KR20020010006A - A Simultaneous Impregnated Adsorbent for Elimination of Hydrogen Sulfide Gas and a Preparation Method Using the Same - Google Patents

A Simultaneous Impregnated Adsorbent for Elimination of Hydrogen Sulfide Gas and a Preparation Method Using the Same Download PDF

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KR20020010006A
KR20020010006A KR1020000043734A KR20000043734A KR20020010006A KR 20020010006 A KR20020010006 A KR 20020010006A KR 1020000043734 A KR1020000043734 A KR 1020000043734A KR 20000043734 A KR20000043734 A KR 20000043734A KR 20020010006 A KR20020010006 A KR 20020010006A
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adsorbent
activated carbon
hydrogen sulfide
diethanolamine
sodium hydroxide
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KR1020000043734A
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KR100374691B1 (en
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박영성
이석기
황수덕
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박영성
황수덕
이석기
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/304Hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/46Materials comprising a mixture of inorganic and organic materials

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  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Gas Separation By Absorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PURPOSE: A method for producing an adsorbent that is simultaneously impregnated with sodium hydroxide and diethanolamine for the elimination of hydrogen sulfide gas is provided. CONSTITUTION: The production method of the adsorbent includes: (i) preparation of activated carbon(240mesh size) having a specific surface area 1050m¬2/g and average pore diameter 13-20Å; (ii) dipping the activated carbon in a mixed solution of 0.5-4mol sodium hydroxide and 0.01-0.25mol diethanolamine; (iii) agitating the obtained slurry for 3-5hrs; (iv) washing and filtering the slurry; and (v) drying the washed/filtered slurry in the temperature range 130 to 170deg.C for 18-36hrs.

Description

황화수소가스 제거용 동시첨착흡착제 및 이의 제조방법 {A Simultaneous Impregnated Adsorbent for Elimination of Hydrogen Sulfide Gas and a Preparation Method Using the Same}A Simultaneous Impregnated Adsorbent for Elimination of Hydrogen Sulfide Gas and a Preparation Method Using the Same}

본 발명은 황화수소가스 제거용 동시첨착흡착제 및 이의 제조방법에 관한 것으로, 보다 상세하게는 수산화나트륨과 디에탄올아민의 혼합용액에 동시 첨착된 활성탄이 수산기와 아민기로부터 유도되는 두 가지 염기성분의 상승작용에 의해 낮은 농도에서도 황화수소 흡착능을 보이는 황화수소가스 제거용 동시첨착흡착제와 이의 제조방법에 관한 것이다.The present invention relates to a co-adsorption adsorbent for removing hydrogen sulfide gas and a method for preparing the same, and more particularly to the rise of two base components in which activated carbon simultaneously co-attached to a mixed solution of sodium hydroxide and diethanolamine is derived from hydroxyl and amine groups. The present invention relates to a co-adhesive adsorbent for removing hydrogen sulfide gas having a hydrogen sulfide adsorption capacity even at a low concentration by the action and a method of manufacturing the same.

고도의 산업발달과 그에 따른 경제규모의 팽창은 방대한 양에 달하는 각종 유해물질의 발생을 가져왔으며 결국 이에 대한 처리능력의 한계와 함께 심각한 환경오염문제를 발생하였다. 이중에서 폐기물 매립장, 석유화학공업, 펄프공업, 도시가스 제조업, 암모니아공업, 하수처리장 등에서 발생하고 있는 황화수소(H2S) 가스는 계란 썩는 냄새가 나는 무색의 기체로서 인체의 위장이나 폐에 흡수되어 질식, 폐질환, 신경중추마비 등을 일으키는 위해성이 큰 기체로 분류되고 있어 이의 효율적인 처리방안의 모색이 당면한 과제로 부각되었다.The high level of industrial development and subsequent expansion of economic scale led to the generation of a large amount of various harmful substances, which in turn caused serious environmental pollution problems with the limitation of processing capacity. Among them, hydrogen sulfide (H 2 S) gas generated from waste landfill, petrochemical industry, pulp industry, city gas manufacturing industry, ammonia industry, sewage treatment plant, etc. is a colorless gas that smells like rotting eggs and is absorbed by the human stomach and lungs. As it is classified as a gas with a high risk of suffocation, lung disease, nerve central palsy, etc., finding an effective treatment method has emerged as a challenge.

이에 따른 종래의 기술로는 심냉법, 흡수법, 막분리법 및 흡착법 등의 처리방법이 제시되었고 심냉법은 분리된 가스의 액화에 필요한 동력비가 과다하게 지출되므로 경제적으로 취약하고 흡수법은 장기간의 운전에 따른 흡수액의 손실, 성능 저하 및 재료의 부식문제가 있으며 막분리법은 분리를 목적으로 하는 성분에 대한 선택성, 분리속도 및 내구성에 대한 연구가 정확하게 정립되지 않은 상태이다. 또한 흡착법은 흡착제의 표면과 흡착질(처리대상가스)이 물리적 또는 화학적으로 결합하는 현상을 통해 혼합된 흡착질로부터 일정 성분을 선택적으로 분리 또는 정제할 때에 이용되는 방법으로서 흡수법에 비하여 재료의 부식이 발생하지 않고 동력비의 부담이 없어 상용화공정에 많이 적용되어 왔지만 흡착제의 온도적용범위가 좁고, 흡착성능이 낮은 문제점이 있었다.Accordingly, conventional techniques have been proposed such as deep cooling method, absorption method, membrane separation method and adsorption method, etc. The deep cooling method is economically vulnerable because excessive power costs are required for the liquefaction of separated gas and the absorption method is long-term operation. There is a problem of loss of absorbent liquid, deterioration of performance and corrosion of materials. In the membrane separation method, studies on selectivity, separation speed, and durability of components for separation are not accurately established. In addition, the adsorption method is a method used to selectively separate or purify a certain component from the mixed adsorbate through the physical or chemical combination of the adsorbent surface and the adsorbent (gas to be treated). It has been applied to many commercialization process because there is no burden of power costs, but there was a problem that the temperature range of the adsorbent is narrow and the adsorption performance is low.

본 발명은 상기와 같은 종래 기술의 문제점을 해결하기 위해 안출된 것으로, 본 발명자들은 수산화나트륨 수용액과 디에탄올아민 수용액이 일정한 비율로 혼합된 수용액에 활성탄을 동시 첨착시켜 제조한 동시첨착 활성탄을 흡착제로 사용하여 흡착력이 개선된 황화수소가스 제거용 동시첨착흡착제를 제조하는데 성공하였다.The present invention has been made to solve the problems of the prior art as described above, the inventors of the present invention is a co-adhesive activated carbon prepared by simultaneously impregnating activated carbon in an aqueous solution in which sodium hydroxide aqueous solution and diethanolamine aqueous solution is mixed at a constant ratio as an adsorbent. It was successfully used to prepare a coadsorption adsorbent for removing hydrogen sulfide gas with improved adsorption capacity.

또한 본 발명의 동시첨착흡착제는 입자 크기가 8×30메쉬이고, 비표면적이 1050m2/g, 평균세공반경이 13∼20Å인 활성탄을 준비하는 단계; 상기 활성탄을 0.5∼4몰의 수산화나트륨과 0.01∼0.25몰의 디에탄올아민이 일정한 비율로 혼합된 용액에 활성탄을 동시첨착하는 단계; 혼합된 활성탄-첨착액 슬러리를 교반기에서 3∼5시간동안 교반하는 단계; 교반된 활성탄-첨착액 슬러리를 세척, 여과하는 단계; 및 세척, 여과된 활성탄을 130∼170℃에서 18∼36시간동안 건조하여 황화수소 가스 제거용 동시첨착흡착제를 제조할 수 있음을 확인하고 본 발명을 완성하게 되었다.In addition, the co-adsorption adsorbent of the present invention comprises the steps of preparing an activated carbon having a particle size of 8 × 30 mesh, a specific surface area of 1050m 2 / g, the average pore radius 13 ~ 20Å; Simultaneously attaching activated carbon to a solution in which 0.5 to 4 mol of sodium hydroxide and 0.01 to 0.25 mol of diethanolamine are mixed at a predetermined ratio; Stirring the mixed activated carbon-adhesive slurry in a stirrer for 3-5 hours; Washing and filtering the stirred activated carbon-adhesive slurry; And the washed and filtered activated carbon was dried for 18 to 36 hours at 130 ~ 170 ℃ confirmed that the co-adhesive adsorbent for removing hydrogen sulfide gas was completed the present invention.

결국, 본 발명의 목적은 황화수소가스 제거용 동시첨착흡착제를 제공하는 것이다.After all, it is an object of the present invention to provide a co-adhesive adsorbent for removing hydrogen sulfide gas.

본 발명의 다른 목적은 전기 황화수소가스 제거용 동시첨착흡착제의 제조방법을 제공하는 것이다.Another object of the present invention is to provide a method for preparing a co-adhesive adsorbent for removing hydrogen sulfide gas.

제1도는 본 발명의 흡착평형 실험장치의 다이아그램1 is a diagram of the adsorption equilibrium experiment apparatus of the present invention

제2도는 본 발명에 따른 동시첨착흡착제의 전자주사현미경 사진Figure 2 is an electron scanning micrograph of the co-adhesive adsorbent according to the present invention

♣ 도면의 주요 부분에 대한 부호의 설명 ♣♣ Explanation of symbols for the main parts of the drawing ♣

1: 온도계 2: 압력게이지1: thermometer 2: pressure gauge

3: 교반모터 4: 기록기3: stirring motor 4: recorder

5: 흡착제 고정판 6: 물중탕5: adsorbent fixing plate 6: water bath

7: 질소 가스 8: 황화수소 가스7: nitrogen gas 8: hydrogen sulfide gas

a: 실시예1에 의한 동시첨착흡착제의 전자주사현미경 사진a: Electron scanning micrograph of the co-adhesive adsorbent according to Example 1

b: 실시예8에 의한 동시첨착흡착제의 전자주사현미경 사진b: Electron scanning micrograph of the co-adhesive adsorbent according to Example 8

c: 실시예10에 의한 동시첨착흡착제의 전자주사현미경 사진c: Electron scanning micrograph of the co-adhesive adsorbent according to Example 10

d: 실시예16에 의한 동시첨착흡착제의 전자주사현미경 사진d: Electron scanning micrograph of the co-adhesive adsorbent according to Example 16

이하, 본 발명을 보다 구체적으로 설명하기로 한다.Hereinafter, the present invention will be described in more detail.

본 발명의 목적을 달성하기 위한 동시첨착흡착제는 황화수소 가스를 제거하기 위한 것으로 0.5∼4몰의 수산화나트륨과 0.01∼0.25몰의 디에탄올아민이 일정한 비율로 혼합된 용액에 활성탄을 동시 첨착시켜 제조되는 것을 특징으로 하는 황화수소 가스 제거용 동시첨착흡착제를 제공한다. 또한 입자 크기가 8×30메쉬이고, 비표면적이 1050m2/g, 평균세공반경이 13∼20Å인 활성탄을 준비하는 단계; 상기 활성탄을 0.5∼4몰의 수산화나트륨과 0.01∼0.25몰의 디에탄올아민이 일정한 비율로 혼합된 용액에 활성탄을 동시첨착하는 단계; 혼합된 활성탄-첨착액 슬러리를 교반기에서 3∼5시간동안 교반하는 단계; 교반된 활성탄-첨착액 슬러리를 세척, 여과하는 단계; 및 세척, 여과된 활성탄을 130∼170℃에서 18∼36시간동안 건조하는 단계로 구성되는 황화수소 가스 제거용 동시첨착흡착제의 제조하는 방법을 제공한다.The coadsorption adsorbent for achieving the object of the present invention is to remove the hydrogen sulfide gas is prepared by simultaneously attaching activated carbon to a solution mixed with 0.5 to 4 mol of sodium hydroxide and 0.01 to 0.25 mol of diethanolamine in a constant ratio Provided is a coadsorption adsorbent for removing hydrogen sulfide gas. Preparing an activated carbon having a particle size of 8 × 30 mesh, a specific surface area of 1050 m 2 / g, and an average pore radius of 13 to 20 GPa; Simultaneously attaching activated carbon to a solution in which 0.5 to 4 mol of sodium hydroxide and 0.01 to 0.25 mol of diethanolamine are mixed at a predetermined ratio; Stirring the mixed activated carbon-adhesive slurry in a stirrer for 3-5 hours; Washing and filtering the stirred activated carbon-adhesive slurry; And washing and drying the filtered activated carbon at 130 to 170 ° C. for 18 to 36 hours to provide a method for preparing a co-adhesive adsorbent for removing hydrogen sulfide gas.

이하 실시예에 의하여 본 발명을 보다 구체적으로 설명하고자 한다. 이들 실시예는 오로지 본 발명을 설명하기 위한 것으로, 본 발명의 요지에 따라 본 발명의범위가 이들 실시예에 국한되지 않는다는 것은 당업계에서 통상의 지식을 가진 자에게 자명할 것이다.Hereinafter, the present invention will be described in more detail with reference to the following examples. These examples are only for illustrating the present invention, and it will be apparent to those skilled in the art that the scope of the present invention is not limited to these examples according to the gist of the present invention.

다음의 표1에 본 발명에서 사용하는 첨착처리되지 않은 상태의 활성탄의 물성을 나타내었다.Table 1 below shows the physical properties of the activated carbon in the unimpregnated state used in the present invention.

[비교예] 입자 크기가 8×30메쉬이고, 비표면적이 1050m2/g, 평균세공반경이 13∼20Å인 활성탄을 증류수로 수 차례 세척한 후 150℃의 건조기에서 24시간동안 건조하여 첨착처리되지 않은 상태의 활성탄을 제조하여 데시케이터에 보관하였다.[Comparative Example] Activated carbon having a particle size of 8 × 30 mesh, a specific surface area of 1050m 2 / g, and an average pore radius of 13 to 20 세척 was washed several times with distilled water, and then dried in an oven at 150 ° C. for 24 hours to be impregnated. Unactivated carbon was prepared and stored in a desiccator.

대표적인 황화가스 제거용 동시첨착흡착제의 실시예:비교예에서 제조된 활성탄 10g을 수산화나트륨과 디에탄올아민이 일정한 비율로 혼합된 용액에 동시첨착하고 혼합된 활성탄-첨착액 슬러리를 교반기에서 4시간동안 교반하고 교반된 활성탄-첨착액 슬러리를 세척, 여과한 후 세척, 여과된 활성탄을 150℃에서 24시간동안 건조하여 동시첨착흡착제를 제조하였다. Example of Co-Adsorption Adsorption Agent for Removing Sulfuric Gas: 10 g of activated carbon prepared in Comparative Example was co-attached to a solution in which sodium hydroxide and diethanolamine were mixed at a constant ratio, and the mixed activated carbon-adhesive slurry was stirred for 4 hours in a stirrer. The stirred and activated carbon-adhesive slurry was washed, filtered and washed, and the filtered activated carbon was dried at 150 ° C. for 24 hours to prepare a coadsorption adsorbent.

이상의 비교예 및 실시예에 있어서 황화수소 가스 제거용 동시첨착흡착제의 평가는 첨착흡착제의 첨착력, 비표면적 측정, SEM 측정, 열천칭 분석, pH분석, 중화적정분석 등의 평가를 실시하였다.In the above comparative examples and examples, the evaluation of the co-adhesive adsorbent for removing hydrogen sulfide gas was carried out to evaluate the adhesion force, specific surface area measurement, SEM measurement, thermobalance analysis, pH analysis, neutralization titration analysis, etc. of the impregnated adsorbent.

(1) 흡착평형 실험 장치(1) adsorption equilibrium experiment apparatus

본 발명의 흡착평형 실험 장치의 다이아그램을 도1에 나타내었다. 흡착제와 흡착질가스를 충전할 수 있도록 내부 총 부피가 1,680㎖에 달하는 2개의 원통형 챔버(내경 7cm, 길이 25cm)로 구성되어 있으며, 이들은 볼밸브가 달린 2개의 관(외경 2.2cm)으로 연결되어 있다. 그리고 연결관에는 흡착이 진행되는 동안 밀폐공간의 압력변화를 측정할 수 있도록 압력변환기(pressure transducer)가 설치되어 있으며, 흡착과정 중 내부의 압력변화에 따른 압력변환기의 출력을 3개의 핀 기록기 에 기록되도록 하였다. 또한 원통형 챔버내의 흡착온도변화를 감지하기 위하여 흡착제 일정량을 충전한 흡착제 받침대의 공간 상단부에 T형 열전대가 설치되어 있다. 흡착질가스가 주입되는 밀폐 공간 내부에는 가스의 혼합을 돕기 위하여 영구자석이 부착되어 있는 임펠러를 설치, 회전시킬 수 있도록 하였다. 또한 전체 실험설비는 등온에서의 흡착평형실험을 위하여 온도조절이 가능한 수조내에 배치하였다.A diagram of the adsorption equilibrium experiment apparatus of the present invention is shown in FIG. It consists of two cylindrical chambers (7cm inner diameter and 25cm length) with a total internal volume of 1680ml to fill the adsorbent and adsorbate gas.They are connected by two tubes (2.2cm outer diameter) with a ball valve. . In addition, a pressure transducer is installed in the connecting pipe to measure the pressure change in the enclosed space during the adsorption process, and the output of the pressure transducer according to the internal pressure change during the adsorption process is recorded on three pin recorders. It was made. In addition, a T-type thermocouple is installed at the upper end of the space of the adsorbent pedestal filled with a predetermined amount of the adsorbent in order to detect the change in the adsorption temperature in the cylindrical chamber. In the sealed space where the adsorbate gas is injected, an impeller with permanent magnets can be installed and rotated to assist gas mixing. In addition, the entire test facility was placed in a temperature control tank for adsorption equilibrium experiments at isothermal temperature.

(2) 동시첨착흡착제의 첨착량 측정(2) Measurement of adhesion amount of co-adhesive adsorbent

황화수소 가스 제거용 동시첨착흡착제의 첨착력을 평가하기 위해 본 발명의 실시예 2∼6, 9∼13, 15∼19 및 21∼25의 흡착제의 첨착량(중량%) 변화를 측정하였다. 그 결과 일정한 디에탄올아민농도에 대해 수산화나트륨의 농도가 높아질수록 첨착량이 증가됨을 표2로 알 수 있었다.In order to evaluate the adhesion force of the co-adhesive adsorbent for removing hydrogen sulfide gas, changes in the adhesion amount (% by weight) of the adsorbents of Examples 2 to 6, 9 to 13, 15 to 19, and 21 to 25 of the present invention were measured. As a result, it can be seen from Table 2 that the amount of deposition increases as the concentration of sodium hydroxide increases for a certain diethanolamine concentration.

(3) 동시첨착흡착제의 비표면적측정(3) Measurement of specific surface area of co-adhesive adsorbent

본 발명에 의한 동시첨착흡착제의 비표면적의 측정은 BET(Brunauer, Emmet, Teller) 질소 흡ㆍ탈착력을 이용한 다중점법으로 측정하였으며, 분석기는 미국 퀀타크로머 사의 Autosorb-1을 사용하였다. 실시예1, 8, 10 및 16의 동시첨착흡착제의 비표면적은 각각 973.4m2/g, 958.5m2/g, 923m2/g, 846m2/g으로 측정되었으며 첨착시약인 수산화나트륨과 디에탄올아민의 혼합용액의 농도가 높아질수록 동시첨착흡착제의 미세기공(micro pore)을 막기 때문에 동시첨착흡착제의 비표면적이 혼합용액의 농도에 반비례하는 것으로 나타났으며, 그 결과를 표3에 나타내었다.The specific surface area of the coadsorption adsorbent according to the present invention was measured by the multipoint method using BET (Brunauer, Emmet, Teller) nitrogen adsorption and desorption force, and the analyzer used Autosorb-1 manufactured by Quanta Chromer, USA. The specific surface areas of the coadsorption adsorbents of Examples 1, 8, 10 and 16 were respectively measured as 973.4m 2 / g, 958.5m 2 / g, 923m 2 / g and 846m 2 / g, respectively. As the concentration of the mixed solution of the amine increases, the micropore of the coadsorption adsorbent is prevented, so that the specific surface area of the coadsorption adsorbent is inversely proportional to the concentration of the mixed solution, and the results are shown in Table 3.

(4) SEM측정(4) SEM measurement

본 발명에 의한 실시예1, 8, 10 및 16의 동시첨착흡착제의 기공내부를 전자주사현미경으로 1,000배 확대하여 측정하였으며, 그 결과를 도2에 나타내었다. 수산화나트륨과 디에탄올아민의 혼합수용액의 농도가 증가할수록 동시첨착흡착제 내부의 미세기공이 많이 막히는 현상이 일어남을 확인할 수 있었다.The pores of the coadsorption adsorbents of Examples 1, 8, 10 and 16 according to the present invention were measured by magnification 1,000 times with an electron scanning microscope, and the results are shown in FIG. As the concentration of the mixed solution of sodium hydroxide and diethanolamine increased, it was confirmed that a phenomenon in which the micropores inside the coadsorption adsorbent were clogged.

(5) 동시첨착흡착제의 열천칭분석(5) Thermal balance analysis of co-adhesive adsorbent

본 발명에 의한 실시예 3, 5, 7, 10, 12, 14, 16, 18, 20, 22, 24 및 26의 첨착된 흡착제의 열적변화특성을 조사하기 위해 열천칭(Du-pont, 2050)을 사용하여 승온·탈착실험을 수행하였다. 흡착제시료를 Sample pan에 놓은 후, 질소가스 분위기 하에서 10oC/min으로 가열하고, 100℃에서 1시간을 유지한 후 다시 1000℃까지 10oC/min 속도로 승온시키면서 탄소표면에 존재하는 산소그룹이 분해되어 일산화탄소와 이산화탄소로 분출될 때 수반되는 질량감소특성을 조사하였다. 그 결과를 표4에 나타내었고 수산화나트륨과 디에탄올아민의 혼합용액의 농도가 증가할수록 승온·탈착에 의해 발생하는 질량감소는 산소와 탄소가 결합해서 여러 가지 조성물의 화합물인 CXOY를 생성하게 되고 이 화합물이 가열에 의해 CO와 CO2의 혼합물로 급격하게 분해되기 때문에 동시첨착흡착제의 질량감소율이 증가하였다.Thermo balance (Du-pont, 2050) to investigate the thermal change characteristics of the impregnated adsorbents of Examples 3, 5, 7, 10, 12, 14, 16, 18, 20, 22, 24, and 26 according to the present invention Using the temperature increase / desorption experiment was performed. After placing the adsorbent sample on the sample pan, it was heated to 10 o C / min under nitrogen gas atmosphere, maintained at 100 ° C for 1 hour, and then heated up to 1000 ° C at 10 o C / min while oxygen was present on the carbon surface. The mass reduction properties associated with the decomposition of the group into the carbon monoxide and carbon dioxide were investigated. The results are shown in Table 4, and as the concentration of the mixed solution of sodium hydroxide and diethanolamine increases, the mass decrease caused by the temperature increase and desorption combines oxygen and carbon to form C X O Y , a compound of various compositions. Since the compound is rapidly decomposed into a mixture of CO and CO 2 by heating, the mass loss rate of the coadsorption adsorbent is increased.

(6) 동시첨착흡착제의 pH분석(6) pH analysis of coadsorption adsorbent

본 발명에 의한 실시예 3, 5, 7, 10, 12, 14, 16, 18, 20, 22, 24 및 26로 제조된동시첨착흡착제 0.5g을 증류수 20ml가 담긴 파이렉스 용기에 첨가시킨 후 12시간 동안 기계적 진탕을 하고 이 용액을 4.5㎛의 나일론 멤브레인 필터로 여과하여 pH측정기(HM-30V)로 상등액의 pH를 측정하였다. 그 결과를 표5에 나타내었으며 수산화나트륨과 디에탄올아민의 혼합용액으로 제조된 동시첨착흡착제는 0.0125몰 디에탄올아민을 1, 2, 3, 4몰의 수산화나트륨과 각각 혼합하여 제조하였을 때 pH가10.75에서 10.96로 증가하고, 0.025몰의 디에탄올아민을 1, 2, 3, 4몰 수산화나트륨과 각각 혼합하여 제조하였을 때 pH가 11.05에서 11.29로 증가하는 것으로 나타났으며, 또한 0.125몰 디에탄올아민을 1, 2, 3, 4몰의 수산화나트륨과 각각 혼합하여 제조하였을 때 pH가 11.23에서 11.36로 증가하는 것으로 나타났다. 이러한 이유는 혼합용액의 농도가 증가함에 따라서 알칼리성분에 의한 흡착제 표면 중화기능으로 흡착제 표면의 산성 관능기가 감소하게 되고, 이로 인해 pH값이 증가하게 되는 것으로 볼 수 있다.12 hours after adding 0.5 g of a co-adhesive adsorbent prepared in Examples 3, 5, 7, 10, 12, 14, 16, 18, 20, 22, 24 and 26 according to the present invention to a Pyrex container containing 20 ml of distilled water. While mechanical shaking was performed and the solution was filtered through a 4.5 탆 nylon membrane filter to measure the pH of the supernatant with a pH meter (HM-30V). The results are shown in Table 5, and the coadsorption adsorbent prepared with a mixed solution of sodium hydroxide and diethanolamine had a pH of 0.0125 mol diethanolamine mixed with 1, 2, 3, and 4 mol of sodium hydroxide, respectively. It was found that the pH increased from 11.05 to 11.29 when prepared by mixing from 10.75 to 10.96 and mixing 0.025 moles of diethanolamine with 1, 2, 3, and 4 moles of sodium hydroxide, respectively, and also 0.125 moles of diethanolamine. Was prepared by mixing with 1, 2, 3 and 4 moles of sodium hydroxide, respectively, and the pH was increased from 11.23 to 11.36. The reason for this is that as the concentration of the mixed solution increases, the acidic functional group on the surface of the adsorbent decreases due to the neutralizing function of the adsorbent surface by the alkaline component, and thus the pH value increases.

(7) 중화적정곡선(7) Chinese titration curve

동시첨착흡착제의 표면에 존재하는 산성 표면관능기의 양을 측정은 Boehm 방법에 의거하여 측정하였고 동시첨착흡착제 1g씩을 강도가 다른 세 종류의 탄산수소나트륨, 탄산나트륨 및 수산화나트륨 0.1노르말농도의 염기용액 100ml와 각각 혼합하여 48시간동안 기계적 진탕 후, 흡착제를 침강시켜 맑은 용액을 얻었다. 이때 얻어진상등액 10ml를 pH 측정장치가 부착된 적정장치(Metrohm titroprocessor Model 682)을 사용하여 실시예1, 8, 10 및 16의 탄소표면에 존재하는 산성 표면관능기의 양을 측정하였다. 그 결과를 표6에 나타내었으며 0.0125몰의 디에탄올아민과 혼합하는 수산화나트륨의 농도를 0.5에서 3몰로 증가시켰을 때, 탄산수소나트륨에 의해 적정된 강산성의 카르복실기는0∼0.096meq/g-AC, 탄산나트륨에 의해 적정된카르복실기와 약산성의 카르복실기인 락톤기는 0∼0.269meq/g-AC, 수산화나트륨에 의해 적정된 카르복실기, 락톤기 및 페놀기는 0.219∼0.557meq/g-AC 범위에서 혼합용액의 농도에 반비례하여 산도가 변하는 것을 보였다. 이것은 농도가 증가함에 따라서 산성 관능기에 속하는 카르복실기, 락톤기, 페놀기의 양이 감소하기 때문이다.The amount of acidic surface functional groups present on the surface of the coadsorption adsorbent was measured according to the Boehm method. Each 1 g of the coadsorption adsorbent was added to 100 ml of a basic solution of 0.1 normal concentration of sodium hydrogencarbonate, sodium carbonate and sodium hydroxide having different strengths Each mixture was mechanically shaken for 48 hours, and then the adsorbent was allowed to settle to obtain a clear solution. The amount of the acidic surface functional groups present on the carbon surface of Examples 1, 8, 10 and 16 was measured using a titrator (Metrohm titroprocessor Model 682) equipped with a pH measuring device 10ml of the supernatant. The results are shown in Table 6, and when the concentration of sodium hydroxide mixed with 0.0125 moles of diethanolamine was increased from 0.5 to 3 moles, the strongly acidic carboxyl groups titrated by sodium bicarbonate were 0 to 0.096 meq / g-AC, The lactone group, which is a carboxyl group titrated with sodium carbonate and a weakly acidic carboxyl group, is 0 to 0.269 meq / g-AC. Inversely, the pH was shown to change. This is because the amount of carboxyl, lactone and phenol groups belonging to the acidic functional groups decreases as the concentration increases.

(8) 동시첨착흡착제의 평형흡착량에 대한 온도의 영향(8) Effect of temperature on the equilibrium adsorption amount of the coadsorption adsorbent

표7은 온도변화에 따른 비첨착흡착제의 황화수소 가스의 평형흡착량 변화를 보여주고 있다. 황화수소 가스의 주입농도가 4.96mg/ℓ일 때 흡착온도를 25℃에서 45℃로 증가시킬 경우, 황화수소흡착량은 13.24mg/gAC에서 2.01mg/gAC로 약 85% 감소한 것으로 나타났다. 이처럼 황화수소의 평형 흡착량이 흡착온도에 반비례하는 것은 비첨착흡착제의 경우 온도가 증가할수록 흡착질가스의 휘발성이 증대되면서 물리적인 결합을 방해하기 때문이다.Table 7 shows the change of equilibrium adsorption amount of hydrogen sulfide gas of non-adsorption adsorbent with temperature change. When the adsorption temperature of hydrogen sulfide gas was increased from 4.96mg / L to 25 ° C to 45 ° C, the hydrogen sulfide adsorption amount decreased by 85% from 13.24mg / gAC to 2.01mg / gAC. The equilibrium adsorption amount of hydrogen sulfide is inversely proportional to the adsorption temperature because the non-adsorption adsorbent increases the volatility of the adsorbate gas as the temperature increases, thereby preventing physical bonding.

표8은 실시예1, 3 및 8의 동시첨착흡착제의 흡착온도에 따른 평형흡착량의 변화를 나타낸 것으로 흡착온도를 25℃에서 45℃로 증가시키면 평형흡착량은 증가하는 것으로 나타나 비첨착흡착제와 비교해 상반된 결과를 보여주고 있다. 이는 첨착합착제의 경우 주로 화학흡착에 의해 온도가 증가할수록 평형흡착량이 증가하기 때문이며, 따라서 고온조건일수록 동시첨착흡착제의 황화수소 가스 흡착처리에 효율적으로 적용될 수 있음을 알 수 있다.Table 8 shows the change in the equilibrium adsorption amount according to the adsorption temperature of the coadsorption adsorbents of Examples 1, 3, and 8, and the equilibrium adsorption amount increases when the adsorption temperature is increased from 25 ° C to 45 ° C. Comparing results are shown. This is because in the case of the impregnated binder, the equilibrium adsorption amount increases as the temperature increases mainly by chemical adsorption, and thus, it can be seen that the high temperature condition can be effectively applied to the hydrogen sulfide gas adsorption treatment of the coadsorbent.

(9) 동시첨착흡착제의 농도에 따른 평형흡착량의 변화(9) Change in equilibrium adsorption according to the concentration of coadsorption adsorbent

표9는 본 발명의 실시예 3, 4, 6, 10, 11, 13, 16, 17, 19, 22, 23 및 25의 수산화나트륨 및 디에탄올아민 혼합용액의 농도변화에 따른 황화수소 가스의 흡착특성을 나타낸 것이다. 전체적으로 흡착량은 13.4mg/g-AC에서 30.7mg/g-AC에 해당하는 것으로 나타났으며, 실시예10으로 제조된 동시첨착흡착제가 최대흡착량을 나타냈다. 동시첨착흡착제의 황화수소 최대흡착량은 비교예에 비해 2배이상 증가된 값을 갖는 것으로 나타났다.Table 9 shows the adsorption characteristics of hydrogen sulfide gas according to the concentration change of sodium hydroxide and diethanolamine mixed solution of Examples 3, 4, 6, 10, 11, 13, 16, 17, 19, 22, 23 and 25 of the present invention. It is shown. Overall, the adsorption amount was found to correspond to 30.7 mg / g-AC at 13.4 mg / g-AC, and the coadsorption adsorbent prepared in Example 10 showed the maximum adsorption amount. The maximum amount of hydrogen sulfide adsorption of the coadsorption adsorbent was found to have a value increased by more than 2 times compared with the comparative example.

표10는 실시예3, 4, 6, 10, 11, 13, 16, 17, 19, 22, 23 및 25로 제조된 동시첨착흡착제의 흡착량변화를 나타낸 것으로 황화수소 흡착량은 일정한 수산화나트륨용액의 농도하에서 디에탄올아민의 농도가 증가될수록 감소되었으며 실시예10으로 제조된 동시첨착흡착제가 가장 높은 흡착량을 보였다. 이처럼 특정 염기시약농도조건에서 최대흡착량을 보이는 것은 수산화나트륨이나 디에틸아민의 농도가 증가될수록 흡착제 기공표면에 염기시약의 첨착량이 늘어나면서 화학흡착은 향상되지만 일부 기공이 폐쇄되면서 물리흡착이 상대적으로 감소되기 때문이다.Table 10 shows the change in the adsorption amount of the coadsorption adsorbents prepared in Examples 3, 4, 6, 10, 11, 13, 16, 17, 19, 22, 23, and 25. Under the concentration, the concentration of diethanolamine decreased with increasing concentration, and the coadsorption adsorbent prepared in Example 10 showed the highest adsorption amount. As the concentration of sodium hydroxide or diethylamine increases, the adsorption amount of base reagent increases on the surface of the adsorbent pores as the concentration of sodium hydroxide or diethylamine increases. Because it is reduced.

상기 성능평가에 있어서, 동시첨착흡착제의 황화수소 가스 흡착량 변화실험에서 알 수 있듯이 본 발명의 제품은 수산화나트륨과 디에탄올아민의 혼합용액의 낮은 농도에서도 황화수소 가스의 흡착력이 매우 뛰어난 것으로 판명되었다.In the above performance evaluation, as can be seen in the hydrogen sulfide gas adsorption amount change experiment of the coadsorption adsorbent, the product of the present invention was found to have excellent adsorption power of hydrogen sulfide gas even at a low concentration of the mixed solution of sodium hydroxide and diethanolamine.

이상에서 살펴본 바와 같이 본 발명에 의하면, 수산화나트륨과 디에탄올아민의 혼합용액의 낮은 농도에서 황화수소 가스의 높은 흡착능을 얻을 수 있는 점을 고려할 때 황화수소를 비롯한 악취 및 휘발성유기물질 등의 유해가스 제거를 위한 첨착흡착제로 효과가 있다.As described above, according to the present invention, considering the fact that a high adsorption capacity of hydrogen sulfide gas can be obtained at a low concentration of a mixed solution of sodium hydroxide and diethanolamine, it is possible to remove harmful gases such as hydrogen sulfide, odors and volatile organic substances. It is effective as an adhesive adsorbent for.

Claims (4)

수산화나트륨과 디에탄올아민이 일정한 비율로 혼합된 용액에 활성탄을 동시첨착시켜 제조되는 것을 특징으로 하는 황화수소 가스 제거용 동시첨착흡착제.A co-adsorption adsorbent for removing hydrogen sulfide gas, characterized in that it is produced by co-attaching activated carbon to a solution in which sodium hydroxide and diethanolamine are mixed at a constant ratio. 제 1항에 있어서,The method of claim 1, 상기 수산화나트륨은 0.5∼4몰, 디에탄올아민은 0.01∼0.25몰인 것을 사용하는 것을 특징으로 하는 황화수소 가스 제거용 동시첨착흡착제.The sodium hydroxide gas co-adhesive adsorbent for removing hydrogen sulfide gas, characterized in that 0.5 to 4 mol, diethanolamine is 0.01 to 0.25 mol. 제1항에 있어서,The method of claim 1, 상기 활성탄의 입자 크기가 8×30메쉬이고, 비표면적이 1050m2/g, 평균세공반경이 13∼20Å인 것을 사용하는 것을 특징으로 하는 황화수소 가스 제거용 동시첨착흡착제.The particle size of the activated carbon is 8 × 30 mesh, the specific surface area of 1050m 2 / g, the average pore radius is 13 to 20 kPa, hydrogen sulfide gas removal co-adhesive adsorbent. 입자 크기가 8×30메쉬이고, 비표면적이 1050m2/g, 평균세공반경이 13∼20Å인 활성탄을 준비하는 단계; 상기 활성탄을 0.5∼4몰의 수산화나트륨과 0.01∼0.25몰의 디에탄올아민이 일정한 비율로 혼합된 용액에 활성탄을 동시첨착하는 단계; 혼합된 활성탄-첨착액 슬러리를 교반기에서 3∼5시간동안 교반하는 단계; 교반된 활성탄-첨착액 슬러리를 세척, 여과하는 단계; 및 세척, 여과된 활성탄을 130∼170℃에서 18∼36시간동안 건조하는 단계로 구성되는 황화수소 가스 제거용 동시첨착흡착제의 제조 방법.Preparing activated carbon having a particle size of 8 x 30 mesh, a specific surface area of 1050 m 2 / g, and an average pore radius of 13 to 20 microns; Simultaneously attaching activated carbon to a solution in which 0.5 to 4 mol of sodium hydroxide and 0.01 to 0.25 mol of diethanolamine are mixed at a predetermined ratio; Stirring the mixed activated carbon-adhesive slurry in a stirrer for 3-5 hours; Washing and filtering the stirred activated carbon-adhesive slurry; And washing and drying the filtered activated carbon at 130 to 170 ° C. for 18 to 36 hours.
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