• 한국자원식물학회지
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• 제29권1호
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• pp.39-45
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• 2016

2012년부터 2013년에 걸쳐 식물체 근권과 비근권 토양을 수집하였다. 수집한 토양을 희석평판법을 이용하여 총 782개의 세균을 분리하였고, 분리한 세균을 실험실내에서 Trichothecium roseum과의 대치배양을 통해 균사생장억제율이 80% 내외로 우수한 길항력을 나타내는 균주를 선발하였다. I-plate에서 HK2균주와 T. roseum두 균을 격리하여 밀폐배양 시 모두 균사생장억제 효과는 없기 때문에 휘발 물질은 아닌 것으로 판단되었다. NB배지에 길항균주와 T. roseum을 액체배양 한 결과 88% 이상 균사생장억제 효과를 보였다. HK2균주를 동정하기 위해 16S rDNA 염기서열분석과 API 50 CHB Kit (BioMerieux, France)를 이용하여 생화학적 특성을 분석한 결과 Bacillus subtilis로 동정되었다. HK2 균주가 생산한 항진균물질을 butanol로 추출한 후 flash column chromatography를 이용하여 항진균물질을 정제한 결과 methanol 80%의 조건에서 잘 분리되었으며 향후 분리 순화를 통한 화학구조분석이 필요하다.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 1998년도 총회 및 춘계 학술발표회 논문집
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• pp.43-49
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• 1998

Retardation effect of heavy metals in soils caused by adsorption onto the surfaces of solids particles is well known phenomena. The adsorption of metal ions has been recognized more strong in clay mineral and organic matter contents rather than sands and gravels. In this study, we investigated the retardation effect in two sandy soils by conducting batch and column tests. The column tests were conducted to obtain the relationship between concentration and time known as breakthrough curve (BTC). We applied pulse type injection of ZnCl$_2$solution on the inlet boundary and monitored the effluent concentration at the exit boundary under steady state condition using EC-meter and ICP-AES. Batch test consisted of an equilibrium procedure for fine fractions collected from two sandy soils for various initial ZnCl$_2$concentrations, and analysis of Zn ions in equilibrated solution using ICP-AES. The results of column test showed that i) the peak concentration of Zn analyzed by ICP was far less than that detected by EC-meter for both soils and ii) travel times for peak concentration were more less identical for two different monitoring techniques. The first result can be explained by ion exchange between Zn and other cations initially present in the soil particles since ICP analysis showed a significant amount of Ca, Mg ions in the effluent. From the second result, we found that retardation effect was not present in these soils due to strong cation exchange capacity of Zn ion over other cations since we did not apply a solution containing more adsorptive cations such as Al. The result of batch test also showed high distribution coefficients (K$_{d}$) for two soils supporting the dominant ion exchange phenomena. Based on the retardation factor obtained from the Kd, we predicted the BTC using CDE model and compared with the BTC of Zn concentration obtained from ICP The predicted BTC, however, disagreed with the monitored in terms of travel time and magnitude of the peak concentrations. The only way to describe the prominent decrease of Zn ion was to introduce decay or sink coefficient in the CDE model to account for irreversible decrease of Zn ions in liquid phase.e.