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Çѱ¹È¯°æ»ý¹°ÇÐȸ / v.17, no.4, 1999³â, pp.529-541
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´ëûȣ¿¡¼ ¼öȯ°æ ¿äÀΰú ½Ä¹°ÇöûũſÀÇ º¯µ¿
( Dynamics of Water Environmental Factors and Phytoplankton in Taechong Reservoir ) |
| ½ÅÀç±â;Á¶°æÁ¦;¿ÀÀÎÇý; Çѱ¹¼öÀÚ¿ø°ø»ç ¼öÀÚ¿ø¿¬±¸¼Ò;ÀÎÁ¦´ëÇб³ ȯ°æ½Ã½ºÅÛÇкÎ;¹èÀç´ëÇб³ »ý¸í°úÇкÎ;
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| ´ëûȣÀÇ Áß.ÇÏ·ù ÁÖ¿äÁöÁ¡¿¡¼ ¼öÁúƯ¼ºÀ» ÆÄ¾ÇÇϱâ À§ÇÏ¿© ȯ°æ¿äÀΰú ½Ä¹°ÇöûũſÀÇ º¯µ¿À» 98³â 6¿ùºÎÅÍ 99³â 6¿ù±îÁö ¸Å¿ù Á¶»çÇÏ¿´´Ù. ȯ°æ¿äÀÎ Áß ¼ö¿Â, DO¹× pH´Â °¢°¢ 5.3~27.7$^{circ}C$, 6.2~13.8 mgO$_2$/1 ¹× 6.4~9.5 ¹üÀ§·Î¼ °èÀýÀû ¿µÇâÀÌ ÄÇ´Ù. ¹«±â¿µ¾ç¿° Áß NH$_4$, NO$_3$, SRP ¹× SRSi ³óµµ´Â °¢°¢ 18~104 $mu$g N/1, 79~1,111 $mu$g N/1, 0~16 $mu$g P/1 ¹× 0~3.0 mg Si/l ¹üÀ§¿´´Ù. ¹«±âÁú¼Ò Áß NH$_4$ ´Â NO$_3$ÀÇ 5.5~7.2%¼öÁØÀ̾ú´Ù. NO$_3$´Â Çϰ迡¸¸ ´Ù¼Ò ³·¾Ò°í ´Ù¸¥ ½Ã±â¿¡´Â °ÅÀÇ ÀÏÁ¤ÇÏ¿´´Ù. SRP¿Í SRSi³óµµ´Â ³²Á¶·ù°¡ ¿ìÁ¡ÇÏ´Â Çϰ迡 Áõ°¡ÇÏ¿´°í ¼ö¿ÂÀÌ °¨¼ÒµÈ 10¿ù ÀÌÈÄ¿¡ ±ÔÁ¶·ùÀÇ Áõ°¡¿Í ÇÔ²² SRP¿Í SRSi³óµµ°¡ °¨¼ÒÇÏ¿´´Ù. µû¶ó¼ SRSi´Â SRP¿Í ´õºÒ¾î Á¶·ù »ýÀå¿¡ ¹ÐÁ¢ÇÑ °ü·Ã¼ºÀÌ ÀÖ´Â ¿µ¾ç¿°À¸·Î Æò°¡µÇ¾ú´Ù. Chl-$alpha$ Æò±Õ³óµµ´Â 8~12 $mu$g/1 ¹üÀ§·Î¼ ÇÏ·ù(´ï)¿¡¼ °¡Àå ³·¾Ò´Ù. ¶ÇÇÑ ÇÏÀý±â¿¡ TN/TPºñ°¡ °¨¼ÒÇÒ¼ö·Ï chi-$alpha$ ³óµµ´Â Áõ°¡ÇÏ¿´°í TN/TPºñÀÇ Æò±Õ°ªÀº 110À¸·Î¼ Á¶·ùÀÇ »ýÀå¿¡ ´ëÇØ P Á¦ÇѼºÀÌ °ÇÏ¿´´Ù. ½Ä¹°ÇöûũſÀÇ º¯µ¿Àº °èÀý¿¡ µû¶ó ¼Ò¼öÁ¾ÀÌ ¿ìÁ¡Çϴ Ư¼ºÀÌ °üÂûµÇ¾ú´Ù. Çϰ迡´Â ³²Á¶·ù Anabaena, Microcystis ¹× Oscillatoria¼Ó Á¶·ù°¡ ÁÖ·Î ÃÊ¿©¸§ºÎÅÍ ´Ê°¡À»±îÁö ¹ß»ýÇÏ¿© ¹ø¹«ÇÏ¿´´Ù. ÀÌ Áß¿¡¼ A. spiroides v. crassa´Â 0.3~2.0$ imes$$10^4$cells/ml, M. aeruginosa´Â 6.4$ imes$$10^2$~1.0$ imes$$10^4$cells/m1 ¹× O. limosu´Â 4.6$ imes$$10^3$~1.6$ imes$$10^4$ cells/ml ¹üÀ§·Î¼ º¯È ÆøÀÌ °¡Àå ÄÇ´Ù. ¹Ý¸é µ¿°è¿¡´Â ±ÔÁ¶·ù Stephanodiscus¼Ó Á¶·ù°¡ 11¿ù~4¿ù¿¡ Æò±Õ 4.9$ imes$$10^2$cells/m1¼öÁØÀ̾ú°í 1¿ù¿¡ Æò±Õ ¼¼Æ÷¼ö°¡ 1.3$ imes$$10^3$ cells/ml·Î ¸¹¾Æ Áß¿äÁ¾À¸·Î º¼ ¼ö ÀÖ¾ú´Ù. |
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| In order to elucidate characteristics of water quality, investigation of monthly dynamics of environmental factors and algal populations at major four stations of the mid and lower part in Taechong Reservoir was performed from June 1998 to June 1999. Water temperature, DO and pH were ranged 5.3~27.7$^{circ}C$, 6.2~13.8 mgO$_2$/1 and 6.4~9.5, respectively. Those were varying as the season changes. Among inorganic nitrogen nutrients, NH$_4$was ranged from 5.5% to 7.2% of NO$_3$and NO$_3$was almost same through the seasons except summer in which it was low. SRP and SRSi were increased in summer when the blue-green algae became dominant. Those were decreased as the cell density of diatom increased when the water temperature dropped. Therefore SRSi was considered to be another important nutrient factor contributing to the increment of biomass of freshwater algae as well as SRP. Average chi-$alpha$ concentration ranged from s to 12 $mu$g/1 and in the lower part or the reservoir, the lowest was found. Moreover, there were remarkable increment in summer when TN/TP ratio were decreasing from relationships between TN/TP ratio and chi-$alpha$ concentration. Annual mean ratio of TN/TP ratio was relatively high as the value was 110, which was relatively high, and it showed that P is the dominant factor in the algal growth. The dynamics of phytoplankton were simply dominated by a few species seasonally. In summer, blue -green algae such as Anabaena, Microcystis and Oscillatoria were dominant and algal bloom of blue -green began from early summer, sustained to late autumn. The average standing crops of A. spiroides v. crassa, M. aeruginosa and O. limosa were ranged 0.3~2.0$ imes$10$^4$cells/ml, 6.4$ imes$10$^2$~1.0$ imes$10$^4$cells/ml and 4.6$ imes$10$^3$~1.6$ imes$10$^4$cells/ml, respectively. In winter, diatom Stephanodiscus was considered to be an important species whose average standing crops of Stephunodiscus was 4.9$ imes$10$^2$cells/ml from November to April of the next year and the highest was 1.3$ imes$10$^3$cells/ml in January. |
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| Ű¿öµå |
| Taechong Reservoir;Inorganic nutrient;Phytoplankton;Anabaena;Microcystis;Stephanodiscus; |
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ȯ°æ»ý¹° / v.17, no.4, 1999³â, pp.529-541
Çѱ¹È¯°æ»ý¹°ÇÐȸ
ISSN : 1226-9999
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO199911921495129)
¾ð¾î : Çѱ¹¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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