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Çѱ¹ÇÏõȣ¼öÇÐȸ / v.35, no.1, 2002³â, pp.1-9
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ÆÈ´çÈ£ÀÇ »ýÅÂÇÐÀû ¿¬±¸ 4. °æ¾Èõ ÇÏ·ùÀÇ ¿µ¾ç¿° ¹× ÀÔÀÚÅ À¯±â¹° °Åµ¿°ú ½Ä¹°ÇöûũſÀÇ ÃµÀÌ
( Ecological Studies on Pal'tang River-Reservoir System in Korea. 4. Dynamics on Inorganic nutrients, POM and Phytoplankton Succession in the Lower Stream Kyungan ) |
| È«¼º¼ö;¾îÀ±¿;ÇѸí¼ö; ¹°È¯°æ»ýź¹¿ø ±¹°¡ÁöÁöÁ¤¿¬±¸½Ç, ÇѾç´ëÇб³ ȯ°æ°úÇаú;ÇѾç´ëÇб³ »ý¸í°úÇаú, ±¤µ¿ÁßÇб³;ÇѾç´ëÇб³ »ý¸í°úÇаú, ¹°È¯°æ»ýź¹¿ø ±¹°¡ÁöÁöÁ¤¿¬±¸½Ç, ÇѾç´ëÇб³ ȯ°æ°úÇаú;
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| ÆÈ´çÈ£ Áö·ùÀÎ °æ¾ÈõÀÇ ÀÔÀÚÅ ¹× ¹«±â ¿µ¾ç¿°ÀÇ µ¿ÅÂ¿Í À̵éÀÌ ½Ä¹°ÇöûũſÀÇ ±ºÁý±¸Á¶ÀÇ ÃµÀÌ¿¡ ¹ÌÄ¡´Â ¿µÇâÀ» ±Ô¸íÇϱâ À§ÇÏ¿© 1993³â 8¿ù 18ÀϺÎÅÍ 11¿ù 13ÀϱîÁö ÁÖ 1ȸÀÇ Á¶»ç¸¦ 14ÁÖ µ¿¾È¿¡ °ÉÃļ ¼öÇàÇÏ¿´´Ù. Áú»ê¼º Áú»ê¿°Àº Á¶»ç±â°£ Áß Ç×»ó dzºÎÇÏ¿´°í Àλ꿰°ú ±Ô»ê¿°Àº °¥¼ö±â¿¡ ±Þ°ÝÈ÷ °¨¼ÒÇÏ´Â °æÇâÀ» º¸¿´´Ù. Chlorophyll aÀÇ °ªÀº 1993³â 8¿ù 21ÀÏ $90.6;{mu}g/l$·Î ÃÖ´ë °ªÀÌ °üÂûµÇ¾úÀ¸¸ç 10¿ù Áß¼ø ÀÌÈĺÎÅÍ´Â $15{sim}16;{mu}g/l$À» À¯ÁöÇÏ¿´´Ù. ÀÔÀÚÅ À¯±âź¼Ò¿Í ÀÔÀÚÅ¡¡À¯±âÁú¼Ò´Â ¸Å¿ì dzºÎÇѵ¥ ºñÇØ, ÀÔÀÚÅ À¯±âÀÎÀÇ ³óµµ´Â ÃÖÀú$0.3;{mu}g; atm/l$ÀÇ ³·Àº ´Éµµ ºÐÆ÷¸¦ º¸¿´À¸¸ç, ÀÔÀÚÅ À¯±âź¼Ò ¹× À¯±âÁú¼ÒÀÇ º¯È¾ç»óÀº chlorophyll aÀÇ º¯Â÷¾ç»ó°ú Àß ÀÏÄ¡ÇÏ¿´À¸¸ç, À̰ÍÀº ÀÔÀÚÅ À¯±âź¼Ò ¹× Áú¼Ò´Â ½Ä¹°ÇöûũſÀÇ ¼ºÀå¿¡ ÀÇÇÑ ³»»ýÀû °ø±Þ¿¡ ÀÇÇÔÀ» ÀǹÌÇÑ´Ù. À̿ʹ ¹Ý´ë·Î °æ¾ÈõÀÇ ÀÎÀÇ °ø±ÞÀº ¿ÜºÎ·ÎºÎÅÍ °ø±ÞµÇ°í ÀÖÀ¸¸ç, Ç×»ó Àλ꿰ÀÌ ½Ä¹°ÇöûũſÀÇ Á¦ÇÑÀÎÀÚ·Î ÀÛ¿ëÇÏÁö¸¸, ¶§¶§·Î ³·Àº Si/P ratioÀ» ³ªÅ¸³»¾î ±Ô»ê¿°ÀÇ °í°¥ Çö»óÀÌ °üÂûµÇ¾ú´Ù. ÀÌ °á°ú´Â ¶§·Î´Â ½Ä¹°ÇöûũſÀÇ ¼ºÀå¿¡ Àλ꿰 º¸´Ù´Â ±Ô»ê¿°ÀÌ Á¦ÇÑ ÀÎÀÚ·Î ÀÛ¿ëÇÑ´Ù´Â °ÍÀ» ¾Ï½ÃÇÑ´Ù. Àλ꿰ÀÌ Á¦ÇÑ ÀÎÀÚ·Î ÀÛ¿ëÇÏ´Â ½Ã±â¿¡´Â ±ÔÁ¶·ù°¡ ¿ìÁ¡Çϰí ÀÖ¾úÀ¸¸ç, ±Ô»ê¿°ÀÌ Á¦ÇÑÀÎÀÚ·Î ÀÛ¿ëÇÏ´Â ½Ã±â (9¿ù $11{sim}18$ÀÏ, 10¿ù $2{sim}16$ÀÏ)¿¡´Â¡¡³²Á¶·ù¿Í ³ìÁ¶·ù°¡ ¿ìÁ¡ ÇÏ¿´´Ù. ƯÈ÷,¡¡³²Á¶·ù Áß¿¡¼ Anabaena, Microcystis¹× Oscillatoria°¡¡¡¿ìÁ¡Á¾À¸·Î ÃâÇöÇÏ¿´´Ù.¿¡¼ $90;{mu}S/cm$Á¤µµ±îÁö °¨¼ÒÇÏ¿© Ç¥Ãþº¸´Ù ³·Àº °ªÀ» º¸¿´´Ù. ±×·¯³ª,´ÊÀº °¡À»ºÎÅÍ Ãʺ½±îÁöÀÇ Àü±âÀüµµµµ´Â ¾à $10^{circ}Cm$±íÀ̱îÁö Ç¥ÃþÀÌ ½ÉÃþº¸´Ù ³·°Ô °üÂûµÇ¾ú´Ù. ¼Ò¾çÈ£ÀÇ Ã¼·ù½Ã°£Àº Æò±Õ 245ÀÏ·Î, ÆÈ´çÈ£ÀÇ Æò±Õ 5.1Àϰú Å« Â÷À̸¦ º¸¿´À¸³ª, ÆÈ´çÈ£´Â ¼Ò¾çÈ£º¸´Ù Ŭ·Î·ÎÇÊ 3³óµµ´Â ¾à 2.7¹è, ÃÑ Áú¼Ò ³óµµ´Â ¾à 1.2¹è ±×¸®°í ÃÑ ÀÎ ³óµµ´Â ¾à 2.6¹è ³ô¾Ò´Ù. µû¶ó¼ ¿µ¾ç¿°·ù ³óµµ°¡ ü·ù½Ã°£º¸´Ù Á¶·ùÁõ½Ä¿¡ ´õ ±â¿©ÇÑ °ÍÀ¸·Î ÆÇ´ÜµÈ´Ù..21}{ imes}(DA/SA)^{-0.50}$À̸ç $R^2$°¡ 61%ÀÇ ¼³¸í·ÂÀ» ³ªÅ¸³»¾î ³ó¾÷¿ë Àú¼öÁöÀÇ ÀÎ ³óµµ °æÇâÀ» ¿¹ÃøÇϴµ¥ »ç¿ë °¡´ÉÇÒ¡¡°ÍÀ¸·Î »ý°¢µÈ´Ù. ÀÌ»óÀÇ °á°ú·Î¼ ¿ì¸® ³ª¶ó ³ó¾÷¿ë Àú¼öÁöÀÇ ¼öÁú¿¹Ãø¿¡ ÀÖ¾î´Â º¹ÀâÇÑ À¯Ãâ¸ðÇüÀ̳ª À¯¿ª¸ðÇü, È£¼Ò¼öÁú¸ðÇü µîÀ» »ç¿ëÇϱ⺸´Ù´Â º» ¿¬±¸¿¡¼¿Í¡¡°°ÀÌ ±âÁ¸ÀڷḦ ºÐ¼®ÇÏ¿© µµÃâÇÑ °æÇèÀû °ü°è½ÄÀ» »ç¿ëÇÏ¸é ºñ±³Àû ÀûÀº ³ë·ÂÀ¸·Îµµ »ó´çÈ÷ ½Å·Ú¼ºÀÖ°Ô ¿¹ÃøÇÏ¿© ¼öÁú°ü¸®¿¡ µµ¿òÀÌ µÉ ¼ö ÀÖÀ» °ÍÀ¸·Î ÆÇ´ÜµÈ´Ù.°¡ Á¤ÈÈ¿À²°úÀÇ »ó°ü°ü°èº¸´Ù Á»´õ À¯ÀǼº ÀÖ°Ô ³ªÅ¸³µ´Ù. À̰ÍÀº ³ôÀº ¼ö¸®ÇÐÀû ºÎÇÏÁ¶°ÇÀÌ ¿µ¾ç¿°·ù µîÀÇ Á¤ÈÈ¿À²¿¡´Â Å©°Ô ¿µÇâÀ» ¹ÌÄ¡Áö ¾ÊÀ½À» º¸¿©ÁÖ°í ÀÖÀ¸¸ç, µû¶ó¼ ºñ±³Àû ³·Àº ³óµµÀÇ ¿µ¾ç¿°·ù¸¦ °¡Áö°í ÀÖ°í, ¸¹Àº 󸮼ö·®À» ¿ä±¸ÇÏ´Â ºÎ¿µ¾çÈµÈ Àú¼öÁöÀÇ ¼öÁú°³¼±À» À§Çؼ´Â ³ôÀº ¼ö¸®ÇÐÀû ºÎÇÏÁ¶°Ç¿¡¼ ½Ã°£´ç Á¤È·®À» ´Ã¸®´Â °ü¸®¹æ¹ýÀÌ °æÁ¦ÀûÀ̸ç, ÀÌ¿¡ ÃÊÁ¡À» ¸ÂÃß¾î ³ª°¡¾ß ÇÒ °ÍÀ¸·Î »ç·áµÈ´Ù.µµ·Î °ËÃâµÇ¾î À̸¦ °í·ÁÇÑÁ¤¼ö°øÁ¤ÀÇ °ü¸®°¡ ÇÊ¿äÇϸ®¶ó »ý°¢µÈ´Ù.$yr^{-1}$)ÀÇ 71%°¡ °¨¼ÒµÇ¾î¾ß ÇÒ Çʿ伺ÀÌ Á¦±âµÇ¾ú´Ù. ¶ÇÇÑ ¿©¸§Ã¶ ½ÉÃþ »ê¼Ò °í°¥ÀÌ ¾ß±âµÇ¾ú |
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| In order to understand the relationship between succession of phytoplankton community structure and inorganic nutrients and particulate organic matters, a one station in Kyungan stream in Korea during the dry season was chosen. Water samplings were carried out once a week from 18 August to 13 November 1993. The DIN concentration distributed always abundantly, however, phosphate and silicate gradually reduced during the period. Phytoplankton community had a peak chlorophyll a concentration of $90.6;{mu}g/l$ in late summer (21 August 1993) and a second peak of $29.7;{mu}g/l$ in autumn (2 October 1993). After then late autumn was characterined by relatively low chlorophyll a concentration of $15{sim}16;{mu}g/l$. Seasonal fluctuation of chlorophyll a concentrations were correlated with measured POC and PON concentrations: phytoplankton blooming may be a major factor controlling POC and PON concentrations in this ecosystem. Phosphate plays an most important role as a limiting factor of phytoplankton growth. However, when Si/P ratio low, silicate may be a more critical limiting factor than phosphate. Shifts of P-limitation to Si- limitation the succession of dominant phytoplankton can in duce: diatom to cyanobacteria such as Anabaena, Microcystis and Oscillatoria. |
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| Ű¿öµå |
| Pal'tang river-reservoir system;Inorganic nutrients;POM;DIN/P ratio;Si/P ratio;Phytoplankton succession; |
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Çѱ¹ÇÏõȣ¼öÇÐȸÁö / v.35, no.1, 2002³â, pp.1-9
Çѱ¹ÇÏõȣ¼öÇÐȸ
ISSN : 1976-8087
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200218317179118)
¾ð¾î : Çѱ¹¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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