응집 효능을 확인하기 위하여 다양한 조건에서 응집 교반 시험(Jar Test)을 수행하여 황산알루미늄(LAS) 및 폴리염화알루미늄(PAC)과의 효능을 비교하였다. In order to confirm the coagulation efficacy of the polyaluminum calcium chloride coagulant mixed with the amine prepared according to Preparation Example 1, a coagulation agitation test (Jar Test) was performed under various conditions to be combined with aluminum sulfate (LAS) and polyaluminum chloride (PAC). Efficacy was compared.
실시예Example 1. One.
응집 교반 시험은 급속 교반 150rpm에서 1분, 완속 교반 50rpm에서 10분 및 20rpm에서 1분, 정치 10분의 조건에서 밑면에서 5cm 지점에서 시료를 채수하고, 원수는 pH 9.00, 탁도 8.2NTU, COD 13.80mg/L, 수온 14℃ 및 원수 알칼리도 75mg/L인 조건에서 수행하였고, 황산알루미늄(LAS) 65ppm, 폴리염화알루미늄(PAC) 45ppm 및 아민이 혼합된 폴리염화알루미늄칼슘 45ppm을 투입하였다. The coagulation stirring test takes a sample at 5 cm from the bottom under conditions of 1 minute at 150 rpm for rapid stirring, 10 minutes at 50 rpm for slow stirring, and 1 minute at 20 rpm for 10 minutes, and the raw water is pH 9.00, turbidity 8.2 NTU, COD 13.80 It was carried out under the conditions of mg / L, water temperature of 14 ℃ and raw water alkalinity of 75 mg / L, 65 ppm of aluminum sulfate (LAS), 45 ppm of poly aluminum chloride (PAC) and 45 ppm of polyaluminum calcium chloride mixed with an amine.
그 결과, 본 발명의 아민이 혼합된 폴리염화알루미늄칼슘을 사용한 경우 탁도가 0.4 NTU로 측정되어, 1.5배 가량 높은 농도를 사용한 황산알루미늄(LAS)보다 매우 낮았으며, 1.3 NTU로 측정된 폴리염화알루미늄(PAC)보다도 0.9 낮은 수치를 보여, 부유물 제거효율이 기존의 알루미늄 응집제보다 월등한 것으로 나타났다(표 1).As a result, when the polyaluminum chloride mixed with the amine of the present invention was used, the turbidity was measured at 0.4 NTU, which was much lower than that of aluminum sulfate (LAS) using about 1.5 times higher concentration, and the polyaluminum chloride measured at 1.3 NTU. The value of 0.9 was lower than that of (PAC), indicating that suspended solids removal efficiency was superior to that of conventional aluminum flocculant (Table 1).
(LAS)Aluminum sulfate
(LAS)
(PAC)Poly Aluminum Chloride
(PAC)
실시예Example 2 2
응집 교반 시험은 급속 교반 150rpm에서 1분, 완속 교반 50rpm에서 10분 및 20rpm에서 1분, 정치 10분의 조건에서 밑면에서 5cm 지점에서 시료를 채수하고, 원수는 pH 9.54, 탁도 7.41NTU, 수온 10℃ 및 원수 알칼리도 70mg/L인 조건에서 수행하였고, 아민이 혼합된 폴리염화알루미늄칼슘은 30, 35, 40, 45 및 50ppm, 황산알루미늄(LAS) 및 폴리염화알루미늄(PAC)은 45, 50, 55, 60, 65 및 70ppm을 투입하여 응집제 농도별 수처리 기능을 측정하였다. The coagulation agitation test takes 1 minute at 150 rpm for rapid stirring, 10 minutes at 50 rpm for slow stirring, and 1 minute at 20 rpm for 5 minutes at the bottom under standing 10 minutes, and the raw water is pH 9.54, turbidity 7.41 NTU, water temperature 10 It was carried out under the conditions of ℃ and raw water alkalinity 70mg / L, amine-mixed
그 결과 아민이 혼합된 폴리염화알루미늄칼슘은 비교적 낮은 농도로 처리하였을 경우에도 탁도가 현저하게 감소되었고, 50ppm에서 약 0.5NTU로써 같은 농도에서 약 1.1NTU로 측정된 황산알루미늄(LAS) 및 폴리염화알루미늄(PAC)에 비하여 두 배 이상 낮은 수치를 보여, 월등한 수처리 능력을 확인하였다(도 1). 또한, 50ppm의 아민이 혼합된 폴리염화알루미늄칼슘과 70ppm의 황산알루미늄(LAS) 및 폴리염화알루미늄(PAC)을 사용하였을 경우에 약 0.5NTU로서 비숫한 효과를 보여, 본 발명의 아민이 혼합된 폴리염화알루미늄칼슘을 사용하였을 경우 기존의 응집제에 비하여 매우 낮은 농도로 동일한 효과를 얻을 수 있는 것으로 나타남으로써 본 발명의 아민이 혼합된 폴리염화알루미늄칼슘 응집제의 우수한 효능을 확인하였다. As a result, polyaluminum calcium chloride mixed with amines significantly reduced turbidity even when treated at relatively low concentrations. Aluminum sulfate (LAS) and polyaluminum chloride were measured at about 0.5 NTU at 50 ppm and at about 1.1 NTU at the same concentration. (PAC) showed more than twice the value, confirming the superior water treatment capacity (Fig. 1). In addition, when polyaluminum calcium chloride mixed with 50 ppm of amine, 70 ppm of aluminum sulfate (LAS) and polyaluminum chloride (PAC) was used, it showed a similar effect as about 0.5 NTU. When calcium aluminum chloride was used, it was shown that the same effect can be obtained at a very low concentration compared to the existing flocculant, and thus the excellent efficacy of the polyaluminum calcium chloride flocculant mixed with the amine of the present invention was confirmed.
실시예Example 3 3
급속 교반 150rpm에서 1분, 완속 교반 50rpm에서 10분 및 20rpm에서 1분, 정치 10분의 조건에서 밑면에서 5cm 지점에서 시료를 채수하고, 원수는 pH 7.8, 탁도 35NTU, COD 13.80mg/L, 수온 17℃ 및 원수 알칼리도 27mg/L로 탁도가 매우 높은 조건에서 수행하였고, 황산알루미늄(LAS) 75ppm, 폴리염화알루미늄(PAC) 40ppm 및 아민이 혼합된 폴리염화알루미늄칼슘 40ppm을 투입하였다. Samples were taken at 5 cm from the bottom under conditions of rapid stirring at 150 rpm for 1 minute, slow stirring at 50 rpm for 10 minutes and 20 rpm for 1 minute, and stationary for 10 minutes. Raw water was pH 7.8,
그 결과, 아민이 혼합된 폴리염화알루미늄칼슘을 사용한 경우 2.62NTU로 측정된 황산알루미늄(LAS)보다 매우 우수한 응집효능을 보였고, 0.73NTU로 비교적 효과가 좋은 폴리염화알루미늄(PAC)보다도 두 배 이상 낮은 수치를 나타내었다 (표 2).As a result, the use of polyaluminum calcium chloride mixed with amine showed a very good coagulation effect than aluminum sulfate (LAS) measured at 2.62 NTU, and more than twice as low as the relatively effective poly aluminum chloride (PAC) at 0.73 NTU. The figures are shown (Table 2).
(LAS)Aluminum sulfate
(LAS)
(PAC)Poly Aluminum Chloride
(PAC)
도 1은 폴리염화알루미늄칼슘아민(아민이 혼합된 폴리염화알루미늄칼슘), 폴리염화알루미늄(PAC) 및 황산알루미늄(LAS)의 농도별 응집력을 그래프로 나타낸 것이다. 1 is a graph showing the cohesion of polyaluminum chloride amine (polyaluminum chloride mixed with amine), polyaluminum chloride (PAC), and aluminum sulfate (LAS).
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020090085393A KR100960151B1 (en) | 2009-09-10 | 2009-09-10 | Coagulant composition and manufacturing method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020090085393A KR100960151B1 (en) | 2009-09-10 | 2009-09-10 | Coagulant composition and manufacturing method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
KR100960151B1 true KR100960151B1 (en) | 2010-05-28 |
Family
ID=42282154
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR1020090085393A KR100960151B1 (en) | 2009-09-10 | 2009-09-10 | Coagulant composition and manufacturing method thereof |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR100960151B1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101726701B1 (en) * | 2016-09-21 | 2017-04-13 | 주식회사 비봉케미칼 | The polyaluminium chloride for remuval of algae or dinoflagellate, and manufacturing method thereof |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH10503459A (en) * | 1994-03-11 | 1998-03-31 | モザイク タイル アンド ポッタリー カンパニー ピーテーワイ リミテッド | Waste treatment agent |
KR20000038153A (en) * | 1998-12-04 | 2000-07-05 | 박이순 | Purifying method using polymer coagulant |
-
2009
- 2009-09-10 KR KR1020090085393A patent/KR100960151B1/en active IP Right Grant
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH10503459A (en) * | 1994-03-11 | 1998-03-31 | モザイク タイル アンド ポッタリー カンパニー ピーテーワイ リミテッド | Waste treatment agent |
KR20000038153A (en) * | 1998-12-04 | 2000-07-05 | 박이순 | Purifying method using polymer coagulant |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101726701B1 (en) * | 2016-09-21 | 2017-04-13 | 주식회사 비봉케미칼 | The polyaluminium chloride for remuval of algae or dinoflagellate, and manufacturing method thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR101661179B1 (en) | Preparation process of high basic polyaluminium chloride coagulants | |
CN112850867B (en) | Deep defluorination medicament and preparation method thereof | |
KR101752276B1 (en) | Preparing method of poly aluminum chloride inorganic coagulant with low basicity for waste water treatment and purification method of waste water using the inorganic coagulant prepared by the same | |
KR20150091929A (en) | Improved ability to remove fluoride method of producing a coagulant for water treatment and its preparation method of manufacturing a coagulant for water treatment | |
KR101752777B1 (en) | Preparing method of poly aluminum chloride inorganic coagulant with low basicity for waste water treatment and purification method of waste water using the inorganic coagulant prepared by the same | |
KR101128864B1 (en) | Inorganic cohesive agents for water-treatment and Preparing method thereof | |
CN111018169B (en) | Advanced treatment method for cyanogen-fluorine combined pollution wastewater | |
KR101252710B1 (en) | Poly aluminum calcium chloride inorganic coagulant with high basicity for water-treatment and method of preparing the same | |
KR101032478B1 (en) | Water-treatment cohesive agents and Preparing method thereof | |
KR101297435B1 (en) | The preparing method of aluminium sulfate from waste water | |
KR100748601B1 (en) | Preparation method of high basic polyaluminium chloride | |
KR100960151B1 (en) | Coagulant composition and manufacturing method thereof | |
KR100245196B1 (en) | Highly prepolymerized polyaluminium chlorides and their production methods for use as coagulant in water treatment | |
US20100061919A1 (en) | Production of polyaluminum chloride from basic aluminum chloride and sodium aluminate via ultrasonic processing | |
KR101119623B1 (en) | Inorganic cohesive agents for water-treatment and Preparing method thereof | |
KR101157887B1 (en) | Remove the ability of a method for preparing coagulants for water treatment improvements and water treatment coagulants prepared by the method of preparation thereof | |
KR100622295B1 (en) | Preparation method of polyaluminiumchloride | |
KR20050005111A (en) | Manufacturing method of waste water cohesive agents and manufactured goods thereof | |
US6537464B1 (en) | Mid-basicity aluminum compounds and methods of making | |
KR102141652B1 (en) | Method for preparing poly aluminium chloride-based coagulants | |
KR102709790B1 (en) | Method for preparing high-functional fluorine and phosphorus treatment agent for wastewater | |
KR20180014119A (en) | Improved ability to remove fluoride method of producing a coagulant for water treatment and its preparation method of manufacturing a coagulant for water treatment | |
CN109534467A (en) | A kind of high-performance aluminium polychloride and preparation method thereof | |
KR100192872B1 (en) | Poly aluminum calcium chloride and process for preparation thereof | |
JP2005262186A (en) | Method for treating boron-containing waste water |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
A302 | Request for accelerated examination | ||
E902 | Notification of reason for refusal | ||
E701 | Decision to grant or registration of patent right | ||
GRNT | Written decision to grant | ||
FPAY | Annual fee payment |
Payment date: 20130417 Year of fee payment: 4 |
|
FPAY | Annual fee payment |
Payment date: 20140314 Year of fee payment: 5 |
|
FPAY | Annual fee payment |
Payment date: 20150519 Year of fee payment: 6 |
|
FPAY | Annual fee payment |
Payment date: 20160512 Year of fee payment: 7 |
|
FPAY | Annual fee payment |
Payment date: 20170522 Year of fee payment: 8 |
|
FPAY | Annual fee payment |
Payment date: 20180509 Year of fee payment: 9 |