주암호 홍수조절용지내 침수 식물체의 영양염류 제거속도 및 용출속도
Removal and Release Velocities of Nutrients by Submerged Plants in Flood Control Reservoirs around Juam Lake
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본 연구는 주암호 홍수조절용지내에 서식하는 침수식물체들의 영양염류 용출이 주암호 수질에 미치는 영향을 조사하고자 침수상태의 수질, 토양 및 식물체를 자연상태 그대로 column으로 옮겨와 침수기간별 영양염류의 제거속도 및 용출속도를 조사하였고, 이들 결과를 토대로 각 홍수조절용지에서 침수식물체별 영양염류 용출량을 산출하였다. COD 제거속도 상수(K, day^(-1))는 이삭사초의 경우 침수 0~4 day, 5~19 day 및 20~33 day 구간에서 0.07~0.18, -0.23~-0.17 및 -0.28~0.03 day^(-1)이었고, 물억새의 경우 침수 0~6 day, 7~19 day 및 20~33 day 구간에서 0.14~0.22, -0.19~-0.04 및 -0.05 day^(-1)이었다. T-N 제거속도 상수(K, day^(-1))는 이삭사초의 경우 침수 0~4(8) day 및 5(9)~33 day 구간에서 0.02 및 -0.13~-0.10 day^(-1)이었고, 물억새의 경우 침수 0~2(4) day, 3(5)~19 day 및 20~33 day 구간에서 0.01~0.04, -0.03 및 -0.18~-0.17 day^(-1)이었다. T-P 제거속도 상수(K, day^(-1))는 이삭사초의 경우 침수 0~4 day 및 5~33 day 구간에서 0.05~0.06 및 -0.14~-0.09 day^(-1)이었고, 물억새의 경우 침수 0~4 day 및 5~33 day 구간에서 0.05~0.06 및 -0.15~-0.12 day^(-1)이었다. 이상의 결과에서 침수초기에는 침수식물체가 생육하면서 영양염류를 분해 이용하여 수질을 정화하였으나, 침수식물체에 따라 다소 차이가 있었지만 침수 4~10일후부터 침수식물체가 미생물에 의해 서서히 분해되면서 영양염류가 수질내로 용출되는 경향이었다. 홍수조절용지에서 침수식물체별 영양염류 용출량은 이삭사초가 물억새에 비해 약간 많았다. 특히 site 1 에서 COD, T-N 및 T-P 용출량은 이삭사초의 경우 각각 6,719, 2,397 및 466 kg/month/area이었고, 물억새의 경우 각각 53.1, 14.8 및 3.30 kg/month/area이었다.
Abstract
BACKGROUND: Eutrophication occurs occasionally in flood control reservoirs around Juam lake in summer and early autumn. Lakeside macrophyte which is one of internal pollutants effects on water quality when it is submerged during water surface is rising after rainy season. METHODS AND RESULTS: To improve water the quality of water from water supply source and to establish the management plan of submerged plants in flood control reservoirs around Juam Lake, the removal and release velocities of nutrients by submerged plants in site 1 and 2 were investigated. Removal or release velocity constant (K) of COD by Carex dimorpholepis Steud in column was 0.07~ 0.18 day^(-1) at 0~4 days after flooding, -0.23~-0.17 day^(-1) at 5~19 days after flooding and -0.28~0.03 day^(-1) at 20~33 days after flooding. Removal or release velocity constant (K) of T-N by Carex dimorpholepis Steud was 0.02 day^(-1) at 0~4(8) days after flooding, -0.13~-0.10 day^(-1) at 5(9)~33 days after flooding in column. Removal or release velocity constant (K) of T-P by Carex dimorpholepis Steud was 0.05~0.06 day^(-1) at 0~4 days after flooding, -0.14~-0.09 day^(-1) at 5~33 days after flooding. Release velocity constant (K) of nutrients by Miscanthus sacchariflorus Benth was lower than that by Carex dimorpholepis Steud. In site 1, the amount of nutrients release by Carex dimorpholepis Steud was 6,719 kg/month/area for COD, 2,397 kg/month/area for T-N and 466 kg/month/area for T-P. The amounts of nutrients release by Carex dimorpholepis Steud were higher than those by Miscanthus sacchariflorus Benth in both sites. CONCLUSION(s): The results of this study suggest that COD, T-N and T-P in water quality of Juam lake were strongly influenced by submerged plants in flood control reservoirs.
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