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Çѱ¹È¯°æ»ý¹°ÇÐȸ / v.27, no.1, 2009³â, pp.124-133
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ÇÑ·ÁÇØ»ó±¹¸³°ø¿ø Á¶ÇÏ´ë ÇØ¿ª ´ëÇüÀú¼µ¿¹°ÀÇ ±ºÁý±¸Á¶
( Community Structure of Macrobenthic Fauna in the Hallyeohaesang National Park from Korea Strait, Korea ) |
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| º» ¿¬±¸´Â ÇÑ·ÁÇØ»ó±¹¸³°ø¿ø ÇØ¿ª¿¡ ¼½ÄÇÏ´Â ´ëÇüÀú¼µ¿¹°ÀÇ ±ºÁý±¸Á¶¸¦ ÆÄ¾ÇÇϱâ À§ÇÏ¿© 2005³â 6¿ù¿¡ ÇöÀåÁ¶»ç¸¦ ½Ç½ÃÇÏ¿´´Ù. ÇöÀåÁ¶»ç´Â °ÅÁ¦ ÇØ±Ý°Áö±¸¿¡¼ ¿©¼ö ¿Àµ¿µµÁö±¸¿¡ À̸£´Â ÃÑ 25°³ Á¤Á¡À» ´ë»óÀ¸·Î ½Ç½ÃÇÏ¿´´Ù. Á¶»ç °á°ú, ÃÑ 284Á¾ÀÇ ´ëÇüÀú¼µ¿¹°ÀÌ ÃâÇöÇÏ¿´°í, ´ÜÀ§¸éÀû´ç($m^2$)°³Ã¼¼ö¿Í »ýü·®Àº °¢°¢ 2,002°³Ã¼¿Í 154.92 gWWtÀ̾ú´Ù. °³Ã¼¼ö¿Í »ýü·®ÀÇ ÀڷḦ ±âÃÊ·Î LeBris index(1988)¸¦ ÀÌ¿ëÇÏ¿© »óÀ§ 20±îÁöÀÇ ¿ìÁ¡Á¾À» ¼±Á¤ÇÏ¿´´Ù. °³Ã¼¼ö¿¡ ÀÖ¾î¼ »óÀ§ 20À§ ¿ìÁ¡Á¾Àº Àüü ÃâÇö ¹ÐµµÀÇ 47.64%¸¦ Á¡À¯ÇÏ¿´°í, Áß¿ä ¿ìÁ¡Á¾Àº ´Ù¸ð·ùÀÇ ±äÀÚ¶ô¼Û°÷°¹Áö·· ÀÌ(S. longifolia), I. pulchella, M. californiensis, M. multibranchiata, Tharyx sp. 1 ¹× ÀÌ¸ÅÆÐ·ùÀÇ ¾Æ±â¹ÝÅõ¸íÁ¶°³(T. fragilis)µîÀ̾ú´Ù. ¹Ý¸é, »ýü·®¿¡ À־ »óÀ§ 20À§ ¿ìÁ¡Á¾µéÀÌ Àüü Áß·®ÀÇ 70.47%¸¦ Á¡À¯ÇÏ¿´°í, ÀÌ °¡¿îµ¥ ±ØÇǵ¿¹°¹®ÀÇ ¿°Å뼺°Ô(S. lacunosus), ¿¬¾È°Å¹ÌºÒ°¡»ç¸® A. cadicola)¿Í ÀÌ¸ÅÆÐ·ùÀÇ »õÁ¶°³(Fulvia mutica)ÀÇ »ýü·®ÀÌ ³ô¾Ò´Ù. ÃâÇö Á¾ÀÇ °³Ã¼¼ö ÀڷḦ ±âÃÊ·Î ´Ùº¯·®ºÐ¼®(Áý±«ºÐ¼®°ú ´ÙÂ÷¿ø¹è¿¹ý)À» ½Ç½ÃÇÑ °á°ú, Å©°Ô 2°³ÀÇ Á¤Á¡(Á¤Á¡ 1°ú 4)°ú 2°³ÀÇ Á¤Á¡±ºÀ¸·Î ±¸ºÐµÇ¾ú´Ù. ÀÌ Áß Á¤Á¡±º 1Àº ÆÞÇÔ·®ÀÌ ¿ì¼¼ÇÑ Á¤Á¡µé·Î, Á¤Á¡±º 2´Â Á×Àº ÆÐ°¢°ú ¸ð·¡ÇÔ·®ÀÌ ³ôÀº Á¤Á¡±ºÀ¸·Î ´ëº°µÇ¾ú´Ù. ƯÈ÷, ÆÞÇÔ·®ÀÌ ³ôÀº Á¤Á¡ ±º¿¡¼´Â ´Ù¸ð·ùÀÇ ¾ç¼Õ°¹Áö··ÀÌ(M. japonica), ¿À¶Ñ±â°¹Áö··ÀÌ(S. scutata), P. pinnata, Tharyx sp. 1°ú ÀýÁöµ¿¹°¹®ÀÇ ´Ü°¢·ù(¿·»õ¿ì·ù)¿¡ ¼ÓÇÏ´Â M. sinense ¹× E. sechellensis µîÀÌ ¿ìÁ¡ÇÏ¿´´Ù. ¹Ý¸é, ¸ð·¡ÇÔ·®ÀÌ ¸¹Àº ±×·ì 2¿¡¼´Â ´Ù¸ð·ùÀÇ I. pulchella, M. multibranchiata, ´Ü°¢·ùÀÇ µÎ°¡½ÃÀ°Áú²¿¸®¿·»õ¿ì(M. acherusicum), ±Øµ¿À°Áú²¿¸®¿·»õ¿ì(G. japonicus) ¹× ¿¬¾È°Å¹Ìº¼°¡»ç¸®°¡ Ư¡ÀûÀ̾ú´Ù. |
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| The study was performed to investigate the community structure of macrobenthic fauna during June 2005, in Hallyeohaesang National Park from Korea Strait. A total of 284 macrobenthic fauna were collected. The overall average macrobenthic density and biomass were 2,002 individuals m$^{-2}$ and 154.92 gWWt m$^{-2}$, respectively. Based on the Lebris (1988) index, there were 20 species accounting for approximately 47.64% of total individuals. And the highest densities were found in the polychaetes Scoletoma longifolia, Isolda pulchella, Mediomastus californiensis, Minuspio multibranchia, Tharyx sp. 1 and the bivalve Theora fragilis. On the other hand, the top twenty species made up 70.47% of the total biomass while the three most abundant, the echinoderms Schizaster lacunosus, Amphiura vadicola and the bivalve Fulvia mutica. The conventional multivariate statistics (cluster analysis and non-metric Multi-Dimensional Scaling) applied to assess spatial variation in macrobenthic assemblages. As a result of cluster analysis and nMDS ordination, this study area was divided into two different groups of stations and species. In case of station, there are two groups: one is a mud dominated station group and the other is dead shell and sand dominated group. And the 2 faunistic groups were established as follows: 1) a group of relatively higher abundances in mud dominated sediment. There were numerically dominated by the polychaetes Magelona japonica, Sternaspis scutata, Paraprionospio pinnata, Tharyx sp. 1 and the amphipods Monocorophium sinense and Eriopisella sechellensis. 2) a group of relatively higher densities dead shell and sand dominated sediment. These groups were characterized by the polychaetes I. pulchella, M. multibranchiata, the amphipods M. acherusicum, Gammaropsis japonicus and the echinoderm A. vadicola. |
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| Ű¿öµå |
| macrobenthic fauna;distribution;community structure;Hallyeohaesang National Park;Korea; |
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ȯ°æ»ý¹° / v.27, no.1, 2009³â, pp.124-133
Çѱ¹È¯°æ»ý¹°ÇÐȸ
ISSN : 1226-9999
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200920258463379)
¾ð¾î : Çѱ¹¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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