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Çѱ¹»ýÅÂÇÐȸ / v.29, no.6, 2006³â, pp.531-537
¿ù¾Ç»ê ÁÖ¿ä ÀÓºÐÀÇ Á¾Á¶¼º°ú ±¸Á¶: ±¹°¡Àå±â»ýÅ¿¬±¸Áö¼Ò¸¦ Áß½ÉÀ¸·Î
( Composition and Structure of the Major Forest Stands in Mt. Worak, Korea: On the National Long-Term Ecological Research Sites )
Á¶ÇöÁ¦;ÀÌÁßÈ¿;¹è°üÈ£; °æºÏ´ëÇб³ ³ó¾÷°úÇбâ¼ú¿¬±¸¼Ò;°æºÏ´ëÇб³ ³ó¾÷°úÇбâ¼ú¿¬±¸¼Ò;»óÁÖ´ëÇб³ »ê¸²È¯°æÀÚ¿øÇаú;
 
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º» ¿¬±¸´Â ¿ù¾Ç»ê ±¹°¡Àå±â»ýÅ¿¬±¸Áö¼Ò¸¦ Áß½ÉÀ¸·Î ÀÌ Áö¿ª¿¡¼­ ´Ù¸¥ °³Ã¼±º¿¡ ºñÇÏ¿© »ó´ëÀûÀ¸·Î ±¤¿ª ¿ìÁ¡ÇÏ´Â ¼Ò³ª¹«¸², ±¼Âü³ª¹«¸², ±×¸®°í ½Å°¥³ª¹«¸² µî 3°³ ÁÖ¿ä ÀÓºÐÀ» ´ë»óÀ¸·Î ±×µéÀÇ Á¾Á¶¼º°ú ±¸Á¶Àû Ư¼ºÀ» Æò°¡ÇÏ¿´´Ù. Á¾ ¹× °³Ã¼¼ö´Â ºÐÆ÷ °æÇâÀº Èä°íÁ÷°æ±ÞÀÌ Áõ°¡ÇÒ¼ö·Ï °¨¼ÒÇÏ´Â °æÇâÀ» ³ªÅ¸³»¾úÀ¸¸ç, Á¾ dzºÎ¼º¿¡ À־ ´Ù¾çÇÑ ÀÔÁö ÀûÀÀ ÆøÀ» °¡Áö°í ÀÖ´Â ½Å°¥³ª¹«¸²ÀÌ ´Ù¸¥ µÎ ÀӺп¡ ºñÇÏ¿© »ó´ëÀûÀ¸·Î ³ô°Ô ³ªÅ¸³²À» ¾Ë ¼ö ÀÖ¾ú´Ù. õÀÌ °æÇâÀº ÀӺк°·Î õÀÌ ´Ü°è»ó ´Ù¼Ò Â÷À̰¡ ÀÖÁö¸¸ Àå±âÀûÀ¸·Î º¸¸é ÀӺРÀ¯Çü¿¡ °ü°è¾øÀÌ ¸ðµÎ ½Å°¥³ª¹«¸²À¸·Î º¯È­µÉ °ÍÀ¸·Î ÆÇ´ÜµÇ¾ú´Ù. °¢ ÀÓºÐÀÇ ¿ìÁ¡Á¾À» ±âÁØÀ¸·Î »ý¸ñ°ú »ç¸ñÀÇ °³Ã¼ ¹Ðµµ ±¸¼ººñ¸¦ º¸¸é ½Å°¥³ª¹«¸²¿¡¼­ ½Å°¥³ª¹« °³Ã¼ 75:25, ±¼Âü³ª¹«¸²¿¡¼­ ±¼Âü³ª¹« °³Ã¼ 94:6, ±×¸®°í ¼Ò³ª¹«¸²¿¡¼­ ¼Ò³ª¹« 86:14·Î ½Å°¥³ª¹«¸²¿¡¼­ °³Ã¼ °í»çÀ²ÀÌ °¡Àå ³ô°í ±¼Âü³ª¹«¸²ÀÌ °¡Àå ³·°Ô ³ªÅ¸³µ´Ù. À̰ÍÀº °¢ ÀÓºÐÀÇ ÃµÀÌ ´Ü°èÀÇ Â÷ÀÌ¿¡ µû¸¥ Á¾°£ ¹× Á¾³» °æÀïÀÇ °á°ú·Î ÆÇ´ÜµÇ¾ú´Ù. ÇÑÆí, ÀӺк° ±¸¼º °³Ã¼¸ñÀÇ °Ç°­ »óŸ¦ º¸¸é ÀÓºÐÀ¯Çü¿¡ °ü°è¾øÀÌ ASÇüÀÌ 75$sim$85%·Î °¡Àå ³ô°Ô ³ªÅ¸³µÀ¸¸ç DFÇüÀº ÀüÇô ³ªÅ¸³ªÁö ¾Ê¾Ò´Ù. ³¡À¸·Î º» ¿¬±¸¸¦ À§ÇØ ¼³Ä¡ÇÑ ¿µ±¸ ¹æÇü±¸´Â ÇâÈÄ Á¤±âÀûÀÎ Á¶»ç¸¦ ÅëÇÏ¿© ÀÌ Áö¿ª »ê¸² »ýÅÂ°è º¸Àü¿¡ ÀûÇÕÇÑ À¯¿ë Á¤º¸¸¦ Á¦°øÇÏ¿© ÁÙ ¼ö ÀÖÀ» °ÍÀÌ´Ù.
We assessed the species composition and structure of the three representative forest stands(Pinus densiflora stand, Quercus variabilis stand, and Ouercus mongolica stand), dominated in the National Long-Term Ecological Research Sites of Mt. Worak, Korea and established a benchmark series of permanent plots and transects with which future changes in forest composition and structure could be monitored. Species richness of Q. mongolica stand was greater than other two stands, due in large part to the greater habitat heterogeneity. Number of trees and species are decreased with increasing DBH classes. The successional trends of the three study stands would be mostly changed as Q. mongolica forest, regardless of forest types. Mean density ratio between alive trees and dead trees of three forest stands appeared with Q. mongolica stand 75:25, Q. variabilis stand 94:6, and P. densiflora stand 86:14, Q. mongolica stand appeared most highly from in three stands. This may be due to interspecific or intraspecific competition that it follows in various successesional stages. One side, when it saw the tree status which shows the tree health, the three forest stands all standing alive type (AS) appeared most highly with 75% to 85% and fallen dead type (DF) did not appear entirely. Remeasurement of permanent plots at periodic intervals will provide useful information on the dynamics of the forest vegetation that can be used in the development of adaptive conservation plans.
 
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Forest stands;Permanent plots;Species composition and structure;Successional trends;Tree status;
 
Journal of Ecology and Field Biology / v.29, no.6, 2006³â, pp.531-537
Çѱ¹»ýÅÂÇÐȸ
ISSN : 1975-020X
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200606142024528)
¾ð¾î : Çѱ¹¾î
³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø
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