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Çѱ¹ÇÏõȣ¼öÇÐȸ / v.37, no.2, 2004³â, pp.180-192
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( Seasonal Variation of Water Quality in a Shallow Eutrophic Reservoir ) |
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| º» ¿¬±¸´Â 2002³â 11¿ùºÎÅÍ 2004³â 2¿ù±îÁö ¼ö½ÉÀÌ ¾èÀº ºÎ¿µ¾ç»óÅÂÀÇ Àú¼öÁö¿¡¼°èÀý¿¡ µû¸¥ ¼öÁúº¯È¿ÍÀÌ¿¡ ´ëÇÑ À¯ÀÔ ºÎÇÏ·® ¿µÇâÀ» Æò°¡Çϱâ À§ÇØ ÀÌ·ç¾îÁ³´Ù. ¼ö½É°£ÀÇ ¼ö¿ÂÂ÷°¡ $1^{circ}C;m^{-1}$ ÀÌ»óÀÇ ¼ö¿Â¾àÃþÀÌ 5¿ù¿¡ Çü¼ºµÇ¾ú°í, ½ÉÃþ¿¡¼ 2 mg $O_2;L^{-1}$ ÀÌÇÏÀÇ ³·Àº »ê¼Ò³óµµ°¡ 5¿ùºÎÅÍ 9¿ù±îÁö °üÂûµÇ¾ú´Ù. $Z_{eu}/Z_{m}$Àº 0.2${sim}$l.1ÀÇ ¹üÀ§·Î ¼ö¿Â¾àÃþ Çü¼ºÀ¸·Î È¥ÇÕ ÃþÀÌ ¼ö½É 4m±ÙóÀ̰í À¯±¤´ë ÃþÀÌ ¼ö½É 4.3m¿´´ø 5¿ùÀ» Á¦¿ÜÇϰí´Â ´ëºÎºÐÀÇ ±â°£ µ¿¾È¿¡ À¯±¤´ëÃþ¿¡ ºñÇØ È¥ÇÕÃþÀÇ ¼ö½ÉÀÌ ±íÀº °ÍÀ¸·Î ³ªÅ¸³µ´Ù. ¼öü³» Áú¼Ò´Â 1.1 ${sim}$ 4.5 mg N $L^{-1}$ ÀǹüÀ§·Î, ´ëºÎºÐÀÌ ¿ëÁ¸ ÇüÅÂ(Avg. 58.7%)·Î Á¸ÀçÇϰí ÀÖ¾úÀ¸¸ç °áºùµÈ ¼öÇ¥¸éÀÇ ÇØºù ½Ã¿¡ ¾Ï¸ð´Ï¾Æ¼º Áú¼Ò¿Í Áú»ê¼ºÁú¼Ò°¡ Áõ°¡ÇÏ¿´´Ù. Àú¼öÁö³» ÃÑÀÎ ³óµµ´Â43.g${sim}$126.6 ${mu}g;P;L^{-1}$¹üÀ§·Î ´ëºÎºÐÀº ÀÔÀÚ¼ºÀÎÀÇ ÇüÅÂ(Avg. 80%)·Î Á¸ÀçÇϰí ÀÖ¾ú´Ù. ¿ëÁ¸¹«±âÀÎ ³óµµ´Â ½ÉÃþ¿¡¼ÀÇ ÀϽÃÀûÀÎ Áõ°¡°¡ °üÂûµÈ 7¿ù°ú 8¿ùÀ» Á¦¿ÜÇϰí´Â 10 ${mu}g;P;L^{-1}$ ÀÌÇÏ¿´´Ù. ¿±·Ï¼Ò a ³óµµÀÇ ¶Ñ·ÇÇÑ Áõ°¡´ÂÀÎ À¯ÀÔºÎÇÏ·®ÀÌ ¸¹¾Ò´ø 7¿ù (99 ${mu}g;L^{-1}$)°ú 11¿ù (109 ${mu}g;L^{-1}$)¿¡ °üÂûµÇ¾ú°í ¼öü³» ÃÑÀΰú ¾çÀÇ »ó°ü¼ºÀ» º¸¿´´Ù(r=0.55, P<0.008, n=22).¼öÃþ°£ÀÇ Æò±Õ ¿±·Ï¼Ò a ³óµµ´Â11¿ù 8ÀÏ¿¡ 84.5${pm}$29.0 ${mu}g;L^{-1}$À¸·Î °¡Àå ³ô¾Ò°í 2¿ù¿¡13.5${pm}$ 1.0 ${mu}g;L^{-1}$·Î °¡Àå ³·¾Ò´Ù. À¯ÀÔ¼ö·®ÀÌ Áõ°¡ÇÒ ¼ö·ÏÀ¯ÀÔ¼ö³» ÃþÀÎ ³óµµµµ Áõ°¡ÇÏ´Â °æÇâÀ» ³ªÅ¸³ÂÀ¸¸ç(r=0.69,P<0.001), 1³â Áß °¿ì·®ÀÌ ¸¹¾Ò´ø 7¿ù 25ÀÏ ÇϷ絿¾È¿¡ ¿¬°£ ÃÑÀÎ À¯ÀÔºÎÇÏ·®ÀÇ 40.5%°¡ À¯ÀԵǾú°í, 11¿ù 8ÀÏ¿¡µµ 17.1%°¡ À¯ÀԵǾú´Ù. À¯¿ªÀ¸·ÎºÎÅÍ À¯ÀԵǴÂÃÑÀÎ ºÎÇÏ·®Àº 159.0kg P $yr^{-1}$¿´°í, ½Ä¹°Çöûũſ¿¡ ÀÇÇØÁ÷Á¢ ÀÌ¿ë µÉ ¼ö ÀÖ´Â ¿ëÁ¸¹«±âÀÎ ºÎÇÏ·®Àº 126.3 kg P $yr^{-1}$·Î ÃÑÀÎÀÇ 77.7%¿¡ ÇØ´çÇÏ¿´´Ù. ÃÑ Áú¼Ò ºÎÇÏ·®Àº 5.0 ton $yr^{-1}$·Î ÃÑ ÀÎ ºÎÇÏ·®(159.0 kg P $yr^{-1}$)¿¡ ºñÇØ 30¹è Á¤µµ ¸¹¾ÒÀ¸¸ç, ÃÑÁú¼Ò ºÎÇÏ Áß ¹«±âÁú¼Ò ºÎÇÏ·®Àº3.9 ton $yr^{-1}$·Î ÃÑ Áú¼ÒÀÇ 78%¿´´Ù. ÀÎ ÀÓ°è ºÎÇÏ·®Àº 1.6 g ${cdot}$ $m^{-2}$${cdot}$$yr^{-1}$À¸·Î °úÀ×ÀÓ°èºÎÇÏ·®À» »óȸÇÏ´Â ¼öÁØ ÀÌ¿´´Ù. º» ¿¬±¸°á°ú Àú¼öÁöÀÇ À¯¿ªÀ¸·ÎºÎÅÍ À¯ÀԵǴ ¸¹Àº¾çÀÇ À¯ÀÔ ÀÎ ºÎÇÏ´Â Àú¼öÁö ¼öÁúÀÇ °èÀýÀûÀÎ º¯È »Ó ¸¸¾Æ´Ï¶ó ºÎ¿µ¾çÈÀÇ °¡Àå Å« ¿øÀÎÀ¸·Î ³ªÅ¸³µÀ¸¸ç, Áß¿µ¾ç»óÅÂÀÇ ¼öÁúÀ» À¯ÁöÇϱâ À§Çؼ´Â ÃÑÀÎ À¯ÀÔºÎÇÏ·®(159 kg $yr^{-1}$)ÀÇ 71%°¡ °¨¼ÒµÇ¾î¾ß ÇÒ Çʿ伺ÀÌ Á¦±âµÇ¾ú´Ù. ¶ÇÇÑ ¿©¸§Ã¶ ½ÉÃþ »ê¼Ò °í°¥ÀÌ ¾ß±âµÇ¾ú°í, ÀÌ ½Ã±â¿¡ ÅðÀû¹°·Î ¿ëÃâµÈ ÀÎÀÌ ½Ä¹°Çöûũſ ¼ºÀå¿¡ ÀÌ¿ëµÉ ¼ö Àֱ⶧¹®¿¡ ÅðÀû¹°¿¡ ´ëÇÑ °ü¸®µµ ¼öÇàµÉ Çʿ䰡 ÀÖ´Ù. |
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| This study was carried out to assess the seasonal variation of water quality and the effect of pollutant loading from watershed in a shallow eutrophic reservoir (Shingu reservoir) from November 2002 to February 2004, Stable thermocline which was greater than $1^{circ}C$ per meter of the water depth formed in May, and low DO concentration (< 2 mg $O_2;L^{-1}$) was observed in the hypolimnion from May to September, 2003. The ratio of euphotic depth to mixing depth ($Z_{eu}/Z_{m}$) ranged 0.2 ${sim}$ 1.1, and the depth of the mixed layer exceeded that of the photic layer during study period, except for May when $Z_{eu}$ and $Z_{m}$ were 4 and 4.3 m, respectively. Most of total nitrogen, ranged 1.1 ${sim}$ 4.5 ${mu}g;N;L^{-1}$, accounted for inorganic nitrogen (Avg, 58.7%), and sharp increase of $NH_3$-N Hand $NO_3$-N was evident during the spring season. TP concentration in the water column ranged 43.9 ${sim}$ 126.5 ${mu}g;P;L^{-1}$, and the most of TP in the water column accounted for POP (Avg. 80%). During the study period, DIP concentration in the water column was &;lt 10 ${mu}g;P;L^{-1}$ except for July and August when DIP concentration in the hypolimnion was 22.3 and 56.7 ${mu}g;P;L^{-1}$, respectively. Increase of Chl. a concentration observed in July (99 ${mu}g;L^{-1}$) and November 2003 (109 ${mu}g;L^{-1}$) when P loading through two inflows was high, and showed close relationship with TP concentration (r = 0.55, P< 0.008, n = 22). Mean Chl. a concentration ranged from 13.5 to 84.5 mg $L^{-1}$ in the water column, and the lowest and highest concentration was observed in February 2004 (13.5 ${pm}$ 1.0 ${mu}g;L^{-1}$) and November 2003 (84.5 ${pm}$29.0 ${mu}g;L^{-1}$), respectively. TP concentration in inflow water increased with discharge (r = 0.69, P< 0.001), 40.5% of annual total P loading introduced in 25 July when there was heavy rainfall. Annual total P loading from watershed was 159.0 kg P $yr^{-1}$, and that of DIP loading was 126.3 kg P $yr^{-1}$ (77.7% of TP loading. The loading of TN (5.0ton yr-1) was 30 times higher than that of TP loading (159.0 kg P yr-1), and the 78% of TN was in the form of non-organic nitrogen, 3.9 ton $yr^{-1}$ in mass. P loading in Shingu reservoir was 1.6 g ${cdot}$ $m^{-2}$ ${cdot}$ $yr^{-1}$, which passed the excessive critical loading of Vollenweider-OECD critical loading model. The results of this study indicated that P loading from watershed was the major factor to cause eutrophication and temporal variation of water quality in Shingu reservoir Decrease by 71% in TP loading (159 kg $yr^{-1}$) is necessary for the improvement of mesotrophic level. The management of sediment where tine anaerobic condition was evident in summer, thus, the possibility of P release that can be utilized by existing algae, may also be considered. |
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| Ű¿öµå |
| shallow eutrophic reservoir;water quality;seasonal variation;$Z_{eu}/Z_{m}$;P loading;sediment; |
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Çѱ¹ÇÏõȣ¼öÇÐȸÁö / v.37, no.2, 2004³â, pp.180-192
Çѱ¹ÇÏõȣ¼öÇÐȸ
ISSN : 1976-8087
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200418317182827)
¾ð¾î : Çѱ¹¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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