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Çѱ¹È¯°æ»ý¹°ÇÐȸ / v.27, no.1, 2009³â, pp.31-39
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³ó¾÷»ýÅÂ°è ±òµû±¸ À¯ÃæÀÇ ´Ù¾ç¼º ¹× ¿ìÁ¡Á¾ ´ÕÆù±òµû±¸¸¦ ÀÌ¿ëÇÑ À¯±â¹° ºÐÇØ´É Æò°¡
( Species Diversity of Chironomid Midge and Evaluation on Removal Capacity of Organic Matter Using a Dominant Species, Chironomus nipponensis in Agroecosystem ) |
| ½ÉÇϽÄ;¹Úº´µµ;ÀÌ¿µº¸;ÃÖ¿µÃ¶;±èÁ¾±æ;¹ÚÇØÃ¶; ±¹¸³½Ä·®°úÇпø ±â´É¼ºÀÛ¹°ºÎ µÎ·ùÀ¯ÁöÀÛ¹°°ú;±¹¸³³ó¾÷°úÇпø ³ó¾÷»ý¹°ºÎ °ïÃæ»ê¾÷°ú;±¹¸³³ó¾÷°úÇпø ³ó¾÷»ý¹°ºÎ °ïÃæ»ê¾÷°ú;±¹¸³³ó¾÷°úÇпø ³ó¾÷»ý¹°ºÎ °ïÃæ»ê¾÷°ú;±¹¸³³ó¾÷°úÇпø ³ó¾÷»ý¹°ºÎ °ïÃæ»ê¾÷°ú;±¹¸³³ó¾÷°úÇпø ³ó¾÷»ý¹°ºÎ °ïÃæ»ê¾÷°ú;
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| ³ó¾÷»ýŰèÀÇ È¯°æº°·Î ±òµû±¸·ùÀÇ ºÐÆ÷¸¦ ¹àÈ÷°í ¿ìÁ¡Á¾À» ÀÌ¿ëÇÑ À¯±â¹° ºÐÇØ´ÉÀ» Æò°¡ÇϰíÀÚ ´ë´ÜÀ§°æÀÛÁö, ģȯ°æ³ó¾÷Áö, »ýȰÇϼö À¯ÀÔÁö, Ãà»êÆó¼ö À¯ÀÔÁö ¹× ÁÖº¯¼ö·Î µîÀÇ 5°³ ¼½Äóº°·Î ³ª´©¾î '04$sim$'06³â±îÁö °¢ ±¸È¹À» ´ëÇ¥ÇÏ´Â ÃÑ 78°³ ÁöÁ¡¿¡¼ ±òµû±¸°ú ¹× °ø¼ ¹«Ã´Ãßµ¿¹°À» Á¤·® äÁýÇÏ¿´´Ù. ±× °á°ú, ³ó¾÷Áö´ëÀÇ ±òµû±¸·ù´Â ÃÑ 16Á¾À¸·Î µ¿Á¤µÇ¾ú´Ù. ¼½ÄÁö À¯Çüº°·Î ÃâÇöÇÑ Á¾¼ö¸¦ º¸¸é, Ãà»êÆó¼ö À¯ÀÔÁö¿¡¼ 11Á¾, ´ë´ÜÀ§ ³ó°æÁö´Â 8Á¾, ³ó°æÁö ÁÖº¯¼ö·Î´Â 7Á¾, ģȯ°æ³ó¾÷Áö´Â 6Á¾, »ýȰÇϼö À¯ÀÔÁö´Â 2Á¾À¸·Î Á¶»çµÇ¾ú´Ù ±¸È¹º°·Î ³ªÅ¸³ ¿ìÁ¡Á¾À» º¸¸é, À¯±â¹°ÀÇ ³óµµ°¡ ³ôÀº ´ë´ÜÀ§°æÀÛÁö(A), »ýȰÇϼö À¯ÀÔÁö(C) ¹× Ãà»êÆó¼ö À¯ÀÔÁö(D)¿¡¼´Â ´ÕÆù±òµû±¸(C. nipponensis), À¯±â¹° ÇÔ·®ÀÌ ³·Àº ÁÖº¯¼ö·Î(E)¿¡¼´Â ½£¾Æ±â±òµû±¸(C. sylvestris), ģȯ°æ³ó¾÷Áö(B)¿¡¼´Â ¼»êÀåºÎ±òµû±¸(Tanytarsus sesanensis)¿´´Ù. ¼öÁú°ú ±ºÁýÁö¼ö´Â ³íÁÖº¯ÀÇ ¼ö·Î¿¡¼ ³ô¾Ò°í, ´ë´ÜÀ§ °æÀÛÁö, ģȯ°æ³ó¾÷Áö, »ýȰÇϼö À¯ÀÔÁö, Ãà»êÆó¼ö À¯ÀÔÁö´Â ³·Àº ¼öÁØÀ¸·Î Á¶»çµÇ¾ú´Ù. ÀúÁú³»¿¡¼ ´ÕÆù±òµû±¸ÀÇ À¯±â¹° Á¦°Å´É·ÂÀº ¹«Ã³¸®±¸¿Í ´ëºñÇÏ¿© 90°³Ã¼ 󸮱¸¿¡¼ 18% Áõ°¡ÇÏ¿´´Ù. |
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| To recognize the species composition and community of chironomid midge in agroecosystem and evaluate removal capacity of organic matter using the dominant species among them. Chironomid midge and invertebrate cohabitants were quantitatively collected at 78 representative stations of five habitat types (in arable land during 2004$sim$2006) A, paddy fields of the large scale arable land; B, paddy fields of the environmental friendly arable land; C, influent of domestic waste water; D, influent of waste water by livestock; E, the irrigation ditch of paddy area. The total sixteen species of chironomid midges at arable land were presented. And also chironomid midges were recognized by five habitat types: eleven species in D, eight in A, seven in E, six in B, and two in C. We confirmed dominant species in each habitat types as followings: Chironomus nipponensis in A, C, and D; Cricotopus sylvestris in E; Tanytarsus seosanensis in B. Water quality and community index were high in E, but low in A, B, C, and D. Comparing with non-treatment, removal activities of organic matter in bottom by C. nipponensis were increased 18% in 90 individuals treatment. |
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| Ű¿öµå |
| diversity;removal capacity;organic matter;chironomid midge;Chironomus nipponensis;agroecosystem; |
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ȯ°æ»ý¹° / v.27, no.1, 2009³â, pp.31-39
Çѱ¹È¯°æ»ý¹°ÇÐȸ
ISSN : 1226-9999
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200920258463362)
¾ð¾î : Çѱ¹¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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