¶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.17, no.4, 2004³â, pp.337-345
»ê¸² ¹úäÀûÁöÀÇ ½Ä»ý±¸Á¶ º¯È­(II)-Ȳ¾ç½Ã ¹é¿î»ê¿¬½À¸²Áö¿ªÀ» Áß½ÉÀ¸·Î-
( Change of Vegetation Structure in the Harvested forest Area(II)-A Case of (Mt.)Baegwoonsan Research forest at Kwangyang City- )
¿À±¸±Õ;ÃÖ¼ÛÇö;¹Ú»ó±Ô;½ÉÇ׿ë; È£³²´ëÇб³ ȯ°æÁ¶°æÇаú;¹Ð¾ç´ëÇб³ Á¶°æÇаú;È£³²´ëÇб³ ´ëÇпø Á¶°æÇаú;È£³²´ëÇб³ ȯ°æµðÀÚÀÎ °øÇкΠÁ¶°æÇаú;
 
ÃÊ ·Ï
³«¿±È°¿±¼ö¸² °³¹ú ÈÄ ¹úäÁö¿¡¼­ ½Ä»ý±¸Á¶ ȸº¹°úÁ¤°ú º¯È­¸¦ °üÂûÇϱâ À§ÇÏ¿© ¼­¿ï´ëÇб³ ³ó¾÷»ý¸í°úÇдëÇÐ ºÎ¼Ó ³²ºÎ¿¬½À¸²ÀÎ ¹é¿î»êÀÇ ¹úäÁö¸¦ ´ë»óÀ¸·Î ¼±Á¤ÇÏ¿´´Ù. 1994³â¿¡ 2°³ÀÇ ¸ð´ÏÅ͸µ Á¶»ç±¸¸¦ ¼³Ä¡ÇÏ¿´°í, 1997³â°ú 1999³â, 2001³â, 2003³â¿¡ ½Ä»ýÁ¶»ç¸¦ ÇÏ¿´´Ù. ¹úäÈÄ 10³â°£ ¹úäÁöÀÇ »ê¸²½Ä»ýº¯È­´Â ´ÙÀ½°ú °°´Ù. ¹úäÁö »ê¸²³»ºÎ¿¡¼­ ¹úä ÈÄ 1³â°¿¡´Â ÀÜÁ¸ ¼ö¸ñÀÎ Âʵ¿¹é³ª¹«, ¶§Á׳ª¹« ¹× ºñ¸ñ³ª¹«°¡ ¿ì¼¼ÇÏ°Ô ³ªÅ¸³µÀ¸¸ç, ¹úä ÈÄ 6³â°¿¡´Â ±ÙÁָ;ƸñÀÎ ¶§Á׳ª¹«¿Í ºñ¸ñ³ª¹«, ½Ç»ý¸ñÀÎ µÎ¸¨³ª¹«°¡ ¿ì¼¼ÇÏ°Ô ³ªÅ¸³µ°í, ¹úä ÈÄ 8³âÂ÷ºÎÅÍ ¹úä ÈÄ 10³âÂ÷ ±îÁö ºñ¸ñ³ª¹« ¶§Á׳ª¹«, Á¹Âü³ª¹« µîÀÌ ¿ìÁ¡Á¾À¸·Î ³ªÅ¸³µ´Ù. ¹úäÁö »ê¸²³»ºÎÀÇ Á¾´Ù¾çµµÁö¼ö´Â ³²¼­»ç¸é¿¡¼­ °è¼Ó ³·¾ÆÁ³À¸¸ç, ºÏµ¿»ç¸é¿¡¼­´Â 6³âÂ÷±îÁö Áõ°¡ÇÏ´Ù°¡ ¹úä ÈÄ 8³âÂ÷ºÎÅÍ °¨¼ÒÇÏ¿´´Ù. Èä°íÁ÷°æ±Þ(DBH) ºÐ¼®¿¡¼­ ¹úä ÈÄ 10³â°æ°ú½Ã ³²¼­»ç¸éÀÇ °æ¿ì Á¹Âü³ª¹«, ¶§Á׳ª¹«, ºñ¸ñ³ª¹«ÀÇ °³Ã¼¼ö°¡ ÃâÇöÀ²ÀÌ ³ô¾Ò°í, ºÏµ¿»ç¸éÀÇ °æ¿ì ´ç´Üdz³ª¹«, Âʵ¿¹é³ª¹«, ÇԹڲɳª¹«, ºñ¸ñ³ª¹«. µÎ¸¨³ª¹«ÀÇ °³Ã¼¼ö ÃâÇöÀ²ÀÌ ³ô°Ô ³ªÅ¸³µ´Ù. ±âÀú¸éÀûÀº ³²¼­»ç¸éÀÇ °æ¿ì 8³âÂ÷¿¡ ºñÇØ °¨¼ÒÇÏ¿´À¸³ª, ºÏµ¿»ç¸é °æ¿ì´Â Áõ°¡ÇÏ¿© »ç¸é°£ Â÷À̸¦ º¸¿´´Ù.
The objective of this study was to monitor vegetation recovery process after timber harvesting at (Mt.) Baekwoonsan Seoul National University Forests, Korea. Two monitoring plots were established in 1994 and woody plant were monitored in 1997, 1999, 2001, and 2003. Vegetation development pattern during last ten years (1994-2003) after timber harvesting were as follows; Styrax obassia, Styrax japonica and Lindera erythrocarpa as of the existing tree were competitive species in the first year after clear-cut, Styrax japonica and Lindera erythrocarpa as of sprout tree and Aralia elata as of seedling were dominant species in the sixth year after clear-cut, and Lindera erythrocarpa, Styrax japonica and Quercus serrata were dominant species from the eighth year to the tenth year after clear-cut. Species diversity index of harvested forest interior was decreased at the southwestern slope while it was increased in the northeastern slope till 6th year and decreased after the 8th year). According to DBH distribution pattern, No. of individuals of Quercus serrata, Styrax japonica and Lindera erythrocarpa showed high frequency in the southwestern slope, and Acer pseudosieboldianum, Styrax obassia, Magnolia sieboldii, Lindera erythrocarpa, and Aralia elata showed good growth in the northeastern slope. There was a difference between slopes in Basal area. It was decreased at the southwestern slopes during the 10th year continuously and it was increased the sixth year however, was decreased after the eighth year at the northeastern slope.
 
Ű¿öµå
±ÙÁָ;Ƹñ;½Ç»ý¸ñ;±âÀú¸éÀû;SPROUT TREE;SEEDLING TREE;BASAL AREA;
 
Çѱ¹È¯°æ»ýÅÂÇÐȸÁö / v.17, no.4, 2004³â, pp.337-345
Çѱ¹È¯°æ»ýÅÂÇÐȸ
ISSN : 1229-3857
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200411922098429)
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¿