• 한국환경생태학회지
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• 제18권3호
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• pp.340-345
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• 2004

본 연구에서는 FETAX의 방법에 따라 PCB(Aroclor)가 산개구리의 배아발생에 미치는 효과를 조사하였다. 배아의 치사율과 기형률은 probit 분석법으로 조사하였다. PCB에 의한 LC$_{50}$은 1.48ppb을 나타냈고 EC$_{50}$은 0.25ppb를 나타냈으며 TI는 5.7을 나타내어 PCB는 높은 치사율을 나타내는 최기형성 물질로 판단된다. 기형양상은 수포형성 기형이 0.1ppb에서 62.0%, 꼬리기형이 1ppb에서 32.0%, profund형의 기형이 5ppb에서 68.0%를 나타냈다. PCB는 비교적 낮은 농도인 1.0ppb에서 머리에서 꼬리까지의 성장을 저해하는 결과를 나타내어 이러한 배아의 성장억제에 의 한 평가는 환경오염물질의 독성을 평가하는 데 민감한 지표로 사용되어질 수 있을 것으로 생각된다. 결론적으로 이러한 결과는 PCB가 산개구리 배아발생과정에 높은 독성을 지닌 것을 나타낸다.

• Journal of Microbiology
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• 제44권1호
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• pp.23-28
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• 2006

We investigated the effects of halogenated aromatic compounds (HACs) including naturally occurring ones (L-thyroxine, 3-chloro-L-tyrosine, 5-chloroindole, 2-chlorophenol, 4-chlorophenol and chlorobenzene) on polychlorinated biphenyl (PCB) dechlorination in sediment cultures. A PCB-dechlorinating enrichment culture of sediment microorganisms from the St. Lawrence River was used as an initial inoculum. When the culture was inoculated into Aroclor 1248 sediments amended with each of the six HACs, the extent of dechlorination was not enhanced by amendment with HACs. The dechlorination patterns in the HAC-amended sediments were nearly identical to that of the HAC-free sediments except the 3-chloro-L-tyrosine-amended ones where no dechlorination activity was observed. When these sediment cultures were transferred into fresh sediments with the same HACs, the dechlorination specificities remained the same as those of the initial inoculations. Thus, in the present study, the substrate range of the highly selected enrichment culture could not be broadened by the HACs. It appears that HACs affect PCB dechlorination mainly through population selection rather than enzyme induction of single population.

• Journal of Microbiology
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• 제39권3호
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• pp.195-201
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• 2001

The effect of moisture content an the reductive dechlorination of polychlorinated biphenyls and population dynamics of dechlorinating microorganisms was investigated in sediments spiked with Aroclor 1248. In sediment slurry with an overlying water layer, dechlorination ensued after a 4-week lag period and reduced the average number of chlorines per biphenyl from 3.91 to 3.15 after 48 weeks. In the sediments of reduced moisture content, however, dechlorination occurred after a lag period of 12 weeks and decreased the average number of chlorines per biphenyl to only 3.62, and the dechlorination rate was also slower. When the population size of dechlorinators, methanogens, and sulfate-reducing bacteria was determined by the most probable number techniques, however, no difference was found between the slurry and the low-moisture sediments, except for methanogens. The growth of dechlorinating populations coincided with the end of the lag period and they then increased by 3 orders of magnitude in two conditions. Specific growth rate of dechlorinators showed little difference between the slurry and the low-moisture sediments; however, growth yield was high in the sediments of reduced moisture content. The reduction of sediment moisture decreased the dechlorination rate and extent of PCBs but did not inhibit the growth of PCB dechlorinators.