KR100373413B1 - Process for removing heavy metal components from fly ash by using microorganism - Google Patents

Process for removing heavy metal components from fly ash by using microorganism Download PDF

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KR100373413B1
KR100373413B1 KR10-2001-0002198A KR20010002198A KR100373413B1 KR 100373413 B1 KR100373413 B1 KR 100373413B1 KR 20010002198 A KR20010002198 A KR 20010002198A KR 100373413 B1 KR100373413 B1 KR 100373413B1
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microorganism
incineration ash
metal
microorganisms
removing heavy
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KR20020061248A (en
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김은기
김순영
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자연엔지니어링 주식회사
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/20Agglomeration, binding or encapsulation of solid waste
    • B09B3/21Agglomeration, binding or encapsulation of solid waste using organic binders or matrix
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B2101/00Type of solid waste
    • B09B2101/30Incineration ashes

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

본 발명은 미생물을 이용하여 소각재 내의 중금속을 제거하는 방법에 관한 것으로, 소각재에 물과 배지를 혼합하고 미생물을 첨가하여 배양하면, 상기 미생물이 성장하면서 생성된 유기산에 의해 소각재 내의 금속이 수용액 상으로 용출되고, 수용액 상에서 미생물의 금속 흡착능에 의하여 상기 미생물에 금속이 흡착되면, 그 미생물을 회수함으로써 이루어지는 것을 특징으로 한다.The present invention relates to a method for removing heavy metals in an incineration ash by using microorganisms. When the medium is mixed with water and incubated in the incineration ash, the microorganism is added to the culture, and the metal in the incineration ash is formed into an aqueous solution by the organic acid generated as the microorganism grows. When the metal is eluted and adsorbed to the microorganism by the metal adsorption capacity of the microorganism in the aqueous solution, the microorganism is recovered by recovering the microorganism.

본 발명의 방법에 따르면, 소각재에 포함되어 있는 중금속 등을 미생물에 흡착시켜서 회수할 수 있으므로, 별도의 특별한 장치 없이 단시간 내에 환경친화적인 방법으로 소각재 중의 금속을 제거할 수 있다.According to the method of the present invention, since heavy metals and the like contained in the incineration ash can be adsorbed and recovered by microorganisms, the metal in the incineration ash can be removed in an environmentally friendly manner within a short time without any special device.

Description

미생물을 이용한 소각재 내의 중금속 제거방법{Process for removing heavy metal components from fly ash by using microorganism}Process for removing heavy metal components from fly ash by using microorganism}

본 발명은 소각재에 포함되어 있는 중금속을 제거하는 방법에 관한 것이다. 더욱 상세하게는, 본 발명은 석탄 소각에 의해 발생된 소각재에 포함되어 있는 중금속을 미생물을 이용하여 제거하는 방법에 관한 것이다.The present invention relates to a method for removing heavy metals contained in an incineration ash. More specifically, the present invention relates to a method for removing heavy metals contained in incineration ash generated by coal incineration using microorganisms.

석탄의 소각에 의해 발생된 소각재에는 구리, 비소, 크롬, 아연 등의 금속이 포함되어 있기 때문에, 이를 직접 매립할 경우에는 소각재에서 용출되어 나오는 금속으로 인하여 수질이 오염되고 나아가 심각한 환경문제의 원인이 된다.Since incineration ash generated by incineration of coal contains metals such as copper, arsenic, chromium, and zinc, when landfilled directly, the metals eluted from the incineration ash contaminate water quality and cause serious environmental problems. do.

이의 대책으로서 현재까지는, 소각재를 직접 매립하지 않고 제한된 공간에서 장기간 보존한 후에 매립하는 방법이 사용되고 있다. 이와 같이 장기간 소각재를 보존하는 경우에(예를 들면, 10년 이상), 소각재 내의 금속은 소각재 내의 물질에 고정화되어서 매립 시에 금속이 용출되지 않는 것으로 보고되어 있다 [Kumar V., Proceeding of the International Conference Fly Ash Disposal and Utilization:India Central Board of Inigation and Power New Delhi, 1998, pp1-7].As a countermeasure, until now, the method of embedding an incineration ash after storing it for a long time in a limited space rather than embedding it is used. In the case of long-term incineration (eg, 10 years or more), metals in the incinerators have been reported to be immobilized to the material in the incinerators, so that the metals do not elute at the time of landfilling. Conference Fly Ash Disposal and Utilization: India Central Board of Inigation and Power New Delhi, 1998, pp 1-7].

그러나, 이러한 방법은 긴 시간이 소요되고 막대한 임시 저장공간이 요구될 뿐 아니라 효과적으로 금속을 제거, 안정화하는 기술은 아니다.However, this method takes a long time and requires a large amount of temporary storage space and is not a technology for effectively removing and stabilizing metal.

최근에는 고온(800-1000℃)에서 소각재를 가열함으로써 금속을 증기화하고, 증발된 금속을 다시 회수하는 열처리 공법이 개발되었다 [A. Jakob S. Stuck, "Complete Heavy Metal Removal from Fly Ash by Heat Treatment": Environ. Sci. Technal 1996, 30, 3275-3283]. 그러나, 이 방법은 많은 에너지가 소요될 뿐 아니라 증발된 금속을 회수하는 별도의 장치가 요구되므로 경제적으로 불합리하다.Recently, a heat treatment method has been developed to vaporize a metal by heating the incinerator at a high temperature (800-1000 ° C.) and recover the evaporated metal again [A. Jakob S. Stuck, "Complete Heavy Metal Removal from Fly Ash by Heat Treatment": Environ. Sci. Technal 1996, 30, 3275-3283. However, this method is economically unreasonable because it not only consumes a lot of energy but also requires a separate device for recovering evaporated metal.

따라서, 본 발명자들은 이와 같은 종래 기술의 문제점을 해소하고, 소각재로부터 유해한 중금속을 효과적으로 제거하기 위한 방법의 개발을 위하여 연구노력을 거듭하여, 미생물을 이용하여 소각재의 중금속을 제거할 수 있는 경제적이고 환경친화적인 방법을 개발하여 본 발명을 완성하였다.Therefore, the present inventors solve the problems of the prior art, and continue to research for the development of a method for effectively removing the harmful heavy metals from incineration ash, economical and environmental that can remove heavy metals from incineration ash using microorganisms A friendly method was developed to complete the present invention.

본 발명에 따른 소각재 내의 중금속 제거방법을 구체적으로 설명하면 다음과 같다.Referring to the heavy metal removal method in the incineration ash according to the present invention in detail.

즉, 소각재에 미생물이 자랄 수 있도록 물과 배지를 적절히 혼합하고, 미생물을 첨가하여 배양하면, 미생물이 성장하면서 유기산이 생산되고 이 유기산에 의해 처리조 내의 pH가 낮아지게 된다.That is, when the microorganisms are properly mixed with water and the medium so that the microorganisms grow, the microorganisms are grown and the organic acid is produced as the microorganisms grow, and the organic acid lowers the pH in the treatment tank.

이에 따라 소각재 내의 금속은 수용액 상으로 용출되는데, pH가 낮아질수록 용해도가 증가됨은 물론이다.Accordingly, the metal in the incineration ash is eluted into the aqueous solution phase, so that the solubility increases as the pH is lowered.

이 때, 용출된 금속은 수용액 중에 존재하는 미생물의 금속 흡착능에 의해 미생물에 흡착된다.At this time, the eluted metal is adsorbed to the microorganism by the metal adsorption capacity of the microorganism present in the aqueous solution.

따라서 금속이 흡착된 상기 미생물을 회수함으로써 소각재 내에 포함되어 있던 금속이 함께 제거되는 것이다.Therefore, the metal contained in the incineration ash is removed together by recovering the microorganisms on which the metal is adsorbed.

본 발명에 사용될 수 있는 미생물은 성장시 유기산을 배출하며 금속 흡착능을 갖는 모든 종류의 미생물이 사용가능하다. 그러한 미생물로서 곰팡이 일부, 낮은 pH에서 성장 가능한 효모 등을 들 수 있다.The microorganisms that can be used in the present invention can be used for all kinds of microorganisms that emit organic acids upon growth and have a metal adsorption capacity. Examples of such microorganisms include some molds and yeasts that can grow at low pH.

특히 바람직하게 사용되는 것은 아스페르질루스 니거(Aspergilus niger)라는 미생물 곰팡이이다. 상기 미생물은 낮은 속도로 교반할 경우, 곰팡이가 실처럼 엉켜서 여과에 의해 쉽게 분리될 수 있다.Particularly preferably used is a microbial fungus called Aspergilus niger. When the microorganism is stirred at low speed, the fungus tangles like a thread and can be easily separated by filtration.

미생물의 배양을 위해 첨가되는 배지는 선택된 미생물의 성장에 적합한 배지라면 비제한적으로 사용이 가능하고, 배양 온도는 미생물의 생장에 적합한 온도 범위에서 임의로 선택되는데, 약 30℃ 정도가 바람직하다.The medium added for the cultivation of the microorganism can be used as long as it is a medium suitable for the growth of the selected microorganism, the culture temperature is arbitrarily selected from a temperature range suitable for the growth of the microorganism, about 30 ℃ is preferred.

<실시예><Example>

이하에, 본 발명을 실시예를 통하여 보다 상세히 설명한다. 다만 본 발명이 이 실시예에 국한되는 것은 아니다.Hereinafter, the present invention will be described in more detail with reference to Examples. However, the present invention is not limited to this embodiment.

실시예 1Example 1

소각재 100 g을 믹서기로 잘게 분쇄한 후 증류수 1 ℓ에 혼합하였다. 여기에 YM배지(효모추출물 3 g/ℓ, 맥아추출물 3 g/ℓ, 펩톤 5 g/ℓ, 포도당 10 g/ℓ) 10 g을 첨가한 후 2 ℓ들이 배양기에 넣고 멸균하였다. 같은 배지에서 하루 전에 배양한 미생물-곰팡이(Aspergilus niger)를 5% 접종하였다.100 g of the incineration ash was pulverized finely with a blender and mixed in 1 L of distilled water. To this was added 10 g of YM medium (3 g / l yeast extract, 3 g / l malt extract, 5 g / l peptone, 10 g / l glucose) and then put into a 2 L incubator and sterilized. The same medium was inoculated with 5% of microorganism-fungus (Aspergilus niger) cultured one day ago.

30℃에서 pH 조정을 하지 않고, 0.05 vvm의 속도로 공기를 공급하였다. 비교적 낮은 100 rpm의 속도로 교반하여 곰팡이가 실처럼 엉켜서 배양액으로부터 쉽게 분리되도록 하였다.Air was supplied at a rate of 0.05 vvm without pH adjustment at 30 ° C. Stirring at a relatively low speed of 100 rpm allowed the fungus to entangle like a yarn and easily separate from the culture.

배양 후 40 mesh의 체를 이용하여 균체를 여과/분리하고, 100℃에서 1일 간 건조 후 건조 중량을 측정하였다. 금속 함유량은 원자흡광기(Atomic Absorption)를 이용하여 측정하였다.After incubation, the cells were filtered / separated using a 40 mesh sieve, dried at 100 ° C. for 1 day, and then dried. Metal content was measured using Atomic Absorption.

5일 동안의 배양 결과를 표 1에 표시하였다.The culture results for 5 days are shown in Table 1.

DayDay 00 1One 22 33 44 55 세포량(g/ℓ)Cell volume (g / ℓ) 00 0.30.3 0.70.7 1.51.5 2.52.5 2.72.7 pHpH 77 5.25.2 4.04.0 3.23.2 3.23.2 3.23.2 포도당(g/ℓ)Glucose (g / ℓ) 1010 7.37.3 5.65.6 2.32.3 1.11.1 00 소각재 잔류 Cu(ppm)Incinerator Residual Cu (ppm) 165165 141141 105105 5454 3131 1313 미생물의 Cu 회수율(%)Cu recovery rate of microorganism (%) 00 14.514.5 3636 6767 8181 9292 소각재잔류 아연 (ppm)Incinerator ash (ppm) 280280 230230 150150 4545 2929 1414 미생물의 아연 회수율(%)% Of microorganisms in zinc 00 1818 4646 8484 8989 9494

상기 실시예의 결과에 나타난 바와 같이, 본 발명에 따르면 소각재 내에 포함되어 있는 중금속 등의 금속을 미생물에 흡착시켜서 회수할 수 있으므로, 별도의 특별한 장치 없이 단시간 내에 환경친화적인 방법으로 소각재 중의 금속을 제거할 수 있는 효과가 있다. 또한 실시의 규모가 커져도 미생물의 성장에 영향이 없으므로 대규모 공정에도 적용가능하다.As shown in the results of the above embodiment, according to the present invention can be recovered by adsorbing metals such as heavy metals contained in the incineration ash to the microorganisms, it is possible to remove the metal in the incineration ash in an environmentally friendly manner in a short time without a special device It can be effective. In addition, since the scale of implementation does not affect the growth of microorganisms, it is applicable to large scale processes.

Claims (2)

소각재에 물과 배지를 혼합하고 미생물을 첨가하여 배양하면, 상기 미생물이 성장하면서 생성된 유기산에 의해 소각재 내의 금속이 수용액 상으로 용출되고, 수용액 상에서 상기 미생물의 금속 흡착능에 의하여 상기 미생물에 금속이 흡착되면, 그 미생물을 회수함으로써 이루어지는 것을 특징으로 하는 미생물을 이용한 소각재 내의 중금속 제거방법.When the incineration ash is mixed with water and a medium, and microorganisms are added and cultured, the metal in the incineration ash is eluted into an aqueous solution by the organic acid generated as the microorganism grows, and the metal is adsorbed to the microorganism by the metal adsorption capacity of the microorganism in the aqueous solution. If so, the method for removing heavy metals in the incineration ash using a microorganism, characterized in that by recovering the microorganism. 제 1 항에 있어서, 상기 미생물은 아스페르질루스 니거(Aspergilus niger)인 것을 특징으로 하는 미생물을 이용한 소각재 내의 중금속 제거방법.[Claim 2] The method of claim 1, wherein the microorganism is Aspergilus niger.
KR10-2001-0002198A 2001-01-15 2001-01-15 Process for removing heavy metal components from fly ash by using microorganism KR100373413B1 (en)

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CN1887382B (en) * 2006-07-18 2010-05-12 哈尔滨工业大学 Method of eliminating heavy metals from garbage burning flyash
CN106111659A (en) * 2016-06-22 2016-11-16 浙江理工大学 Utilize the method that bacillus firmus reduces incineration of refuse flyash Leaching

Citations (4)

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KR100228993B1 (en) * 1996-01-29 1999-11-01 가네꼬 히사시 Method for the remediation of polluted soils
KR100258781B1 (en) * 1991-06-21 2000-06-15 콜스 윌리암 에이. Use of metalic peroxides in bioremediation
KR20010105915A (en) * 2000-05-19 2001-11-29 양인모 Process for the decontamination of soil containing toxic organic materials and heavy metal
KR20020013016A (en) * 2000-08-10 2002-02-20 양인모 Apparatus and method for bioremediation for contaminated sediments and soil

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100258781B1 (en) * 1991-06-21 2000-06-15 콜스 윌리암 에이. Use of metalic peroxides in bioremediation
KR100228993B1 (en) * 1996-01-29 1999-11-01 가네꼬 히사시 Method for the remediation of polluted soils
KR20010105915A (en) * 2000-05-19 2001-11-29 양인모 Process for the decontamination of soil containing toxic organic materials and heavy metal
KR20020013016A (en) * 2000-08-10 2002-02-20 양인모 Apparatus and method for bioremediation for contaminated sediments and soil

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