KR102016146B1 - The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds - Google Patents

The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds Download PDF

Info

Publication number
KR102016146B1
KR102016146B1 KR1020190083258A KR20190083258A KR102016146B1 KR 102016146 B1 KR102016146 B1 KR 102016146B1 KR 1020190083258 A KR1020190083258 A KR 1020190083258A KR 20190083258 A KR20190083258 A KR 20190083258A KR 102016146 B1 KR102016146 B1 KR 102016146B1
Authority
KR
South Korea
Prior art keywords
mixed
weight
parts
porous ceramic
ceramic carrier
Prior art date
Application number
KR1020190083258A
Other languages
Korean (ko)
Inventor
이정훈
Original Assignee
한국환경평가기술 주식회사
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 한국환경평가기술 주식회사 filed Critical 한국환경평가기술 주식회사
Priority to KR1020190083258A priority Critical patent/KR102016146B1/en
Application granted granted Critical
Publication of KR102016146B1 publication Critical patent/KR102016146B1/en

Links

Images

Classifications

    • 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/84Biological processes
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N11/00Carrier-bound or immobilised enzymes; Carrier-bound or immobilised microbial cells; Preparation thereof
    • C12N11/14Enzymes or microbial cells immobilised on or in an inorganic carrier
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/95Specific microorganisms
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/59Biological synthesis; Biological purification

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Biomedical Technology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Zoology (AREA)
  • Wood Science & Technology (AREA)
  • Genetics & Genomics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Biotechnology (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Microbiology (AREA)
  • General Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Engineering & Computer Science (AREA)
  • General Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)

Abstract

The present invention relates to a method for preparing a bio-filter composition for relieving air pollution by removing odor and organic volatile compounds, which comprises: a grinding step of grinding a porous carrier; a binder solution mixing step of mixing the grinded porous carrier and a binder solution; a heat treatment step of thermally treating the porous carrier mixed with the binder solution; a microorganism input step of inputting microorganisms into the thermally treated porous carrier; and a growth promotor adsorption step of absorbing a growth promotor to the porous carrier input with the microorganisms. The bio-filter composition of the present invention has an effect of relieving air pollution by easily converting T-VOCs (benzene, toluene, ethylbenzene, and xylene), which are odor and harmful chemical substances which can be discharged by being included in an elastic floor material installed in a bicycle road of a river side, a child playground, a school playground, etc. into carbon dioxide (CO_2), water (H_2O), minerals, etc. by using microorganisms.

Description

악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법{The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds}The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds}

본 발명은 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법으로서, 다공성 담체를 분쇄하는 분쇄단계와, 상기 분쇄된 다공성 담체와 바인더용액을 혼합하는 바인더용액 혼합단계와, 상기 바인더용액이 혼합된 다공성 담체를 열처리하는 열처리단계와, 상기 열처리된 다공성 담체에 미생물을 투입하는 미생물 투입단계 및 상기 미생물이 투입된 다공성 담체에 생장촉진제를 흡착시키는 생장촉진제 흡착단계를 포함하여 미생물을 이용해서 유해물질을 이산화탄소(CO2), 물(H2O), 무기질 등으로 변환시키기 위한 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법에 관한 것이다. The present invention provides a method for preparing a composition for a biofilter for improving air pollution by removing odors and organic volatile compounds, comprising: a grinding step of pulverizing a porous carrier, a binder solution mixing step of mixing the pulverized porous carrier and a binder solution, and A microorganism is used, including a heat treatment step of heat-treating a porous carrier mixed with a binder solution, a microorganism input step of injecting microorganisms into the heat-treated porous carrier, and a growth promoter adsorption step of adsorbing a growth promoter on the porous carrier into which the microorganisms are introduced. It relates to the harmful substances carbon dioxide (CO 2), water and composition to malodor production method for a biofilter for the improvement of air quality by removing volatile organic compounds such as, for converting (H 2 O), minerals.

일반적으로, 하천변의 자전거 도로, 어린이 놀이터, 학교 운동장 등에 포설되고 있는 탄성바닥재, 일상 생활공간, 시장 및 상가, 자동차, 화학플랜트, 산업현장, 하수처리장, 쓰레기매립장, 소각장, 대형발전소 및 보일러 등 다양한 곳에서 인간에 유해하거나 불쾌감을 주는 유해가스 및 악취가 발생한다. 대표적인 유해가스 및 악취물질로는 휘발성 유기물질(volatile organic compound: VOC) , 암모니아(ammonia), 트리메틸아민(trimethylamine), 아세트알데히드(acetaldehyde), 메탄티올(Methanethiol), 황화메틸(methyl sulfide), 이황화메틸(methyl disulfide), 황화수소(hydrogen sulfide), 산화질소(nitrogen oxide), 이산화질소(nitrogen dioxide), 스티렌(styrene) 등이 있다.In general, a variety of elastic flooring materials such as bicycle roads, children's playgrounds, school playgrounds, riversides, daily living spaces, markets and stores, automobiles, chemical plants, industrial sites, sewage treatment plants, landfills, incinerators, large power plants and boilers It generates harmful gases and odors that are harmful or unpleasant to humans. Representative harmful gases and odorous substances include volatile organic compounds (VOC), ammonia, trimethylamine, acetaldehyde, methanethiol, methyl sulfide and disulfide. Methyl disulfide, hydrogen sulfide, nitrogen oxide, nitrogen dioxide, and styrene.

쾌적하고 인체에 무해한 생활환경에 대해 대중의 요구가 증가함에 따라 유해물질 또는 악취물질 방출에 대한 법적인 규제가 강화되고 있고, 이에 수반되어 악취물질과 유해물질을 효과적으로 제어 또는 제거할 수 있는 탈취제 및 탈취장비의 개발이 절실히 요구되어 왔으며, 많은 연구가 진행되어 왔다.As public demand increases for a pleasant and harmless living environment, legal regulations on the release of harmful or odorous substances are being strengthened, and deodorants and deodorants that can effectively control or remove odorous substances and toxic substances are accompanied. The development of equipment has been urgently required, and a lot of research has been conducted.

최근에는 환경문제에 대한 사회적 관심이 고조되면서 화학물질 대신 미생물을 이용하여 유해물질을 처리하려는 노력이 확대되고 있다. 이러한 생물학적 처리방법으로는 구체적으로 바이오필터(biofilter), 바이오트리클링 필터(biotrickling filter) 또는 바이오스크러버(bioscrubber)를 예로 들 수 있다.In recent years, as social concerns about environmental problems have increased, efforts to deal with harmful substances using microorganisms instead of chemicals have been expanded. Specific examples of such biological treatment methods include biofilters, biotrickling filters, or bioscrubbers.

상기 바이오필터는 주로 오염물질의 용해도가 낮은 경우에 적합하며, 공정이 매우 단순하고 설치비, 운전비가 적게 든다는 장점이 있다. 그러나, 미생물의 적절한 성장을 위하여 pH, 온도, 수분, 영양분의 추가공급 등 공정제어가 어렵고, 장기간 운전 시에는 담체의 수축 또는 영양성분의 고갈로 인하여 담체의 교환이 필요하다는 단점이 있다. The biofilter is mainly suitable for the case of low solubility of contaminants, and has the advantage of a very simple process and low installation and operation costs. However, it is difficult to control the process such as additional supply of pH, temperature, moisture, and nutrients for proper growth of microorganisms, and during the long-term operation, carriers need to be exchanged due to shrinkage of carriers or depletion of nutrients.

상기 바이오트리클링 필터는 생물막 형성에 필요한 질소, 인, 무기염류 등을 포함하는 용액을 공급하면서 운전되며, 담체의 성능에 따라 일시적인 농도 상승에 의한 미생물 충격에 대하여 효과적으로 대응할 수 있고, pH, 온도, 수분 등의 조절이 용이하다는 장점이 있다. The biotrickle filter is operated while supplying a solution containing nitrogen, phosphorus, inorganic salts, etc. necessary for biofilm formation, and can effectively respond to microbial shock due to a temporary increase in concentration according to the performance of the carrier, pH, temperature, There is an advantage that it is easy to control moisture.

상기 바이오스크러버는 오염물질을 물리적으로 분리한 다음 생물학적인 처리를 위한 활성슬러지를 독립적으로 운전할 수 있어 공정을 최적화하기 용이하다는 장점이 있다. 하지만, 대부분의 휘발성 유기화합물과 황화합물은 용해도가 낮아 접촉 면적이 커야 하며, 스크러빙 부분의 크기가 상대적으로 크기 때문에 소요부지 면적이 크다는 단점이 있다.The bioscrubber has the advantage that it is easy to optimize the process because it can physically separate the contaminants and then independently operate the activated sludge for biological treatment. However, most volatile organic compounds and sulfur compounds have a low solubility, so that the contact area is large, and the scrubbing portion has a relatively large size, and thus requires a large area for the site.

이상과 같은 생물학적인 방법을 이용한 반응기들의 성능을 최대화하기 위해서는 반응기 설계뿐만 아니라 반응기내 충진물의 선택이 중요하다. 즉, 상기 충진물은 미생물이 부착 성장할 수 있도록 미생물을 고정화시키는 담체이기 때문에, 이러한 충진물의 선택에 따라 반응기의 크기, 반응기 내의 수분함량, 오염원의 흡수 흡착성능이 결정되며, 따라서 이러한 충진물은 반응기의 성능을 결정하는 중요한 변수이다. 따라서, 미생물을 이용해서 유해물질을 이산화탄소(CO2), 물(H2O), 무기질 등으로 변환시키기 위해 흡착성능이 우수하고, 미생물의 성장 및 증식을 높일 수 있는 조성물의 개발이 필요한 실정이다. In order to maximize the performance of the reactors using the biological method described above, not only the reactor design but also the selection of the fillers in the reactor are important. That is, since the filler is a carrier for immobilizing the microorganisms to allow the microorganisms to adhere and grow, the size of the reactor, the water content in the reactor, and the absorption and adsorption performance of the pollutant are determined according to the selection of such fillers. Is an important variable in determining this. Therefore, in order to convert harmful substances into carbon dioxide (CO 2 ), water (H 2 O), minerals and the like using microorganisms, there is a need for the development of a composition having excellent adsorption performance and enhancing microbial growth and proliferation. .

KR 10-1621098 B1 (2016. 05. 09.)KR 10-1621098 B1 (2016. 05. 09.) KR 10-0664882 B1 (2006. 12. 28.)KR 10-0664882 B1 (Dec. 28, 2006)

본 발명은 상기 종래기술이 갖는 문제점을 해결하기 위해서 안출된 것으로서, 본 발명에서 해결하고자 하는 과제는 하천변의 자전거 도로, 어린이 놀이터, 학교 운동장 등에 포설되고 있는 탄성바닥재에 포함되어 유출될 수 있는 유해화학물질인 T-VOCs(벤젠, 톨루엔, 에틸벤젠, 크실렌)을 제거하기 위한 물리적인 생물학적 처리방법으로서 미생물을 이용해서 유해물질을 이산화탄소(CO2), 물(H2O), 무기질 등으로 변환시켜 대기오염을 개선시키기 위한 바이오필터 조성물을 제공하는데 있다.The present invention has been made in order to solve the problems of the prior art, the problem to be solved in the present invention is a harmful chemical that can be contained in the elastic floor material installed on the riverside road, children's playground, school playground, etc. As a physical biological treatment method to remove T-VOCs (benzene, toluene, ethylbenzene, xylene), which are substances, microorganisms are used to convert harmful substances into carbon dioxide (CO 2 ), water (H 2 O), and minerals. The present invention provides a biofilter composition for improving air pollution.

상기와 같은 목적을 달성하기 위한 본 발명에 따른 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법은 탄소, 탄화규소, 고분자 바인더를 혼합하는 혼합단계와, 상기 혼합된 혼합물을 열처리하여 상기 혼합물에 함유된 탄소를 산화시키는 다공성 세라믹 담체 제조단계와, 상기 제조된 다공성 세라믹 담체에 혼합미생물을 투입하는 혼합미생물 투입단계 및 상기 혼합미생물이 투입된 다공성 세라믹 담체에 산소발생제를 추가하는 산소발생제 추가단계를 포함하는 것을 특징으로 한다. The method for preparing a composition for a biofilter for improving air pollution by removing odors and organic volatile compounds according to the present invention for achieving the above object comprises a mixing step of mixing carbon, silicon carbide, and a polymeric binder, and the mixed mixture A porous ceramic carrier manufacturing step of oxidizing carbon contained in the mixture by heat treatment, a mixed microorganism injecting step of injecting a mixed microorganism into the prepared porous ceramic carrier and adding an oxygen generating agent to the porous ceramic carrier into which the mixed microorganism is added Characterized in that it comprises an additional oxygen generator.

또, 상기 혼합단계는, 입자크기가 10~30㎛인 탄소분말 100중량부에 대하여, 입자크기가 35~50㎛인 탄화규소분말 30~50중량부, 고분자 바인더 0.5~2중량부를 혼합하는 것을 특징으로 한다. In addition, the mixing step is to mix 30 to 50 parts by weight of silicon carbide powder having a particle size of 35 to 50 ㎛, 0.5 to 2 parts by weight of a polymeric binder with respect to 100 parts by weight of carbon powder having a particle size of 10 ~ 30㎛ It features.

또, 상기 다공성 세라믹 담체 제조단계는, 상기 혼합된 혼합물을 700~1200℃의 온도에서 30~45시간 동안 열처리하여 상기 혼합물에 함유된 탄소를 산화시켜 다공성 세라믹 담체 제조하는 것을 특징으로 한다. In the preparing of the porous ceramic carrier, the mixed mixture is heat-treated at a temperature of 700 to 1200 ° C. for 30 to 45 hours to oxidize carbon contained in the mixture to prepare a porous ceramic carrier.

또, 상기 혼합미생물 투입단계는, 상기 제조된 다공성 세라믹 담체 100중량부에 혼합미생물을 2~3중량부을 투입하되, 상기 혼합미생물은 바실러스(Bacillus), 슈도모나스(Pseudomonas), 니트로박터(Nitrobacter), 니트로조모나스(Nitrosomonas), 니트로소코커스(Nitrosococcus), 알칼리게네스(Alcaligenes), 티오바실러스(Thiobacillus) 중에서 선택된 1종 이상이 혼합된 것을 특징으로 한다. In addition, the mixed microorganism input step, the mixed microorganisms 2 to 3 parts by weight to 100 parts by weight of the prepared porous ceramic carrier, the mixed microorganisms are Bacillus (Bacillus), Pseudomonas (Pseudomonas), Nitrobacter (Nitrobacter), Nitrozomonas (Nitrosomonas), Nitrosococcus (Nitrosococcus), Alkali geneses (Alcaligenes), Thiobacillus (Thiobacillus) It is characterized in that at least one selected.

또, 상기 산소발생제 추가단계는, 상기 혼합미생물이 투입된 다공성 세라믹 담체 100중량부에 산소발생제를 5~15중량부 추가하되, 상기 산소발생제는 액상 H2O2, 과립 또는 분말형태의 MGO2, KMnO4로 이루어진 군에서 선택된 1종 이상인 것을 특징으로 한다. In addition, the oxygen generator addition step, 5 to 15 parts by weight of the oxygen generating agent is added to 100 parts by weight of the porous ceramic carrier in which the mixed microorganism is added, the oxygen generating agent in the form of liquid H 2 O 2 , granules or powder MGO 2 , KMnO 4 It is characterized in that at least one member selected from the group consisting of.

본 발명에 따라 제조된 악취 및 유기휘발성 화합물을 제거하기 위한 바이오 필터용 조성물은 하천변의 자전거 도로, 어린이 놀이터, 학교 운동장 등에 포설되고 있는 탄성바닥재에 포함되어 유출될 수 있는 악취 및 유해화학물질인 T-VOCs(벤젠, 톨루엔, 에틸벤젠, 크실렌)을 미생물을 이용해서 용이하게 이산화탄소(CO2), 물(H2O), 무기질 등으로 변환시켜 대기오염을 개선시키는 효과가 있다. Bio-filter composition for removing odor and organic volatile compounds prepared according to the present invention is a odor and harmful chemicals that can be leaked contained in the elastic floor material installed in the riverside bicycle road, children's playground, school playground, etc. -VOCs (benzene, toluene, ethylbenzene, xylene) are easily converted to carbon dioxide (CO 2 ), water (H 2 O), minerals, etc. using microorganisms to improve air pollution.

도 1은 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법을 개략적으로 도시한 단계흐름도이다. 1 is a schematic flowchart illustrating a method for preparing a composition for a biofilter for improving air pollution by removing odors and organic volatile compounds.

이하, 본 발명의 바람직한 실시예를 첨부된 도면을 참조하여 상세히 설명하면 다음과 같다.Hereinafter, preferred embodiments of the present invention will be described in detail with reference to the accompanying drawings.

도 1은 악취 및 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법을 개략적으로 도시한 단계흐름도이다. 1 is a schematic flowchart illustrating a method for preparing a composition for a biofilter for improving air pollution by removing odors and odors and organic volatile compounds.

첨부된 도 1을 참조하면, 본 발명에 따른 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법은 혼합단계(S10), 다공성 세라믹 담체 제조단계(S20), 혼합미생물 투입단계(S30) 및 산소발생제 추가단계(S40)를 포함하여 이루어진다. Referring to FIG. 1, the method for preparing a composition for a biofilter for improving air pollution by removing odors and organic volatile compounds according to the present invention includes a mixing step (S10), a porous ceramic carrier manufacturing step (S20), and a mixed microorganism input step. (S30) and the oxygen generator additional step (S40) is made.

1. 혼합단계(S10) 1. Mixing step (S10)

혼합단계(S10)는 탄소, 탄화규소, 고분자 바인더를 혼합하는 단계이다. Mixing step (S10) is a step of mixing carbon, silicon carbide, polymer binder.

더 상세하게는, 입자크기가 10~30㎛인 탄소분말 100중량부에 대하여, 입자크기가 35~50㎛인 탄화규소분말 30~50중량부, 고분자 바인더 0.5~2중량부를 혼합하는 것이다. More specifically, 30 to 50 parts by weight of the silicon carbide powder having a particle size of 35 to 50 µm and 0.5 to 2 parts by weight of the polymer binder are mixed with 100 parts by weight of the carbon powder having a particle size of 10 to 30 µm.

입자크기가 10~30㎛인 탄소분말 100중량부에 대하여, 입자크기가 35~50㎛인 탄화규소분말 30~50중량부, 고분자 바인더 0.5~2중량부를 혼합하는 것은 하기의 단계에 따라 열처리되어 탄소가 산화되어 기공이 형성되되, 미생물이 원활하게 부착될 수 있도록 입자크기는 20~30㎛, 기공률이 50~60%인 다공성 구조를 갖도록 하기 위함이다. Mixing 30 to 50 parts by weight of the silicon carbide powder having a particle size of 35 to 50 μm and 0.5 to 2 parts by weight of the polymer binder with respect to 100 parts by weight of the carbon powder having a particle size of 10 to 30 μm is heat-treated according to the following steps. The pores are formed by oxidizing carbon, so that the microparticles can be attached smoothly to have a porous structure with a particle size of 20 to 30 μm and a porosity of 50 to 60%.

만약, 상기의 탄소분말, 탄화규소분말의 입자크기가 상기의 범위를 벗어나게 되면, 열처리과정 이후 탄소가 산화되어 기공이 형성될 때 기대하는 입자크기 및 기공율이 도출되기 어려울 수 있다. If the particle size of the carbon powder and silicon carbide powder is out of the above range, it may be difficult to derive the expected particle size and porosity when carbon is oxidized after the heat treatment process to form pores.

그리고, 상기 고분자 바인더는 폴리우레탄, 폴리비닐알콜, 폴리에틸렌글리콜, 폴리아크릴릭산, 폴리메틸메타아크릴레이트 및 하이드록시프로필메틸셀룰로오즈 중에서 선택된 1종 이상을 혼합한 것이다. In addition, the polymer binder is a mixture of one or more selected from polyurethane, polyvinyl alcohol, polyethylene glycol, polyacrylic acid, polymethyl methacrylate, and hydroxypropyl methyl cellulose.

그리고, 입자크기가 10~30㎛인 탄소분말 100중량부에 대하여, 입자크기가 1~5mm인 황토분말 20~30중량부, 입자크기가 3~10mm인 팽창점토분말 10~20중량부를 더 혼합할 수 있다. Further, 20 to 30 parts by weight of ocher powder having a particle size of 1 to 5 mm and 10 to 20 parts by weight of expanded clay powder having a particle size of 3 to 10 mm are further mixed with 100 parts by weight of carbon powder having a particle size of 10 to 30 μm. can do.

상기 황토분말과 팽창점토분말은 미네랄 성분을 함유하여 미생물의 성장을 돕고, 보습력 및 통기성이 우수하다. 또한, 황토분말과 팽창점토분말은 하기의 열처리과정을 통하여 점성을 갖게 되어 결합력을 더욱 높일 수 있다.The ocher powder and expanded clay powder contains minerals to help the growth of microorganisms, and excellent moisture and breathability. In addition, the ocher powder and expanded clay powder has a viscosity through the following heat treatment process can further increase the bonding strength.

2. 다공성 세라믹 담체 제조단계(S20)2. Porous ceramic carrier manufacturing step (S20)

다공성 세라믹 담체 제조단계(S20)는 상기 혼합된 혼합물을 열처리하여 상기 혼합물에 함유된 탄소를 산화시키는 단계이다. Porous ceramic carrier manufacturing step (S20) is a step of oxidizing the carbon contained in the mixture by heat treatment of the mixed mixture.

더 상세하게는, 상기 혼합된 혼합물을 700~1,200℃의 온도에서 30~45시간 동안 열처리하여 상기 혼합물에 함유된 탄소를 산화시켜 다공성 세라믹 담체를 제조하는 것이다. More specifically, the mixed mixture is heat-treated for 30 to 45 hours at a temperature of 700 ~ 1,200 ℃ to oxidize the carbon contained in the mixture to prepare a porous ceramic carrier.

상기 혼합된 혼합물을 700~1,200℃의 온도에서 30~45시간 동안 열처리하여 상기 혼합물에 함유된 탄소를 산화시켜 다공성 세라믹 담체를 제조하는 것은 상기 범위의 온도 및 가열시간으로 인하여 혼합물에 함유된 탄소가 산화되어 CO2 가스형태로 방출되면서, 탄소가 빠져나간 구조체에 기공이 형성되는 것이다. The mixed mixture is heat-treated at a temperature of 700 to 1,200 ° C. for 30 to 45 hours to oxidize the carbon contained in the mixture to prepare a porous ceramic carrier, which is due to the temperature and heating time in the above range. As it is oxidized and released in the form of CO 2 gas, pores are formed in the structure from which carbon is released.

상기 혼합물에 함유된 고분자 바인더는 고온의 열처리 과정에서 기화하여 제거되었다. The polymer binder contained in the mixture was removed by vaporization during the high temperature heat treatment.

만약, 상기 혼합된 혼합물을 700℃ 미만의 온도에서 열처리할 경우에는 상기 혼합물에 함유된 탄소가 충분히 산화되지 않을 수 있으며, 1,200℃ 초과한 온도에서 열처리할 경우에는 상기 혼합물에 함유된 탄소의 산화 양이 더이상 증가되지 않아 비경제적이다. If the mixed mixture is heat treated at a temperature of less than 700 ° C., the carbon contained in the mixture may not be sufficiently oxidized. If the mixed mixture is heat treated at a temperature exceeding 1,200 ° C., the amount of oxidation of carbon contained in the mixture may be reduced. It is not economical anymore because it is no longer increased.

그리고, 상기 혼합된 혼합물을 700~1,200℃의 온도에서 30시간 미만으로 열처리할 경우에는 상기 혼합물에 함유된 탄소가 충분히 산화되지 않고 소결체 내에 기공이 아닌 갈라진 틈이 생길 수 있으며, 45시간 초과하여 열처리할 경우에는 상기 혼합물에 함유된 탄소의 산화 양이 더이상 증가되지 않아 비경제적이다. When the mixed mixture is heat treated at a temperature of 700 to 1,200 ° C. for less than 30 hours, the carbon contained in the mixture may not be sufficiently oxidized, and cracks may be formed in the sintered body without pores. In this case, the amount of oxidation of carbon contained in the mixture is no longer increased, which is uneconomical.

상기 다공성 세라믹 담체는 넓은 비표면적을 가짐으로써 미생물이 부착되어 원활하게 생장할 수 있으며, 이를 통해 악취물질 및 유기휘발성 화합물을 제거할 수 있다. The porous ceramic carrier has a large specific surface area and thus microorganisms can be attached and grown smoothly, thereby removing odorous substances and organic volatile compounds.

3. 혼합미생물 투입단계(S30) 3. Mixed microorganism input step (S30)

혼합미생물 투입단계(S30)는 상기 제조된 다공성 세라믹 담체에 혼합미생물을 투입하는 단계이다. Mixed microbial input step (S30) is a step of adding a mixed microorganism to the prepared porous ceramic carrier.

더 상세하게는, 상기 제조된 다공성 세라믹 담체 100중량부에 혼합미생물을 2~3중량부 투입하는 것이다. More specifically, 2 to 3 parts by weight of mixed microorganisms are added to 100 parts by weight of the prepared porous ceramic carrier.

상기 혼합미생물은 바실러스(Bacillus), 슈도모나스(Pseudomonas), 니트로박터(Nitrobacter), 니트로조모나스(Nitrosomonas), 니트로소코커스(Nitrosococcus), 알칼리게네스(Alcaligenes), 티오바실러스(Thiobacillus) 중에서 선택된 1종 이상이 혼합된 것이다. The mixed microorganism is one selected from Bacillus, Pseudomonas, Nitrobacter, Nitrosomonas, Nitrosococcus, Alcaligenes and Thiobacillus. The above is mixed.

상기 미생물은 휘발성유기화합물(VOC) 등의 유해물질을 이산화탄소(CO2), 물(H2O), 무기질 등으로 변환시켜 주는 세균으로서, 공시균주나 혹은 다양한 미생물로부터 분뇨, 양어장, 그리고 각종 난해성 폐수 슬러지로부터 분리해낸 미생물 중 분해활성도가 높은 미생물을 선별하여 사용한다. The microorganism is a bacterium that converts harmful substances such as volatile organic compounds (VOCs) into carbon dioxide (CO 2 ), water (H 2 O), minerals, and the like. Among microorganisms separated from wastewater sludge, microorganisms with high degradation activity are selected and used.

그리고, 상기 제조된 다공성 세라믹 담체 100중량부에 혼합미생물을 2~3중량부 투입하는 것은 상기 제조된 다공성 세라믹 담체에 미생물이 투입되어 분해 활성도가 원활하게 이루어져 중금속, 다핵방향족탄화수소 및 유기휘발성 화합물인 유해물질과 반응시 각종 오염원이 분해균을 활성화시킨 후 다공성 담체에 흡착시켜 제거하기 위함이다. In addition, 2 to 3 parts by weight of mixed microorganisms are added to 100 parts by weight of the prepared porous ceramic carrier, and microorganisms are added to the prepared porous ceramic support to facilitate the decomposition activity, and are heavy metals, polynuclear aromatic hydrocarbons, and organic volatile compounds. This is to remove various contaminants by activating the decomposing bacteria when reacting with the harmful substances and adsorbing them on the porous carrier.

만약, 상기 제조된 다공성 세라믹 담체 100중량부에 혼합미생물을 2중량부 미만으로 투입할 경우에는 미생물의 분해 활성도가 충분히 진행되지 않을 수 있으며, 3중량부를 초과하여 투입할 경우에는 혼합미생물의 분해 활성도가 더이상 증가되지 않아 비경제적이다. If the mixed microorganism is added to less than 2 parts by weight to 100 parts by weight of the prepared porous ceramic carrier, the degradation activity of the microorganisms may not proceed sufficiently. Is no longer increased, making it uneconomical.

4. 산소발생제 추가단계(S40)4. Oxygen generator additional step (S40)

산소발생제 추가단계(S40)는 상기 혼합미생물이 투입된 다공성 세라믹 담체에 산소발생제를 추가하는 단계이다. Oxygen generator addition step (S40) is a step of adding an oxygen generator to the porous ceramic carrier in which the mixed microorganism is added.

더 상세하게는, 상기 혼합미생물이 투입된 다공성 세라믹 담체 100중량부에 산소발생제를 5~15중량부 추가하는 것이다. More specifically, 5 to 15 parts by weight of an oxygen generator is added to 100 parts by weight of the porous ceramic carrier into which the mixed microorganisms are added.

여기서, 상기 산소발생제는, 액상 H2O2, 과립 또는 분말형태의 MGO2, KMnO4로 이루어진 군에서 선택된 1종 이상인 것이다. Here, the oxygen generator is one or more selected from the group consisting of liquid H 2 O 2 , granules or powder form MGO 2 , KMnO 4 .

산소발생제의 첨가량은 다공성 세라믹 담체의 접촉면적에 따라 증감될 수 있다. The amount of oxygen generator added may be increased or decreased depending on the contact area of the porous ceramic carrier.

그리고, 상기 혼합미생물이 투입된 다공성 세라믹 담체 100중량부에 산소발생제를 5중량부 미만으로 투입할 경우에는 산소 발생량이 부족하여 미생물의 생장을 방해할 수 있으며, 15중량부를 초과하여 투입하면 경제성이 떨어지게 된다. In addition, when less than 5 parts by weight of the oxygen generator is added to 100 parts by weight of the porous ceramic carrier in which the mixed microorganisms are added, oxygen generation may be insufficient to hinder the growth of the microorganisms. Will fall.

상기 산소발생제 추가단계(S40) 이후에, 상기 산소발생제가 추가된 다공성 세라믹 담체 100중량부에 천연식물성 오일을 2~5중량부 더 추가할 수 있다. After the oxygen generator addition step (S40), 2 to 5 parts by weight of the natural vegetable oil may be further added to 100 parts by weight of the porous ceramic carrier to which the oxygen generator is added.

상기 산소발생제가 추가된 다공성 세라믹 담체 100중량부에 천연식물성 오일을 2~5중량부 더 추가함으로써 친환경적인 천연식물성 오일을 주성분으로 포함하게 되면, 이를 통해 유기휘발성 화합물인 유해물질을 더욱 확실하게 제거하면서도 2차 환경오염을 유발시키는 것을 방지 할 수 있다. By adding 2-5 parts by weight of natural vegetable oil to 100 parts by weight of the porous ceramic carrier to which the oxygen generator is added, when eco-friendly natural vegetable oil is included as a main component, the harmful substances as organic volatile compounds are more reliably removed. At the same time, it can prevent secondary environmental pollution.

만약, 상기 산소발생제가 추가된 다공성 세라믹 담체 100중량부에 천연식물성 오일을 2중량부 미만으로 추가할 경우에는 상기 산소발생제가 추가된 다공성 세라믹 담체에 천연식물성 오일이 골고루 혼합되지 않아 그 효과가 미미할 수 있으며, 5중량부를 초과하여 추가할 경우에는 더 이상의 유기휘발성 화합물인 유해물질 제거효과가 나타나지 않을 뿐 아니라 안전성이 저하될 우려가 있다. If the natural vegetable oil is added to less than 2 parts by weight to 100 parts by weight of the porous ceramic carrier to which the oxygen generator is added, the natural vegetable oil may not be evenly mixed with the porous ceramic carrier to which the oxygen generator is added. If the amount is added in an amount exceeding 5 parts by weight, the organic volatile compound may not only remove harmful substances, but also may deteriorate safety.

여기서, 상기 천연식물성 오일은 물 또는 유기용매 100중량부에 대하여, 티트리, 라임, 유자씨 중 하나 또는 둘 이상을 혼합하여 제조한 에센셜 오일 3~5중량부, 비이온계 유화제 3~5중량부, 유기아민 1~2중량부를 혼합하여 교반기에서 500~1,000rpm의 속도로 교반한 후, 15~20℃의 온도에서 3~5시간 동안 숙성하여 제조한 것이다. Here, the natural vegetable oil is 3 to 5 parts by weight of essential oils prepared by mixing one or two or more of tea tree, lime, citron seed with respect to 100 parts by weight of water or organic solvent, 3 to 5 parts by weight of nonionic emulsifier Part, 1 to 2 parts by weight of the organic amine was mixed and stirred at a speed of 500 to 1,000 rpm in a stirrer, and then prepared by aging for 3 to 5 hours at a temperature of 15 to 20 ℃.

상기 에센셜 오일은 티트리, 라임, 유자씨 중 하나 또는 둘 이상을 혼합한 혼합물 100중량부에 물 300~500중량부를 혼합하여 100~120℃ 온도의 고압멸균기에서 3~5시간 동안 추출한 후 여과하여 농축한 농축액을 사용한다. The essential oil is mixed with 300 to 500 parts by weight of water to 100 parts by weight of a mixture of one or two or more of tea tree, lime, citron seed, extracted for 3 to 5 hours in an autoclave at a temperature of 100 ~ 120 ℃ and filtered Use concentrated concentrate.

그리고, 상기 비이온계 유화제는 천연 또는 수소화 식물성 오일과 에틸렌글리콜과의 반응 생성물이다. The nonionic emulsifier is a reaction product of natural or hydrogenated vegetable oil with ethylene glycol.

상기의 방법으로 제조된 바이오 필터용 조성물은 하천변의 자전거 도로, 어린이 놀이터, 학교 운동장 등에 포설되고 있는 탄성바닥재에 포함되어 유출될 수 있는 악취 및 유해화학물질인 T-VOCs(벤젠, 톨루엔, 에틸벤젠, 크실렌)을 미생물을 이용해서 용이하게 이산화탄소(CO2), 물(H2O), 무기질 등으로 변환시켜 대기오염을 개선시키는 효과가 있다. The biofilter composition prepared by the above method is T-VOCs (benzene, toluene, ethylbenzene, which are odors and harmful chemicals that may be leaked by being included in the elastic flooring material installed on a riverside road, children's playground, school playground, etc.). , Xylene) is easily converted to carbon dioxide (CO 2 ), water (H 2 O), minerals and the like using microorganisms to improve air pollution.

또한, 넓은 비표면적을 가진 다공성 물질을 이용하여 미생물이 부착되어 원활하게 성장할 수 있고, 미생물의 성장 및 증식에 필요한 무기 영양분을 공급하기 위한 생장촉진제와 미생물의 활발한 분해를 통해 악취 및 유기휘발성 화합물을 더욱 효율적으로 제거할 수 있는 효과가 있다. In addition, by using a porous material having a large specific surface area, microorganisms can be attached and grow smoothly, and growth accelerators for supplying inorganic nutrients necessary for the growth and proliferation of microorganisms and active decomposition of microorganisms can be used to remove odors and organic volatile compounds. There is an effect that can be removed more efficiently.

이하에서 실시예를 통하여 본 발명을 더욱 구체적으로 설명한다. 그러나 하기의 실시예는 본 발명을 구체적으로 예시하기 위한 것일 뿐, 본 발명의 권리범위를 제한하는 것이 아님은 통상의 기술자에게 있어서 명백한 사실이다. 즉, 본 발명의 단순한 변형 내지 변경은 통상의 기술자에 의하여 용이하게 실시될 수 있으며, 이러한 변형이나 변경은 모두 본 발명의 영역에 포함되는 것으로 볼 수 있다. Hereinafter, the present invention will be described in more detail with reference to Examples. However, the following examples are only intended to specifically illustrate the present invention, it is obvious to those skilled in the art that does not limit the scope of the present invention. That is, simple modifications or changes of the present invention can be easily carried out by those skilled in the art, and all such modifications or changes can be seen to be included in the scope of the present invention.

실시예 1 : 본 발명에 따라 제조된 바이오 필터용 조성물Example 1 Biofilter Compositions Prepared According to the Present Invention

1) 입자크기가 20㎛인 탄소분말 100g, 입자크기가 50㎛인 탄화규소분말 50g, 고분자 바인더 2g을 혼합한다. 1) 100 g of carbon powder having a particle size of 20 μm, 50 g of silicon carbide powder having a particle size of 50 μm, and 2 g of a polymeric binder are mixed.

2) 1)의 혼합된 혼합물을 800℃의 온도에서 40시간 동안 열처리하여 상기 혼합물에 함유된 탄소를 산화시켜 다공성 세라믹 담체를 제조한다. 2) The mixed mixture of 1) is heat treated at a temperature of 800 ° C. for 40 hours to oxidize the carbon contained in the mixture to prepare a porous ceramic carrier.

3) 2)의 다공성 세라믹 담체 50g에 혼합미생물을 1g 투입한다(혼합미생물은 바실러스(Bacillus), 슈도모나스(Pseudomonas), 니트로박터(Nitrobacter), 니트로조모나스(Nitrosomonas)를 혼합하여 사용함). 3) 1 g of mixed microorganism is added to 50 g of the porous ceramic carrier of 2) (mixed microorganism is used by mixing Bacillus, Pseudomonas, Nitrobacter, and Nitrosomonas).

4) 3)의 상기 혼합미생물이 투입된 다공성 세라믹 담체 50g에 산소발생제를 3g추가한다(산소발생제는, 액상 H2O2, 과립 또는 분말형태의 MGO2, KMnO4 로 이루어짐 ). 4) Add 3 g of an oxygen generating agent to 50 g of the porous ceramic carrier in which the mixed microorganisms of 3) are added (oxygen generating agent is liquid H 2 O 2 , granular or powdered MGO 2 , KMnO 4 Consisting of)

실시예 2 : 본 발명에 따라 제조된 바이오 필터용 조성물(천연식물성 오일 추가) Example 2 biofilter composition prepared according to the present invention (natural vegetable oil added)

1) 입자크기가 20㎛인 탄소분말 100g, 입자크기가 50㎛인 탄화규소분말 50g, 고분자 바인더 2g을 혼합한다. 1) 100 g of carbon powder having a particle size of 20 μm, 50 g of silicon carbide powder having a particle size of 50 μm, and 2 g of a polymeric binder are mixed.

2) 1)의 혼합된 혼합물을 800℃의 온도에서 40시간 동안 열처리하여 상기 혼합물에 함유된 탄소를 산화시켜 다공성 세라믹 담체를 제조한다. 2) The mixed mixture of 1) is heat treated at a temperature of 800 ° C. for 40 hours to oxidize the carbon contained in the mixture to prepare a porous ceramic carrier.

3) 2)의 다공성 세라믹 담체 50g에 혼합미생물을 1g 투입한다(혼합미생물은 바실러스(Bacillus), 슈도모나스(Pseudomonas), 니트로박터(Nitrobacter), 니트로조모나스(Nitrosomonas)를 혼합하여 사용함). 3) 1 g of mixed microorganism is added to 50 g of the porous ceramic carrier of 2) (mixed microorganism is used by mixing Bacillus, Pseudomonas, Nitrobacter, and Nitrosomonas).

4) 3)의 상기 혼합미생물이 투입된 다공성 세라믹 담체 50g에 산소발생제를 3g 추가한다(산소발생제는, 액상 H2O2, 과립 또는 분말형태의 MGO2, KMnO4 로 이루어짐 ). 4) Add 3 g of an oxygen generator to 50 g of the porous ceramic carrier in which the mixed microorganisms are introduced (3) (oxygen generator is liquid H 2 O 2 , granular or powdered MGO 2 , KMnO 4). Consisting of)

5) 4)의 산소발생제가 추가된 다공성 세라믹 담체 50g에 천연식물성 오일을 1g 더 추가한다(티트리, 라임, 유자씨를 혼합하여 제조한 에센셜 오일 10g, 비이온계 유화제 10g, 유기아민 5g을 혼합하여 교반기에서 700rpm의 속도로 교반한 후, 20℃의 온도에서 5시간 동안 숙성하여 제조함). 5) Add 1 g of natural vegetable oil to 50 g of the porous ceramic carrier to which the oxygen generator of 4) is added (10 g of essential oil prepared by mixing tea tree, lime and citron seed, 10 g of nonionic emulsifier, and 5 g of organic amine). After stirring at a speed of 700rpm in a stirrer, it is prepared by aging for 5 hours at a temperature of 20 ℃).

실험 : 탈취성능Experiment: Deodorization Performance

유해 및 악취가스에 대한 탈취성능을 실험하였다. 탈취율은 검지관법(KS M 0062:2003)에 준하여 실시하였으며, 10L의 탈취용기에 본 발명에 따라 제조된 바이오 필터용 조성물(실시예 1, 실시예 2) 1g을 각각 투입하여 1시간 후에 탈취율을 확인하였다. The deodorizing performance of harmful and odorous gases was tested. Deodorization rate was carried out according to the detection tube method (KS M 0062: 2003), 1 g of the composition for biofilters prepared according to the present invention (Example 1, Example 2) in each 10L deodorization vessel was added after 1 hour to deodorization rate Confirmed.

탈취율(%)Deodorization rate (%) 암모니아ammonia 황화수소Hydrogen sulfide 포름알데히드Formaldehyde 실시예 1Example 1 8686 9191 8080 실시예 2Example 2 8888 9292 8282

상기 표 1에서 알 수 있는 바와 같이, 본 발명에 따라 제조된 바이오 필터용 조성물은 유해 및 악취가스에 대해 탁월한 성능을 나타내고 있음을 확인할 수 있었다. As can be seen in Table 1, it was confirmed that the biofilter composition prepared according to the present invention exhibited excellent performance against harmful and odorous gases.

Claims (5)

탄소, 탄화규소, 고분자 바인더를 혼합하는 혼합단계(S10);
상기 혼합된 혼합물을 열처리하여 상기 혼합물에 함유된 탄소를 산화시키는 다공성 세라믹 담체 제조단계(S20);
상기 제조된 다공성 세라믹 담체에 혼합미생물을 투입하는 혼합미생물 투입단계(S30); 및
상기 혼합미생물이 투입된 다공성 세라믹 담체에 산소발생제를 추가하는 산소발생제 추가단계(S40);
를 포함하는 것을 특징으로 하는 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법.
Mixing step of mixing carbon, silicon carbide, and a polymeric binder (S10);
Heat-treating the mixed mixture to prepare a porous ceramic carrier for oxidizing carbon contained in the mixture (S20);
A mixed microorganism input step (S30) of introducing a mixed microorganism into the prepared porous ceramic carrier; And
Adding an oxygen generator to the porous ceramic carrier into which the mixed microorganism is added (S40);
Bio-filter composition manufacturing method for improving air pollution by removing odor and organic volatile compounds, characterized in that it comprises a.
제1항에 있어서,
상기 혼합단계(S10)는,
입자크기가 10~30㎛인 탄소분말 100중량부에 대하여,
입자크기가 35~50㎛인 탄화규소분말 30~50중량부,
고분자 바인더 0.5~2중량부를 혼합하는 것을 특징으로 하는 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법.
The method of claim 1,
The mixing step (S10),
With respect to 100 parts by weight of the carbon powder having a particle size of 10 ~ 30㎛,
30-50 parts by weight of silicon carbide powder having a particle size of 35-50 μm,
Method for producing a composition for a bio-filter for improving air pollution by removing odor and organic volatile compounds, characterized in that 0.5 to 2 parts by weight of a polymer binder is mixed.
제1항에 있어서,
상기 다공성 세라믹 담체 제조단계(S20)는,
상기 혼합된 혼합물을 700~1,200℃의 온도에서 30~45시간 동안 열처리하여 상기 혼합물에 함유된 탄소를 산화시켜 다공성 세라믹 담체를 제조하는 것을 특징으로 하는 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법.
The method of claim 1,
The porous ceramic carrier manufacturing step (S20),
The mixed mixture is heat-treated at a temperature of 700 to 1,200 ° C. for 30 to 45 hours to oxidize the carbon contained in the mixture to prepare a porous ceramic carrier, thereby removing odors and organic volatile compounds. Biofilter composition production method.
제1항에 있어서,
상기 혼합미생물 투입단계(S30)는,
상기 제조된 다공성 세라믹 담체 100중량부에 혼합미생물을 2~3중량부을 투입하되,
상기 혼합미생물은 바실러스(Bacillus), 슈도모나스(Pseudomonas), 니트로박터(Nitrobacter), 니트로조모나스(Nitrosomonas), 니트로소코커스(Nitrosococcus), 알칼리게네스(Alcaligenes), 티오바실러스(Thiobacillus) 중에서 선택된 1종 이상이 혼합된 것을 특징으로 하는 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법.
The method of claim 1,
The mixed microorganism input step (S30),
To 2 to 3 parts by weight of mixed microorganisms in 100 parts by weight of the prepared porous ceramic carrier,
The mixed microorganism is one selected from Bacillus, Pseudomonas, Nitrobacter, Nitrosomonas, Nitrosococcus, Alcaligenes and Thiobacillus. Method for producing a composition for a bio-filter for improving air pollution by removing the odor and organic volatile compounds, characterized in that the above mixture.
제1항에 있어서,
상기 산소발생제 추가단계(S40)는,
상기 혼합미생물이 투입된 다공성 세라믹 담체 100중량부에 산소발생제를 5~15중량부 추가하되,
상기 산소발생제는,
액상 H2O2, 과립 또는 분말형태의 MgO2, KMnO4로 이루어진 군에서 선택된 1종 이상인 것을 특징으로 하는 악취 및 유기휘발성 화합물 제거로 대기오염개선을 위한 바이오 필터용 조성물 제조방법.
The method of claim 1,
The oxygen generator addition step (S40),
5 to 15 parts by weight of an oxygen generating agent is added to 100 parts by weight of the porous ceramic carrier into which the mixed microorganism is added,
The oxygen generator,
Method for producing a composition for a bio-filter for improving air pollution by removing odor and organic volatile compounds, characterized in that at least one selected from the group consisting of liquid H 2 O 2 , granules or powder form MgO 2 , KMnO 4 .
KR1020190083258A 2019-07-10 2019-07-10 The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds KR102016146B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1020190083258A KR102016146B1 (en) 2019-07-10 2019-07-10 The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1020190083258A KR102016146B1 (en) 2019-07-10 2019-07-10 The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds

Publications (1)

Publication Number Publication Date
KR102016146B1 true KR102016146B1 (en) 2019-10-23

Family

ID=68460733

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1020190083258A KR102016146B1 (en) 2019-07-10 2019-07-10 The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds

Country Status (1)

Country Link
KR (1) KR102016146B1 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111569640A (en) * 2020-05-21 2020-08-25 赵兰坤 Threonine fermentation tail gas environment-friendly treatment process
KR102708737B1 (en) 2023-11-29 2024-09-23 주식회사 이젠바이오텍 Material production method for reducing radioactivity and volatile organic compounds using coevolutionary microorganisms and plant malt

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100433644B1 (en) * 2003-10-01 2004-06-01 주식회사 에취켓 Porous Polymer Matrix Formed with Activated Carbon and Zeolite for Biofilter and Method for Preparing the Same
KR100664882B1 (en) 2006-05-18 2007-01-04 김영준 Bio-filter media composition for deordorization and apparatus therefor
KR20090045533A (en) * 2007-11-02 2009-05-08 에스케이케미칼주식회사 Deodorizing machine using microorganism culture apparatus
KR101621098B1 (en) 2009-10-29 2016-05-13 한양대학교 에리카산학협력단 Biofilter and the method of preparing the same

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100433644B1 (en) * 2003-10-01 2004-06-01 주식회사 에취켓 Porous Polymer Matrix Formed with Activated Carbon and Zeolite for Biofilter and Method for Preparing the Same
KR100664882B1 (en) 2006-05-18 2007-01-04 김영준 Bio-filter media composition for deordorization and apparatus therefor
KR20090045533A (en) * 2007-11-02 2009-05-08 에스케이케미칼주식회사 Deodorizing machine using microorganism culture apparatus
KR101621098B1 (en) 2009-10-29 2016-05-13 한양대학교 에리카산학협력단 Biofilter and the method of preparing the same

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111569640A (en) * 2020-05-21 2020-08-25 赵兰坤 Threonine fermentation tail gas environment-friendly treatment process
KR102708737B1 (en) 2023-11-29 2024-09-23 주식회사 이젠바이오텍 Material production method for reducing radioactivity and volatile organic compounds using coevolutionary microorganisms and plant malt

Similar Documents

Publication Publication Date Title
Barbusinski et al. Biological methods for odor treatment–A review
Kumar et al. Biofiltration of volatile organic compounds (VOCs): an overview
Kuppusamy et al. Ex-situ remediation technologies for environmental pollutants: a critical perspective
Vikrant et al. Bio-filters for the Treatment of VOCs and Odors-A Review
Padhi et al. Biological oxidation of gaseous VOCs–rotating biological contactor a promising and eco-friendly technique
Fulazzaky et al. Biofiltration process as an ideal approach to remove pollutants from polluted air
CN103418236B (en) A kind of biological deodorizing filler and device
Janni et al. Evaluation of biofiltration of air--an innovative air pollution control technology
KR102016146B1 (en) The manufacturing method of composition for bio filter for improving air pollution by removing odour and organic volatile compounds
EP2767585A1 (en) Microbiological method of H2S removal from biogas
US20050084949A1 (en) Biological filter
Barbusiński et al. Biofilters versus bioscrubbers and biotrickling filters: State-of-the-art biological air treatment
KR102063332B1 (en) The manufacturing method of composition for bio filter for removing volatile organic compounds
Soccol et al. Biofiltration: an emerging technology
JP2002018480A (en) Method for cleaning water contaminated by refractory material
KR100821780B1 (en) Microorganism-immobilized polymer hydrogel beads for the removal of VOC and odor and the preparing method thereof
Gopinath et al. Microbial degradation of toluene
Cha et al. Treatment technologies
KR100319390B1 (en) Agent for treating environmental pollutants utilizing cast and method for producing thereof
Lebrero et al. Air biofiltration applied to odor treatment
KR20160063108A (en) Hybrid type biofilter system for removal of odor cases and volatile organic compounds
Kim et al. Removal of dimethyl sulfide in ceramic biofilters immobilized with Thiobacillus thioparus TK-m
KR102480082B1 (en) Biofilm for food wastewater treatment and food wastewater treatment method using the same
KR102480083B1 (en) Treatment method of food wastewater
KR100277565B1 (en) Porous ceramics for treating food waste and eliminating a bad smell