본 연구에서는 다슬기 중의 자연균총의 정량적 오염도 분석과 해감 제거 공정(지하수, 상수)에 따른 저감화 효과를 조사하였다. 다슬기 중의 일반세균, 대장균군과 대장균, 진균 및 황색포도상구균의 정량적 검출을 위해 표준평판법을 사용하여 각각 plate count agar (PCA), potato dextrose agar (PDA), 대장균군/대장균용 3M Petrifilm 및 황색포도상구균용 3M Petrifilm에 도말하여 집락을 계수하였다. 지하수와 상수 처리에 따른 이들 균의 저감화 정도 역시 동일한 방법으로 수행되었다. 다슬기 원료 중의 미생물 오염도 분석시, 일반세균, 대장균군 및 진균은 각 각 6.40, 2.70 및 6.79 log10CFU/g로 조사되었다. 대장균과 황색포도상구균은 검출되지 않았다 (검출 한계: < 1 log10CFU/g). 그러나, 지하수로 해감 제거한 다슬기의 경우, 분석된 모든 미생물의 정량적 오염도가 원료 다슬기 에 비해 높게 검출되었다. 특히 원료 다슬기에서 불검출 이었던 대장균도 2.46 log10CFU/g 검출되었다. 상수로 해감 제거한 다슬기의 일반세균은 유의적으로 저감화 되지 않았으며(p<0.05), 대장균군은 유의적으로 증가하는 경향을 나타내었다(p>0.05). 진균만이 약간의 저감화(0.2 log 이하)를 유의적으로 보였다(p>0.05). 본 연구결과 지하수와 상수를 이용해서 해감 제거하는 공정만으로는 다슬기의 미생물학적 안전성을 확보하기 곤란한 것으로 판단된다.

Chromated Copper Arsenate (CCA)-treated wood has been widely used in Korea since 1980s, but the release of chromium, copper, and arsenic from the wood has been reported to cause environmental contamination. This study was aimed at investigating the environmental impact of brook water and sediment from the construction of cylindrical wood piles around a brook (partially immersed in the water) and wood bridge structures over the brook. Ten water and ten composite sediment samples (including one control for each) were collected from sites where a large number of treated wood structures were installed. Samples were analyzed for total chromium, copper, and arsenic using atomic absorption spectroscopy. Water contamination was not observed in all samples, but metal concentrations in the sediment samples were elevated at most sites, indicating the accumulation of metals in the sediment. This study suggested that the use of CCA-treated wood by continuos contact with water can lead to marked leaching of metal components and may ultimately cause health effects on aquatic organisms living on or in the sediment.

Sediment works as a resource for electric cells. This paper was designed in order to verify how sediment cells work with anodic material such as metal and carbon fiber. As known quite well, sediment under sea, rivers or streams provides a furbished environment for generating electrons via some electron transfer mechanism within specific microbial population or corrosive oxidation on the metal surfaces in the presence of oxygen or water molecules. We experimented with one type of sediment cell using different anodic material so as to attain prolonged, maximum electric power. Iron, Zinc, aluminum, copper, zinc/copper, and graphite felt were tested for anodes. Also, combined type of anodes-metal embedded in the graphite fiber matrix-was experimented for better performances. The results show that the combined type of anodes exhibited sustainable electricity production for ca. 600 h with max. 0.57 W/㎡ Al/Graphite. Meanwhile, graphite-only electrodes produced max. 0.11 W/㎡ along with quite stationary electric output, and for a zinc electrode, in which the electricity generated was not stable with time, therefore resulting in relatively sharp drop in that after 100 h or so, the maximum power density was 0.64 W/㎡. It was observed that the corrosive reaction rates in the metal electrodes might be varied, so that strength and stability in the electric performances(voltage and current density) could be affected by them. In addition to that, COD(chemical oxygen demand) of the sediment of the cell system was reduced by 17.5∼36.7% in 600 h, which implied that the organic matter in the sediment would be partially converted into non-COD substances, that is, would suggest a way for decontamination of the aged, anaerobic sediment as well. The pH reduction for all electrodes could be a sign of organic acid production due to complicated chemical changes in the sediment.