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Çѱ¹È¯°æ»ýÅÂÇÐȸ / v.24, no.2, 2010³â, pp.139-146
žÈÇØ¾È±¹¸³°ø¿øÀÇ ¹ø½Ä±â Á¶·ù»ó°ú °ü¸®
( Avifauna and Management of Breeding Season in Taeanhaean National Park )
¹éÀÎȯ;Áø¼±´ö;À¯ÀçÆò;¹é¿î±â; ±¹¸³Áß¾Ó°úÇаü ÀÚ¿¬»ç¿¬±¸½Ç;±¹¸³Áß¾Ó°úÇаü ÀÚ¿¬»ç¿¬±¸½Ç;±¹¸³Áß¾Ó°úÇаü ÀÚ¿¬»ç¿¬±¸½Ç;±¹¸³Áß¾Ó°úÇаü ÀÚ¿¬»ç¿¬±¸½Ç;
 
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žÈÇØ¾È±¹¸³°ø¿øÀÇ ¹ø½Ä±â¿¡ ¼­½ÄÇÏ´Â Á¶·ù ÇöȲÀ» ÆÄ¾ÇÇϱâ À§ÇÏ¿© °ø¿ø³» ÇØ¾È¼± Áö¿ª°ú 10°³ÀÇ µµ¼­ Áö¿ªÀ» ¼±Á¤ÇÏ¿© 2009³â 7¿ù 5ÀϺÎÅÍ 9ÀϱîÁö 3°³ ÆÀÀ¸·Î ³ª´©¾î µ¿½Ã Á¶»çÇÏ¿´´Ù. Àüü °üÂûÁ¾Àº 58Á¾ 7,323°³Ã¼¿´°í, ÇØ¾È¼± Áö¿ªÀº 48Á¾ 6,187°³Ã¼, µµ¼­ Áö¿ªÀº 33Á¾ 1,136°³Ã¼¿´´Ù. °ø¿ø³» ÃÖ¿ìÁ¡Á¾Àº ±ªÀ̰¥¸Å±â·Î¼­ ¾à 60%¿¡ À̸£¸ç, °ø¿ø°ú ÀÎÁ¢ÇÑ µµ¼­¿¡¼­ Áý´Ü ¹ø½ÄÇÑ °³Ã¼·Î ÃßÁ¤µÈ´Ù. ÇÑÆí, ¿¬¾È Áö¿ª¿¡¼­¸¸ °üÂûµÈ Á¶·ù´Â Èò»´°ËµÕ¿À¸®, ¹°´ß, Áß¹é·Î µî 25Á¾ 318°³Ã¼À̰í, µµ¼­ Áö¿ª¿¡¼­¸¸ °üÂûµÈ Á¶·ù´Â °¡¸¶¿ìÁö, Ä®»õ, ¼¶°³°³ºñ µî 10Á¾ 308°³Ã¼¿´´Ù. µµ¼­Áö¿ª¿¡¼­´Â °¡Àǵµ¸¦ ºñ·ÔÇÑ À¯Àεµ¼­¿¡¼­ Á¾°ú °³Ã¼¼ö°¡ ³ô°Ô ³ªÅ¸³µ´Âµ¥, µµ¼­ ¸éÀû°ú ¼öÀÚ¿ø À¯¹«, ´Ù¾çÇÑ ¼­½ÄÁö¿Í °ü·Ã ÀÖ´Â °ÍÀ¸·Î ÆÇ´ÜµÈ´Ù. °ú°Å ÀÚ·á¿Í ±Ý¹ø Á¶»ç °á°ú, ÁÖ¿ä ¿ìÁ¡Á¾Àº À¯»çÇÑ °æÇâÀ» º¸À̰í ÀÖÀ¸¸ç, 2007³â ±â¸§À¯Ãâ »ç°í Áö¿ªÀÓ¿¡µµ 2004³âº¸´Ù ¼öÁ¶·ù°¡ Áõ°¡ÇÑ Á¡¿¡¼­ ȸº¹µÇ¾î°¡´Â °ÍÀ¸·Î ÆÇ´ÜµÈ´Ù. ÇöÀç žÈÇØ¾È±¹¸³°ø¿ø°ú ÀÎÁ¢ÇÑ ¿¬¾ÈÀº ¸Å¸³°ú Á¶·Â¹ßÀü¼Ò°¡ Á¶¼º ¹× ¿¹Á¤µÇ°í ÀÖ°í, µµ¼­Áö¿ªÀº Ææ¼ÇÁõ°¡ µîÀÌ ¿¹»óµÇ¸é¼­ Áß¿äÇÑ ¼­½ÄÁö ÈѼհú ±³¶õÀÌ ¿¹»óµÈ´Ù. ÀÌ·¯ÇÑ À§Çù¿äÀο¡ ´ëºñÇϰí, °ø¿øÀÇ ÀûÀýÇÑ °ü¸®¸¦ À§Çؼ­´Â Á¶·ùÁ¤º¸°¡ ºÎÁ·ÇÑ µµ¼­ Áö¿ª¿¡ ´ëÇÑ Á¶·ù¸ð´ÏÅ͸µÀ» °­È­Çϰųª ŽÁ¶°¡ÀÇ Á¶·ù°á°ú¸¦ È¿À²ÀûÀ¸·Î °ü¸®ÇÒ ¼ö ÀÖ´Â Á¶·ùÁ¤º¸½Ã½ºÅÛÀÌ ¿ì¼±ÀûÀ¸·Î ÇÊ¿äÇÏ´Ù°í ÆÇ´ÜµÈ´Ù.
The survey was done in order to find what kinds of birds visit Taeanhaean National Park during breeding season, where we fixed up 10 coastal areas and islands within the National Park. Three groups concurrently performed the field research from 5th to 9th of July in 2009. Total 58 species and 7,323 individuals were recorded in Taeanhaean National Park. 48 species including 6,187 individuals were observed in coastal areas and 33 species including 1,136 individuals in island areas. The most dominant species in the National Park are Larus crassirostris which accounts for 60% of the birds inhabiting there, and they seem to have been bred in the islands near the National Park. The birds observed only around the coastal areas include Anas poecilorhyncha, Fulica atra, Egretta intermedia and the others which consist of 25 species and amount to 318 individuals, and the birds found exclusively in island areas include Phalacrocorax filamentosus, Apus pacificus¢¬ Locustella pleskei and other birds, which consist of 10 species and the number of those individuals observed was 308. The inhabited islands areas such as Gauido were characterized by high ratio of waterbird population, which seems to be correlated with the factors such as the extent of island, the richness of water resources, and the diversity of habitats. Based on the data collected during the research and other data from the previous observations, the kinds of dominant species remain nearly unchanged. And in spite of the oil spill accident in 2007, the increase in the number of waterbirds compared to 2004 may be the evidence that the area is recovering from the environmental pollution. At present, the tidal power plants are being built or scheduled to be built and large-scale reclamation is also under way. What is worse, those areas are seeing the increase of pension construction, which is likely to be the potential cause of damage and disturbance against some key habitats for the waterbirds. Therefore, it is a major priority that we build the bird information system to efficiently manage the knowledge-based asset collected from bird-watching groups and to better monitor the areas that need enhanced database through which the National Park can be appropriately administered.
 
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ÇØ¾ÈÁö¿ª;µµ¼­Áö¿ª;¿ìÁ¡Á¾;Á¶·ùÁ¤º¸;COASTAL AREAS;ISLAND AREAS;DOMINANT SPECIES;BIRD INFORMATION SYSTEM;
 
Çѱ¹È¯°æ»ýÅÂÇÐȸÁö / v.24, no.2, 2010³â, pp.139-146
Çѱ¹È¯°æ»ýÅÂÇÐȸ
ISSN : 1229-3857
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO201027463259745)
¾ð¾î : Çѱ¹¾î
³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø
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