KR960002266B1 - Treatment method for waste water of emulsion type - Google Patents

Treatment method for waste water of emulsion type Download PDF

Info

Publication number
KR960002266B1
KR960002266B1 KR1019930014793A KR930014793A KR960002266B1 KR 960002266 B1 KR960002266 B1 KR 960002266B1 KR 1019930014793 A KR1019930014793 A KR 1019930014793A KR 930014793 A KR930014793 A KR 930014793A KR 960002266 B1 KR960002266 B1 KR 960002266B1
Authority
KR
South Korea
Prior art keywords
waste water
water
emulsion
wastewater
naoh
Prior art date
Application number
KR1019930014793A
Other languages
Korean (ko)
Other versions
KR950003183A (en
Inventor
조범연
Original Assignee
주식회사중원산업
조범연
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 주식회사중원산업, 조범연 filed Critical 주식회사중원산업
Priority to KR1019930014793A priority Critical patent/KR960002266B1/en
Publication of KR950003183A publication Critical patent/KR950003183A/en
Application granted granted Critical
Publication of KR960002266B1 publication Critical patent/KR960002266B1/en

Links

Classifications

    • 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
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular 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

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The treatment of water-soluble oil waste water, such as paraffin wax emulsion, silicon oil emulsion or edible oil emulsion, comprises (A) adjusting the pH of the oily waste water at 4 by adding HCl or NaOH ; (B) adding inorganic polymer compound of formula PHC(Al2(OH)2-Cl6-n)m in the ratio of 1-5% with respect to waste water, where n=1-5 and m<=10 ; (C) adjusting the pH at 7 by adding NaOH ; (D) maintaining the concentration of waste water at 0.05-0.1% ; and (E) adding a polymer compound to produced nuclei to make the big flocs with high density.

Description

에멀죤 폐수의 처리방법Treatment of Emulsion Wastewater

본 발명은 파라핀 왁스 에멀죤, 실리콘오일 에멀죤, 기타 광유 및 식용유 에멀죤을 포함하는 수용성 오일 폐수를 상온 상압하에서 반응 침전 분리하여 맑은 처리액을 얻는것을 특징으로 하는 에멀죤 폐수의 처리방법에 관한 것이다.The present invention relates to a method for treating emulsion zone wastewater, wherein the water-soluble oil wastewater including paraffin wax emulsion zone, silicone oil emulsion zone, other mineral oil and edible oil emulsion zone is reacted and precipitated under normal temperature and pressure to obtain a clear treatment liquid. will be.

수용성 오일폐수의 처리방법은 PH를 산성으로 한후, 무기 전해질을 가해 유분을 유리시키며 부상법으로 처리하나, 이때 여과분리 작업 후 슬러지와는 별도로 나머지 폐수도 생물학적인 처리방법이 뒤따라야만 처리가 가능하며, 그밖에 악화 소각법, 증발농축법 등은 설치비 및 처리비가 높은 결점과 소각시 분건 및 미연 가스등의 오염물질이 발생되어 대기 오염을 유발시키는 등의 결점이 발생되었다.The treatment method of water-soluble oil wastewater is acidified, and then inorganic minerals are added to release the oil and treated by flotation.In this case, the remaining wastewater is separated from the sludge after the filtration and separation treatment only after biological treatment. In addition, defects such as deterioration incineration and evaporative enrichment have high installation and processing costs, as well as defects such as pollutants such as dust and unburned gas during incineration, causing air pollution.

따라서 본 발명은 이와같은 종래의 결점을 해결하기 위하여 안클린 것으로 본 발명은 산성전해질 용액과 고분자 화합물로 복합시킨 약제를 주입해서 FLOC의 핵 (NUCLEAR)을 만든 다음에 고분자 화합물을 가해 거대한 FLOS을 형성시켜 간단히 처리하고, 응집이 침전된 수용성 오일은 여과분리하여 여과액은 방류하며, 이때 COD가 높으면 적당량의 과산화 수소를 첨가하거나 COD 제거제(흡착제)로 간단히 처리한다.Therefore, the present invention is not in order to solve such a conventional defect, the present invention is injected into a drug complexed with an acidic electrolyte solution and a polymer compound to make a nucleus (FLCL) of the FLOC and then add a polymer compound to form a huge FLOS The water-soluble oil precipitated by flocculation is separated by filtration and the filtrate is discharged. If the COD is high, an appropriate amount of hydrogen peroxide is added or simply treated with a COD remover (adsorbent).

이때 수용성 오일슬러지는 건조후 소각처리함을 특징으로 한다.At this time, the water-soluble oil sludge is characterized by incineration after drying.

이하 본 발명의 바람직한 실시예를 상세히 설명하기로 한다.Hereinafter, a preferred embodiment of the present invention will be described in detail.

1) 약재의 제조1) Manufacture of Herbs

(1) 전기의 산성 전해질 용액은 금속의 화합물 알카 금속의 염화물을 포함하여 CHCL2, ALCL3, AL2(SO4)3, FESO4, FECL3, MGCL2, MGSO4등이 사용된다.(1) For the acidic electrolyte solution, CHCL 2 , ALCL 3 , AL 2 (SO 4 ) 3 , FESO 4 , FECL 3 , MGCL 2 , MGSO 4, and the like, including chlorides of the metal compounds of the alkali metals, are used.

(2) 산성 전해질에 배합되는 고분자 화합물(이하 A 약제라 함)의 제조.(2) Preparation of a high molecular compound (hereinafter referred to as A drug) blended in an acidic electrolyte.

산성 전해질에 배합되는 고분자 화합물은 폴리아미드, 폴리 아크릴산, 폴리 메타아크릴 레이드 등이 포함되며 산성 전해질 용액과 고분자 화합물은 1 : 0.0001-1 : 0.01의 비율로 후합사용한다.The polymer compound blended with the acidic electrolyte includes polyamide, polyacrylic acid, polymethacrylate, and the like. The acidic electrolyte solution and the polymer compound are post-polymerized at a ratio of 1: 0.0001-1: 0.01.

(3) FLOC을 형성시키는 고분자 화합물(이하 B 약제라 함)의 제조.(3) Preparation of a high molecular compound (hereinafter referred to as B drug) that forms FLOC.

거대한 FLOC을 형성시키는 고분자 화합물은 폴리아미드계의 음이온 고분자 화합물로서, 분자량은 1,000-5,000의 것을 사용한다.The high molecular compound which forms huge FLOC is an anionic high molecular compound of polyamide type | system | group, The molecular weight uses the thing of 1,000-5,000.

2) 기초이론(Basic Theory)2) Basic Theory

(1) Flocculant은 입자의 전하를 중화하고 입자와 입자간을 얽어매어 단단한 Floc을 형성시키는 것이며, Flocculant는 고분자 물질에 여러개의 극성기를 갖는, 마치 문어발처럼 길다란 줄기에 여러개의 흡판을 가진 형태의 분자구조를 가지고 있다.(1) Flocculant neutralizes the charge of the particles and binds them together to form a solid Floc.Flocculant is a molecule with multiple polarizers in polymer material with multiple suckers on a long stem like an octopus. It has a structure.

(2) flocculant Appication(2) flocculant Appication

응집제는 적당량 투입해야 하며, 과잉 투입시 코로이드 입자표면의 흡착 활성점을 고분자 응집제자신이 전부 점유해 버리므로 다른 입자와의 교량역할을 하지 못하며, 더우기 응집제는 친수성이므로 보호 보호코로이드 기능을 발휘하여 입자를 둘러싸 안정화 시키므로 응집이 분산된다.The coagulant must be added in an appropriate amount, and the coagulant itself occupies all the adsorption active sites on the surface of the colloidal particles. Therefore, the coagulant cannot act as a bridge with other particles. By enclosing and stabilizing particles, aggregation is dispersed.

(3)용해과정(3) Dissolution process

희석수의 수질에 의해 분자구조가 실타쾌가 뭉친것 같은 형태에서 길게 퍼져서 자체의 분자량 길이를 발휘하도록 한다.The water quality of the dilution water spreads the molecular structure long in the form of agglomeration of the practicality to show its molecular weight length.

이때 분자구조가 얼마나 길게 퍼져서 자체의 분자량 길이를 발휘하느냐에 따라 고분자 응집제의 성능을 좌우하게 된다.At this time, the performance of the polymer flocculant depends on how long the molecular structure spreads and exhibits its molecular weight.

(4) Weeting(4) Weeting

분말의 입자표면에 물을 고르게 젖게 하므로써 덩어리로 뭉치는 Fish Eye를 방지해야 한다.Water should be evenly wetted on the surface of the powder to prevent clumping of fish eyes.

(5) Stirring(5) Stirring

예리(Sharp)한 날개(Wing)의 형태보다는 넓은 면적의 아지 테이터로 저속회전시켜서 분자의 손상이 없이 고르게 섞이도록 한다.It rotates slowly with a large area of agitator rather than in the form of sharp wings to mix evenly without damaging the molecules.

(6) Aging(6) Aging

Aging은 분자 응집제의 분자의 길이를 100% 퍼지게 하는 공정으로 시간과 stirring Rate가 관계된다.Aging is a process that spreads the length of a molecule of molecular coagulant 100%, which is related to time and stirring rate.

(7) Theory(7) Theory

현탁액중 입자크기가 10-7~10-5㎝정도로 아주 작아서 진비중이 1보다는 크지만 겉보기 비중이 물과 비슷하여 침강하지 않고 수표면에 떠오르지도 않는 입자는 압자표면에 물분자층이 둘러싼 형태로 있게 되면(+) 또는 (-)의 같은 전하끼리 대전할 땐 서로 반발을 일으켜 칩전하지 못한다.The particle size of the suspension is very small (10 -7 ~ 10 -5 ㎝) and the specific gravity is greater than 1, but the apparent specific gravity is similar to water, so that the particles that do not settle and do not float on the surface of the water are surrounded by a layer of water molecules. When the (+) or (-) of the same charge when the charge to each other will cause a backlash and can not chip.

이 입자는 전기적 반발력인 Zeta potential, 전기적 인력인 Vander Waals 중력에 의해 전기역학적으로 전위상 평형이 되어있다.The particles are electrodynamically equilibrium by Zeta potential, the electrical repulsion, and Vander Waals' gravity, the electrical attraction.

따라서 콜로이드는 전기적으로 대전되어 있고, 서로 잡아당기고 밀어내는 중력이 작용하면서 평형이 되어 항상 안정한 상태로 있으려는 경향이 있다.Thus, colloids are electrically charged and tend to be in equilibrium at all times by the gravitational pull of each other.

이때 물 결합층의 경계면의 발생하는 전위를 Zeta potential 이라 하며, 보통 Zeta potential은 -20~50m정도이고 이 분산계에 (+)전하를 띤 콜로이드 및 이온(A 약제)을 첨가하여 전하를 중화시켜서 현탁입자의 Zeta 전위가 ±10m가 되면 입자 사이의 반발력이 인력보다 작아져 응고(Coag ulalation)가 일어난다.At this time, the potential generated at the interface of the water-bonding layer is called Zeta potential. Usually, the Zeta potential is about -20 ~ 50m, and it is suspended by neutralizing the charge by adding (+) charged colloid and ion (A drug) to this dispersion system. When the Zeta potential of the particles reaches ± 10m, the repulsive force between the particles becomes smaller than the attraction force, causing coag ulalation.

이때 응고에 의해 생성된 Nuclear에 (B 약제)를 첨가하여 보다 큰 Floc로 만들어 걷보기 비중을 무겁게 함으로써 침강속도를 빠르게 처리하는 방법이다.At this time, (B drug) is added to the Nuclear produced by coagulation to make a larger floc, thereby increasing the specific gravity of the walking, and thus speeding up the settling speed.

[실시예]EXAMPLE

1) 셈플의 일정량을 HCL 또는 NaOH에 의해 PH를 4로 조절한다.1) A certain amount of the sample is adjusted to 4 by HCL or NaOH.

2) PHC(AL2(OH)2-Cl6-n)m으로써, N=1-5. M=10 이하의 무기고분자 화합물 투입2) PHC (AL 2 (OH) 2 -Cl 6 -n) m, with N = 1-5. Inorganic high molecular compound below M = 10

a) 수용액중에 투입시 알루미늄 이온을 함유하는 고분자 이온과 탁질 사이에 전하의 중화가 일어나고, 또 이들의 가수분해에 의해서 생기는 수산화알루미늄의 탁질을 급속히 응집하여 floc을 크게 형성하여 극히 빠르게 침강하는 상태로 된다.a) Neutralization of charges occurs between the polymer ions containing aluminum ions and the turbidity in the aqueous solution, and rapidly flocculates the turbidity of aluminum hydroxide produced by their hydrolysis to form large floc and settles extremely rapidly. do.

b) 여기서 농도를 폐수성상에 따라 다르나 통상 폐수대비 1-5%가 하여 미세한 floc의 핵을 형성시킨다.b) The concentration here depends on the wastewater phase, but is usually less than 1-5% of the wastewater to form a fine floc nucleus.

3) NaOH에 의해 PH를 7로 조절한다.3) Adjust pH to 7 with NaOH.

4) polymer4) polymer

생성된 Nuclear을 크고, 비중이 크게 생성시키는 결과를 낳으며, 이때 농도는 통상 0.05-0.1% 정도가 되도록 하나, 현탁입자의 양과 폐수의 성상에 따라 약간의 차이가 있다.The produced Nuclear is large and the specific gravity is large, and the concentration is usually about 0.05-0.1%, but there is a slight difference depending on the amount of suspended particles and the properties of the wastewater.

이상에서 밝힌바와 같이 본 발명은 일반적인 수용성 오일폐수를 손쉽고 신속하게 처리할 수 있다.As described above, the present invention can easily and quickly treat a general water-soluble oil wastewater.

처리가 간단하고 비용이 저렴하며, 탁도 및 COD 제거율이 수용성 폐수는 물론 일반 폐수에도 유용하다.The treatment is simple and inexpensive, and the turbidity and COD removal rate is useful for water soluble waste and general waste water.

일반 폐수성상에 따라 약제의 사용농도가 약간씩 차이가 있으며, 대기오염을 유발시키지 않고 처리할 수 있는 효과가 제공된다.There is a slight difference in the use concentration of the drug according to the general wastewater phase, it provides an effect that can be treated without causing air pollution.

Claims (1)

파라핀 왁스 에멀죤, 실리콘오일 에멀죤, 식용유 에멀죤 등의 수용성 오일폐수를 처리함에 있어서, 수용성 오일폐수에 HCl 또는 NaoH를 넣어 PH를 4로 조절하는 과정과, PHC(AL2(OH)2--Cl6-n)m 으로써, N=1-5, M=10 이하의 무기고분자 화합물을 폐수대비 1-5% 투입하는 과정과, NaoH를 투입 PH를 7로 조절하는 과정과, 농도를 0.05-0.1% 정도로 하며 생성된 Nuclear에 고분자 화합물을 투입해 Floc을 크고 비중이 크게 처리함을 특징으로 하는 에멀죤 폐수의 처리방법.In treating water-soluble oil wastewater such as paraffin wax emulsion, silicone oil emulsion and cooking oil emulsion, the process of adjusting pH to 4 by adding HCl or NaoH to the water-soluble oil wastewater, and PHC (AL 2 (OH) 2- -Cl 6-n ) m, the process of adding inorganic polymer compound of N = 1-5, M = 10 or less 1-5% of the waste water, the process of adjusting the input pH to 7 with NaoH, and the concentration is 0.05 Emulsion wastewater treatment method characterized in that the floc large and large specific gravity treatment by adding a high-molecular compound to the produced Nuclear about -0.1%.
KR1019930014793A 1993-07-28 1993-07-28 Treatment method for waste water of emulsion type KR960002266B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1019930014793A KR960002266B1 (en) 1993-07-28 1993-07-28 Treatment method for waste water of emulsion type

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1019930014793A KR960002266B1 (en) 1993-07-28 1993-07-28 Treatment method for waste water of emulsion type

Publications (2)

Publication Number Publication Date
KR950003183A KR950003183A (en) 1995-02-16
KR960002266B1 true KR960002266B1 (en) 1996-02-14

Family

ID=19360527

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1019930014793A KR960002266B1 (en) 1993-07-28 1993-07-28 Treatment method for waste water of emulsion type

Country Status (1)

Country Link
KR (1) KR960002266B1 (en)

Also Published As

Publication number Publication date
KR950003183A (en) 1995-02-16

Similar Documents

Publication Publication Date Title
Rattanakawin et al. Aggregate size distributions in flocculation
Zouboulis et al. Treatment of oil-in-water emulsions by coagulation and dissolved-air flotation
Shaikh et al. Investigation of the effect of polyelectrolyte structure and type on the electrokinetics and flocculation behavior of bentonite dispersions
Al-Shamrani et al. Destabilisation of oil–water emulsions and separation by dissolved air flotation
Larue et al. Electrocoagulation and coagulation by iron of latex particles in aqueous suspensions
US3701417A (en) Purification of clay by selective flocculation
Hu et al. Enhanced efficiency in HA removal by electrocoagulation through optimizing flocs properties: Role of current density and pH
Hogg et al. Chemical and physical variables in polymer-induced flocculation
Xiong et al. Coupling magnetic particles with flocculants to enhance demulsification and separation of waste cutting emulsion for engineering applications
Wang et al. Flocculation of quartz by a dual polymer system containing tannic acid and poly (ethylene oxide): Effect of polymer chemistry and hydrodynamic conditions
Ries Jr et al. Microelectrophoresis and electron‐microscope studies with polymeric flocculants
Priesing A theory of coagulation useful for design
MXPA97002416A (en) Procedure for purification of polluted waste that contains suspended particulars and flammable composition for the mi
JPH10506570A (en) Purification process of polar liquid waste containing suspended solvated particles and agglomerated compositions therefor
KR960002266B1 (en) Treatment method for waste water of emulsion type
Zhong et al. Effects of humic acid on recoverability and fractal structure of alum-kaolin flocs
Mackrle Mechanism of coagulation in water treatment
JPH10272304A (en) Inorganic electrolytic flocculating agent
Liu et al. Improved coagulation performance using preformed polymeric iron chloride (PICl)
KR101088148B1 (en) Electrical neutralization of colloidal particles with speed control how water
Kowalska et al. Ultrasound in the suspension separation methods
Liu et al. Colloid interaction and coagulation of dye wastewater with extra application of magnetites
US3235491A (en) Method of flocculating mineral solids colloidally suspended in an aqueous medium
Sawain et al. The Effect of pH on the stability of grease and oil in wastewater from biodiesel production process
US20190202720A1 (en) Method for purifying food and meat processing facility liquids and process or waste waters by using a combination of metal salts and a flocculant to coagulate and then flocculate contaminants from a contaminated liquid

Legal Events

Date Code Title Description
A201 Request for examination
G160 Decision to publish patent application
E701 Decision to grant or registration of patent right
NORF Unpaid initial registration fee