¶óÆæÆ®¦¢Ä«Æä¦¢ºí·Î±×¦¢´õº¸±â
¾ÆÄ«µ¥¹Ì Ȩ ¸í»çƯ°­ ´ëÇבּ¸½Ç޹æ Á¶°æ½Ç¹« µ¿¿µ»ó°­ÀÇ Çѱ¹ÀÇ ÀüÅëÁ¤¿ø ÇÐȸº° ³í¹®
ÇÐȸº° ³í¹®

Çѱ¹°Ç¼³°ü¸®ÇÐȸ
Çѱ¹°ÇÃà½Ã°øÇÐȸ
Çѱ¹µµ·ÎÇÐȸ
Çѱ¹»ý¹°È¯°æÁ¶ÀýÇÐȸ
Çѱ¹»ýÅÂÇÐȸ
Çѱ¹¼öÀÚ¿øÇÐȸ
Çѱ¹½Ä¹°ÇÐȸ
Çѱ¹½Ç³»µðÀÚÀÎÇÐȸ
Çѱ¹ÀÚ¿ø½Ä¹°ÇÐȸ
Çѱ¹ÀܵðÇÐȸ
Çѱ¹Á¶°æÇÐȸ
Çѱ¹Áö¹Ý°øÇÐȸ
Çѱ¹ÇÏõȣ¼öÇÐȸ
Çѱ¹È¯°æ»ý¹°ÇÐȸ
Çѱ¹È¯°æ»ýÅÂÇÐȸ

Çѱ¹È¯°æ»ýÅÂÇÐȸ / v.22, no.5, 2008³â, pp.471-480
Áö¸®»ê±¹¸³°ø¿ø ÇØ¹ß°íµµ¿Í ½Ä»ý¿¡ µû¸¥ ¹ø½Ä±â Á¶·ù±ºÁýÀÇ Æ¯¼º
( Characteristics of Breeding Bird Community in Relation to Altitude and Vegetation in Jirisan National Park )
À̵µÇÑ;±ÇÇýÁø;¼ÛÈ£°æ; ±Ý°­À¯¿ªÈ¯°æÃ»;Ãæ³²´ëÇб³ »ê¸²ÀÚ¿øÇаú;Ãæ³²´ëÇб³ »ê¸²ÀÚ¿øÇаú;
 
ÃÊ ·Ï
º» ¿¬±¸´Â Áö¸®»ê±¹¸³°ø¿øÀÇ ÇØ¹ß°íµµ¿Í ½Ä»ý¿¡ µû¸¥ ¹ø½Ä±â Á¶·ù±ºÁýƯ¼ºÀ» ÆÄ¾ÇÇϱâ À§ÇØ ½Ç½ÃÇÏ¿´´Ù. Á¶»ç¸¦ À§ÇÏ¿© °íµµ¿Í ½Ä»ý¿¡ µû¶ó 4°³ Á¶»ç±¸¸¦ ¼±Á¤Çϰí 2006³â 3¿ùºÎÅÍ 8¿ù±îÁö ¹ø½Ä±â Á¶·ù±ºÁý°ú ¼­½ÄÁöȯ°æÁ¶»ç¸¦ ½Ç½ÃÇÏ¿´À¸¸ç ±× °á°ú´Â ´ÙÀ½°ú °°´Ù. Àüü Á¶»çÁö¿¡¼­ °üÂûµÈ Á¶·ù Á¾¼ö´Â ÃÑ 32Á¾À¸·Î °¢ Á¶»ç±¸º° °üÂû Á¾¼ö ¹× ¹Ðµµ´Â °íµµ°¡ ³·Àº ȥȿ¸² Á¶»ç±¸¿¡¼­ 27Á¾, 37.31¸¶¸®/ha, °íµµ°¡ ³·Àº Ȱ¿±¼ö¸² Á¶»ç±¸¿¡¼­ 23Á¾, 34.99¸¶¸®/ha, °íµµ°¡ ³ôÀº ȥȿ¸² Á¶»ç±¸¿¡¼­ 18Á¾, 23.95¸¶¸®/ha, °íµµ°¡ ³ôÀº Ȱ¿±¼ö¸² Á¶»ç±¸¿¡¼­ 19Á¾, 20.21¸¶¸®/haÀ̾ú´Ù. °íµµ°¡ ³·Àº Áö¿ª¿¡¼­¸¸ °üÂûµÈ Á¾Àº 11Á¾(¸äºñµÑ±â, °ËÀºµî»µ²Ù±â, Á÷¹Ú±¸¸®, È£¶ûÁöºü±Í, ºÓÀº¸Ó¸®¿À¸ñ´«ÀÌ, ½£»õ, »ê¼Ö»õ, ¼è¼Öµü»õ, Å«À¯¸®»õ, ¹Ú»õ, µ¿¹Ú»õ)À̾úÀ¸¸ç, °íµµ°¡ ³ôÀº Áö¿ª¿¡¼­¸¸ °üÂûµÈ Á¾Àº 4Á¾(µé²æ, ¸Å»çÃÌ, µÎ°ßÀÌ, Èò¹è¸ä»õ)À̾ú´Ù. Á¶·ù Á¾¼ö¿Í ¹Ðµµ´Â °íµµ°¡ ³·Àº Áö¿ª°ú ȥȿ¸²¿¡¼­ ³ô°Ô ³ªÅ¸³µ´Ù. ¿µ¼Ò±æµå´Â °íµµ°¡ ³·Àº Áö¿ªÀº 3°¡Áö À¯ÇüÀÇ Á¾¼ö°¡ ºñ½ÁÇÏ°Ô ³ªÅ¸³µÀ¸¸ç, °íµµ°¡ ³ôÀº Áö¿ªÀº ¼ö°üÃþ ¿µ¼Ò±æµåÀÇ Á¾¼ö°¡ Àû°Ô ³ªÅ¸³µ´Ù. äÀ̱æµå´Â ¸ðµç Á¶»ç±¸¿¡¼­ ¼ö°üÃþ äÀ̱æµåÀÇ Á¾ÀÌ °¡Àå ³ô°Ô ³ªÅ¸³µ´Ù. Á¾º° ¹ÐµµÀÇ Á¶»ç±¸º° Â÷À̺м®¿¡¼­ ½Ä»ý¿¡ µû¸¥ ¹ÐµµÀÇ À¯ÀÇÀû Â÷¸¦ ³ªÅ¸³½ Á¾Àº °íµµ°¡ ³·Àº Áö¿ª¿¡¼­ 4Á¾À¸·Î ±× Áß ¿À¸ñ´«ÀÌ¿Í ¹Ú»õ´Â ¼ö°üÃþÀÇ Çǵµ·®ÀÇ Â÷ÀÌ, Áø¹Ú»õ´Â ħ¿±¼ö¼­½ÄÁö ¼±Åà Ư¼º¿¡ µû¸¥ °ÍÀ̾ú´Ù. °íµµ°¡ ³ôÀº Áö¿ª¿¡¼­ 5Á¾Àº °ü¸ñÃþ ¼ö¸ñÀÇ ¹Ð»ý¿¡ µû¸¥ °ÍÀ¸·Î Á¶»çµÇ¾ú´Ù. °íµµ¿¡ µû¸¥ ¹ÐµµÀÇ À¯ÀÇÀû Â÷¸¦ ³ªÅ¸³»´Â Á¾Àº 10Á¾À¸·Î º¡¾î¸®»µ²Ù±â, ±¼¶Ò»õ, ¼èÀ¯¸®»õ, ¼è¼Ö»õ, Áø¹Ú»õ, ³ë¶ûÅθä»õ´Â °íµµ°¡ ³ôÀº Áö¿ª¿¡¼­, Èò¹èÁöºü±Í, ¿À¸ñ´«ÀÌ, °ïÁÙ¹ÚÀÌ, µ¿°íºñ´Â °íµµ°¡ ³·Àº Áö¿ª¿¡¼­ ¹Ðµµ°¡ ³ô°Ô ³ªÅ¸³µ´Ù. Áö¸®»ê ¹ø½ÄÁ¶·ù±ºÁý ºÐÆ÷´Â °ü¸ñÃþÀÇ ¹Ð»ý°ú ¼ö°üÃþÀÇ ÃÑÇǵµ·® Â÷ÀÌ¿¡ ¿µÇâÀ» ¹Þ´Â °ÍÀ¸·Î º¸¿©Áø´Ù. ±×·¯¹Ç·Î °ü¸ñÃþÀÇ Çǵµ·®°ú ¼ö°üÃþÀÇ ¿±Ãþ´Ù¾ç¼º ¹× ÃÑÇǵµ·® °ü¸® ¹× À¯Áö°¡ ÇÊ¿äÇÒ °ÍÀ¸·Î ÆÇ´ÜµÈ´Ù.
This study was conducted to investigate the characteristics of breeding bird community in relation to altitude and vegetation in Jirisan National Park. The survey was carried over 4 study sites by point counts method to figure out habitat environment and breeding bird community from March to August in 2006. The study results are summarized as follows: Total 32 species were recorded, and 27 species and density of 37.31 ea/ha in low altitude mixed forest, 23 species and 34.99 ea/ha in low altitude deciduous forest, 18 species and 23.95 ea/ha in high altitude mixed forest, 19 species and 20.21 ea/ha in high altitude deciduous forest, respectively. Eleven species were observed only in the low altitude sites, 4 species were observed only in the high altitude sites. Number of species and density were high in the low altitude sites, and they were high in the mixed forests. In nesting guild analysis, the low altitude sites are similarly found species number of three types but canopy nesting species in the high altitude sites are advent less. In foraging guild analysis, the species number of canopy foraging appeared most highly in all study sites. In the difference analysis of each species density. Four species which are showed the difference in the low altitude sites, owing to vegetation. Long-tailed Tit(Aegithalos caudatus) and Great tit(Parus major) are difference because of difference in volume of canopy layer, and Coal Tit(Parus ater) was difference because of coniferous forest preference quality. Four species(Hazel Grouse, Winter Wren, Pale Thrush, Yellow-throated Bunting) which are showed the difference of the density in the high altitude sites because of thick growth of the bush layer. Ten species which are showed the difference in study sites, owing to altitude. Oriental Cuckoo(Cuculus saturatus), Winter Wren(Troglodytes troglodytes), Siberian Blue Robin(Luscinia cyane), Arctic Warbler(Phylloscopus borealis), Coal Tit(Parus ater), and Yellow-throated Bunting(Emberiza elegans) appeared highly in the high altitude sites, Pale Thrush(Turdus pallidus), Long-taild Tit(Aegithalos caudatus), Varied Tit(Parus varius), and Eurasian Nuthatch(Sitta europaea) appeared highly in the low altitude sites. It seems that bush layer coverage volume and canopy layer total coverage volume do influences on the breeding bird community, because the bush layer was thick growth, and canopy layer coverage volume was difference. It would be needed the management and maintenance of bush layer coverage volume and canopy layer with multi-layer structure to increase foliage height diversity and total coverage volume for the protection and management of bird community in Jirisan National Park.
 
Ű¿öµå
Á¤Á¡Á¶»ç¹ý;±æµå;ÀÏ¿øºÐ»êºÐ¼®;POINT-COUNTS METHOD;GUILD;ONE-WAY ANOVA;
 
Çѱ¹È¯°æ»ýÅÂÇÐȸÁö / v.22, no.5, 2008³â, pp.471-480
Çѱ¹È¯°æ»ýÅÂÇÐȸ
ISSN : 1229-3857
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200803657006793)
¾ð¾î : Çѱ¹¾î
³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø
¸ñ·Ïº¸±â
ȸ»ç¼Ò°³ ±¤°í¾È³» ÀÌ¿ë¾à°ü °³ÀÎÁ¤º¸Ãë±Þ¹æÄ§ Ã¥ÀÓÀÇ ÇѰè¿Í ¹ýÀû°íÁö À̸ÞÀÏÁÖ¼Ò ¹«´Ü¼öÁý °ÅºÎ °í°´¼¾ÅÍ
   

ÇÏÀ§¹è³ÊÀ̵¿