KR101297435B1 - The preparing method of aluminium sulfate from waste water - Google Patents

The preparing method of aluminium sulfate from waste water Download PDF

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KR101297435B1
KR101297435B1 KR1020110120001A KR20110120001A KR101297435B1 KR 101297435 B1 KR101297435 B1 KR 101297435B1 KR 1020110120001 A KR1020110120001 A KR 1020110120001A KR 20110120001 A KR20110120001 A KR 20110120001A KR 101297435 B1 KR101297435 B1 KR 101297435B1
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wastewater
sulfuric acid
aluminum
present
sulfate
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KR1020110120001A
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Korean (ko)
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KR20130054557A (en
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최동민
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주식회사 워켐
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/68Aluminium compounds containing sulfur
    • C01F7/74Sulfates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/40Valorisation of by-products of wastewater, sewage or sludge processing
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies

Abstract

본 발명은 산업현장에서 발생하는 폐수 및 폐기물을 재활용하여 무기응집제 를 제조하는 방법을 제공한다. Alum 제조공법에 의거 폐수 내의 알루미늄 성분을 전 처리하여 재활용하여 기존 응집제들에 비하여 원가는 저렴하면서도 품질이 우수한 무기응집제를 제조하는 방법에 관한 것이다.The present invention provides a method for producing an inorganic coagulant by recycling wastewater and waste generated in an industrial field. The present invention relates to a method of preparing inorganic coagulants having high quality and low cost compared to existing coagulants by pre-treating and recycling aluminum components in wastewater based on the Alum manufacturing method.

Description

폐수 및 폐기물로부터 황산 알루미늄의 제조방법{The preparing method of aluminium sulfate from waste water}The preparing method of aluminum sulfate from waste water

본 발명은 폐수 및 폐기물로부터 황산 알루미늄의 제조방법에 관한 것으로, 더욱 상세하게는 폐수 처리에 사용되는 무기 응집제에 이용되는 알루미늄을 폐수 및 폐기물로부터 회수하여 재활용하는 방법에 관한 것이다.
The present invention relates to a method for producing aluminum sulfate from wastewater and waste, and more particularly, to a method for recovering and recycling aluminum used in inorganic flocculants used for wastewater treatment from wastewater and waste.

본 발명은 폐수 및 폐기물로부터 황산 알루미늄의 제조방법에 관한 것으로, 더욱 상세하게는 폐수 처리에 사용되는 무기 응집제에 이용되는 알루미늄을 폐수 및 폐기물로부터 회수하여 재활용하는 방법에 관한 것이다.The present invention relates to a method for producing aluminum sulfate from wastewater and waste, and more particularly, to a method for recovering and recycling aluminum used in inorganic flocculants used for wastewater treatment from wastewater and waste.

무기응집제는 폐수에 포함된 유기성, 무기성 콜로이드 입자의 표면전하를 중화시킴으로서 콜로이드 입자를 응집시키고 침강시켜 제거하는 약품이다. 처리된 폐수의 수질을 개선시킬 목적으로, 오래 전부터 사용해 오고 있는 폐수처리 중요한 약품 중 하나이다.Inorganic coagulant is a drug that coagulates and precipitates colloidal particles by neutralizing the surface charge of organic and inorganic colloid particles contained in wastewater. It is one of the important wastewater treatment chemicals that has been used for a long time in order to improve the quality of treated wastewater.

이러한 무기 응집제 가운데, 대표적인 것으로 Alum(황산 알루미늄), 황산철, 염화철, PAC 등이 있고, 산업체 폐수처리장 수질에 따라 가장 일반적으로 Alum이나 제이철염을 보통 사용하고 있다.
Representative examples of such inorganic flocculants include Alum (aluminum sulfate), iron sulfate, iron chloride, and PAC, and most commonly Alum or Ferric Salt are used depending on industrial wastewater treatment water quality.

본 발명은 폐수 및 폐기물로부터 황산 알루미늄을 회수하여 재활용하는 방법을 제공하는 것이다.
The present invention provides a method for recovering and recycling aluminum sulfate from wastewater and wastes.

황산 알루미늄을 제조하기 위해서는 수산화알루미늄과 황산을 반응시켜 제조하며 반응식은 다음과 같다.In order to prepare aluminum sulfate, aluminum hydroxide and sulfuric acid are reacted, and a reaction formula is as follows.

2Al(OH)3 + 3H2SO4 → Al2(SO4)3· 6H2O 2Al (OH) 3 + 3H 2 SO 4 → Al 2 (SO 4) 3 · 6H 2 O

또한, 이렇게 회수된 황산알루미늄을 제이철염과 혼합하여 사용하면, 황산알루미늄과 제이철염의 장단점을 상호보완한 무기 응집제를 제조할 수 있다.
When the aluminum sulfate thus recovered is mixed with ferric salt, an inorganic flocculant having complementary advantages and disadvantages of aluminum sulfate and ferric salt can be produced.

본 발명의 제조방법에 의해 폐기물 및 폐수로부터 알루미늄을 회수하여 재활용함으로써 환경오염 방지와 자원 재활용 효과를 나타낼 수 있다. By recovering and recycling aluminum from waste and wastewater by the manufacturing method of the present invention, it is possible to exhibit environmental pollution prevention and resource recycling effects.

또한, 본 발명에 의해 제조된 황산 알루미늄과 제이철염을 혼합한 무기 응집제는 콜로이드의 흡착력, 슬러지 침강성이 우수하고, COD 및 중금속 처리효율에서 기존 무기응집제에 비해 탁월한 성능을 모두 가지고 있다.
In addition, the inorganic flocculant mixed with aluminum sulfate and ferric salt prepared according to the present invention is excellent in the adsorption power of the colloid, sludge settling properties, and excellent performance compared to the conventional inorganic coagulant in COD and heavy metal treatment efficiency.

황산 알루미늄을 제조하기 위해서는 수산화알루미늄과 황산을 반응시켜 제조하며 반응식은 다음과 같다In order to prepare aluminum sulfate, it is prepared by reacting aluminum hydroxide with sulfuric acid.

2Al(OH)3 + 3H2SO4 → Al2(SO4)3· 6H2O 2Al (OH) 3 + 3H 2 SO 4 → Al 2 (SO 4) 3 · 6H 2 O

본 발명의 제조방법에서는 폐수 및 폐기물 내의 알루미늄 성분을 원료로 재활용하고 폐수 및 폐기물 내 포함된 산(acid)들도 재활용한다. In the manufacturing method of the present invention, aluminum components in the wastewater and the waste are recycled as raw materials, and acids contained in the wastewater and the waste are also recycled.

본 발명의 제조방법은 황산을 투입하여 황산의 용해열과 중화반응열을 이용하여 110~115℃에서 충분히 반응시키고, 이후 50℃이하로 냉각하는 것으로 구성된다. The production method of the present invention consists of adding sulfuric acid to sufficiently react at 110 ~ 115 ℃ using the heat of dissolution and neutralization reaction heat of sulfuric acid, and then cooled to 50 ℃ or less.

상세하게 설명하면 다음과 같다. The details are as follows.

보온이 철저히 된 반응기에 재활용 수산화알루미늄, 전처리된 알루미늄 포함 폐수, 재활용 수산화알루미늄 Cake 등(재활용 수산화알루미늄 - Al(OH)3 97.5%, 재활용 수산화알루미늄 Cake - Al(OH)3 25.0%, 재활용 알루미늄 폐수 - Al2O3 17%)을 투입하고 충분한 슬러리 상태가 이루어지도록 교반한다.Recycled aluminum hydroxide, wastewater containing pretreated aluminum, recycled aluminum hydroxide cake, etc. (recycled aluminum hydroxide-Al (OH) 3 97.5%, recycled aluminum hydroxide cake-Al (OH) 3 25.0%, recycled aluminum wastewater Add Al 2 O 3 17%) and stir to achieve a sufficient slurry.

다음 단계에서 투입하는 진한 황산과 혼합되었을 때 초기 형성되는 황산의 농도가 60~ 70%가 되도록 1차 용수를 공급한다.When mixed with the concentrated sulfuric acid introduced in the next step, the primary water is supplied so that the concentration of sulfuric acid formed is 60-70%.

반응식에 의거 계산된 진한 황산을 원활하게 투입하기 위하여 Dipping배관을 반응기 바닥 가까이에 설치하고 약 30분에 걸쳐서 투입되도록 정량 펌프를 가동한다.In order to smoothly add the concentrated sulfuric acid calculated according to the reaction scheme, a dipping pipe is installed near the bottom of the reactor, and the metering pump is operated to be added for about 30 minutes.

반응기 내부 액은 황산이 물에 용해될 때 발생하는 용해열에 의해 온도가 상승하기 시작하며 중화 반응열과 함께 100℃까지 상승하게 되면 Boiling 상태가 된다. 이 시점에서 황산투입을 중지한다. The liquid inside the reactor starts to rise in temperature due to the heat of dissolution generated when sulfuric acid is dissolved in water. At this point, sulfuric acid injection is stopped.

이후에는 중화반응열의 상승작용에 의해서 온도가 115℃ 정도로 상승하게 된다. 온도가 다시 하강하기 시작하면 반응기 내부온도가 110 ~ 115℃가 유지되도록 정량 펌프의 유량을 조절하여 잔여 황산을 투입한다.Thereafter, the temperature rises to about 115 ° C by synergy of the heat of neutralization reaction. When the temperature starts to fall again, the remaining sulfuric acid is added by adjusting the flow rate of the metering pump so that the reactor internal temperature is maintained at 110 ~ 115 ℃.

황산 알루미늄 제조반응의 종료는 반응액 온도를 기준하여 112℃에서 120분 반응을 기준으로 한다.The completion of the aluminum sulfate production reaction is based on a 120-minute reaction at 112 ° C based on the reaction solution temperature.

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

<실시예 1>&Lt; Example 1 >

재활용 수산화알루미늄과 재활용 알루미늄 포함폐수 사용 예Examples of recycled aluminum hydroxide and recycled aluminum wastewater

4L 4구 둥근 플라스크에 재활용 수산화알루미늄 200g과 재활용 알루미늄 포함폐수 100g을 투입하고 1차 용수 325g을 가한 다음 완전히 슬러리화 할 수 있도록 교반하였다. 98% 황산 452g을 천천히 투입하니 황산 용해열과 중화 반응열이 발생하여 온도가 상승하기 시작하였다. 100℃부근에서 Boiling 하기 시작하면 황산투입을 중지하고 110~115℃가 될 때까지 기다렸다. 온도가 하강하기 시작하면 잔여황산을 천천히 투입하여 온도가 110~115℃가 유지되도록 하였다. 반응의 종료는 반응액 온도를 기준하여 112℃에서 120분 반응을 기준으로 하였다.
200 g of recycled aluminum hydroxide and 100 g of wastewater containing recycled aluminum were added to a 4L four-necked round flask, and 325 g of primary water was added thereto, followed by stirring to fully slurry. When 452 g of 98% sulfuric acid was slowly added, the heat of dissolution of sulfuric acid and the heat of neutralization reaction were generated and the temperature started to rise. When boiling was started at around 100 ℃, sulfuric acid was stopped and waited until it reached 110 ~ 115 ℃. When the temperature began to drop, the remaining sulfuric acid was slowly added to maintain the temperature of 110-115 ° C. Termination of the reaction was based on the reaction 120 minutes at 112 ℃ based on the reaction solution temperature.

<제조예 1>&Lt; Preparation Example 1 &

실시예 1에서 제조된 반응생성물에 황산 제이철을 부가하고 용수를 부가하여 황산알루미늄의 농도는 5% 황산 제2철의 농도는 2%가 되도록 조절하였다. 최종 제품의 무게는 2865g이었다. 24시간 숙성시킨 후 여과하여 제품화하였다.
Ferric sulfate was added to the reaction product prepared in Example 1 and water was added to adjust the concentration of aluminum sulfate to 5% and the concentration of ferric sulfate to 2%. The final product weighed 2865 g. After aging for 24 hours, the product was filtered.

<제조예 2>&Lt; Preparation Example 2 &

황산 제이철 대신 염산 제이철을 사용하는 것을 제외하고는 제조예 1과 같이 제조하였다.
It was prepared in the same manner as in Preparation Example 1 except that ferric hydrochloride was used instead of ferric sulfate.

<시험예><Test Example>

제조예 1,2,3 3종을 일반적으로 산업체에 사용하고 있는 7% 황산알루미늄과 10% 제이철염을 비교 시험하여 본 발명품을 평가하였다.
Preparation Example 1, 2, 3 Three kinds of 7% aluminum sulfate and 10% ferric salt, which are generally used in industry, were tested to evaluate the present invention.

-표준 폐수 성상- Standard wastewater characteristics

ItemsItems 단위unit ResultsResults pHpH -- 10.510.5 CODCOD mg/ℓmg / l 1,0251,025 T-NT-N mg/ℓmg / l 2222 T-PT-P mg/ℓmg / l 1313 SSSS mg/ℓmg / l 862862 T-CrT-Cr mg/ℓmg / l 2.52.5 AsAs mg/ℓmg / l 2.02.0 PbPb mg/ℓmg / l 1.51.5 CuCu mg/ℓmg / l 2.42.4

- 시험 조건- Exam conditions

1) 무기응집제 : 각각의 제품 별로 동일량 투입1) Inorganic coagulant: the same amount for each product

2) pH 중화제 : 25% 소석회수 (pH Target 7.0)2) pH neutralizer: 25% lime water (pH Target 7.0)

3) 중합체 : A-230E (음이온 계)
3) Polymer: A-230E (Anionic)

- 시험 결과- Test result

7% 7% AlumAlum 10%   10%
제이철염   Ferric salt
본 발명품(The present invention ( Al2O3Al2O3 5.0%+ 5.0% + Fe3Fe3 + 2.0%)+ 2.0%)
제조예Manufacturing example 1 One 제조예Manufacturing example 2 2
응집제 투입량(ppm)Coagulant input (ppm) 500500 500500 500500 500
500
중화제 투입량(ppm)Neutralizing agent input (ppm) 1,2001,200 1,3501,350 1,1501,150 1,150
1,150
Polymer 투입량(ppm)Polymer input (ppm) 44 44 44 4
4
Floc Size (mm)Floc Size (mm) 1.5 ~ 2.251.5 to 2.25 1.0 ~ 1.51.0 to 1.5 2.25 ~ 3.02.25 to 3.0 2.25 ~ 3.0
2.25 to 3.0
SV30 (%)SV30 (%) 2222 1414 1616 16
16
처리수Treated water 수질 Water quality COD (ppm)COD (ppm) 565565 600600 520520 515
515
COD 제거율(%)COD Removal Rate (%) 44.944.9 41.541.5 49.349.3 49.8
49.8
T-N (ppm)T-N (ppm) 1616 1717 1414 14
14
T-P (ppm)T-P (ppm) 1.51.5 1.71.7 1.31.3 1.3
1.3
SS (ppm)SS (ppm) 1212 1010 88 7
7
T-Cr (ppm)T-Cr (ppm) 1.01.0 1.01.0 0.40.4 0.4
0.4
As (ppm)As (ppm) 0.60.6 0.50.5 0.30.3 0.3
0.3
Pb (ppm)Pb (ppm) 0.60.6 0.50.5 0.20.2 0.2
0.2
Cu (ppm)Cu (ppm) 0.70.7 0.60.6 0.20.2 0.2
0.2
SludgeSludge 발생량 Generation O.D (gr/ℓ)O.D (gr / l) 2.0242.024 2.5202.520 1.9541.954 2.000
2.000

기존 시판 응집제인 7% 황산알루미늄 및 10% 제이철염 사용대비 본 발명의 제조예 1, 2 의 제품은 CDD 제거율이 우수하고, 중금속 제거율이 우수하며, Floc 침강성이 우수하고, 처리수 중 SS 함량이 낮으며 Sludge 탈수 속도가 우수함을 알 수 있다.The products of Preparation Examples 1 and 2 of the present invention have excellent CDD removal rate, good heavy metal removal rate, good floc sedimentation, and SS content in treated water, compared to the existing commercially available coagulant, 7% aluminum sulfate and 10% ferric salt. It is low and the sludge dewatering speed is excellent.

Claims (3)

알루미늄을 포함한 폐수 및 폐기물에 황산을 투입하여 황산의 용해열과 중화반응열을 이용하여 110~115℃에서 2시간 동안 반응시킨 후 10 내지 50℃의 온도로 냉각하는 것을 특징으로 하는 황산알루미늄의 제조방법.
The sulfuric acid is added to the wastewater and wastes containing aluminum and reacted at 110 to 115 ℃ for 2 hours using the heat of dissolution and neutralization reaction of sulfuric acid, and then cooled to a temperature of 10 to 50 ℃.
삭제delete 제 1항 의해 얻어진 황산알루미늄 및 황산 또는 염산의 제이철염으로 이루어지는 것을 특징으로 하는 폐수 처리용 무기 응집제.An inorganic flocculant for wastewater treatment, comprising ferric salt of aluminum sulfate and sulfuric acid or hydrochloric acid obtained according to claim 1.
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Publication number Priority date Publication date Assignee Title
KR101790289B1 (en) * 2017-04-14 2017-10-27 주식회사 태원 Method of manufacturing ferric sulfate solutions which has low concentration of free acid with improved filtration
KR101980478B1 (en) 2018-01-19 2019-05-21 신태욱 Manufacturing method of inorganic coagulants used acid waste water for treatment an activated clay
KR102630157B1 (en) 2023-09-25 2024-01-29 주식회사 그린이앤씨 Aluminium sulfate manufacture system and manufacture method

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SE539935C2 (en) * 2016-06-16 2018-01-30 Hans Ulmert Med Firma Flocell Method for the recovery of coagulants from the sewage sludge from water and sewerage plants

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KR19990001532A (en) * 1997-06-16 1999-01-15 김명호 Manufacturing method of inorganic polymer flocculant mainly composed of aluminum chloride
KR100947674B1 (en) 2009-02-11 2010-03-12 (주) 에코솔루텍 Manufacture method of high functional cohesive agent for water-treatment

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KR19990001532A (en) * 1997-06-16 1999-01-15 김명호 Manufacturing method of inorganic polymer flocculant mainly composed of aluminum chloride
KR100947674B1 (en) 2009-02-11 2010-03-12 (주) 에코솔루텍 Manufacture method of high functional cohesive agent for water-treatment

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101790289B1 (en) * 2017-04-14 2017-10-27 주식회사 태원 Method of manufacturing ferric sulfate solutions which has low concentration of free acid with improved filtration
KR101980478B1 (en) 2018-01-19 2019-05-21 신태욱 Manufacturing method of inorganic coagulants used acid waste water for treatment an activated clay
KR102630157B1 (en) 2023-09-25 2024-01-29 주식회사 그린이앤씨 Aluminium sulfate manufacture system and manufacture method

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