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Çѱ¹È¯°æ»ýÅÂÇÐȸ / v.18, no.4, 2004³â, pp.369-381
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( Restoration for Evergreen Broad-leaved Forests by Successional Trends of Pasture-grassland in the Seonheulgot, Jeju-do ) |
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º» ¿¬±¸´Â Àå±â°£ÀÇ ÀÌ¿ë°ú °£¼·À¸·Î ÈÑ¼ÕµÈ ¼±Èê°ù ¹æ¸ñÃÊÁö¸¦ ¿ø½Ä»ýÀÎ »ó·ÏȰ¿±¼ö¸²À¸·Î º¹¿øÇϱâ À§ÇÏ¿© ½Ä»ýÀ¯Çü¿¡ µû¸¥ ½Ä¹°±ºÁý±¸Á¶ ºÐ¼®À» ÅëÇØ õÀ̰æÇâÀ» ¿¹ÃøÇϰí ÀûÇÕÇÑ º¹¿ø¹æ¾ÈÀ» µµÃâÇϰíÀÚ ÇÏ¿´´Ù. ÃÑ 26°³ Á¶»çÁö¸¦ ¼±Á¤ÇÏ¿© ºÐ¼®ÇÑ °á°ú ¿ìÁ¡Á¾ÀÇ Æò±Õ»ó´ë¿ìÁ¡Ä¡¿¡ µû¶ó 4°³ À¯ÇüÀ¸·Î ±¸ºÐµÇ¾ú°í ±³¸ñÃþ ¿ìÁ¡Á¾ÀÇ °æ±ÞÀ» °í·ÁÇÏ¿© 6°³ ±ºÁýÀ¸·Î ºÐ·ùÇÏ¿´À¸¸ç ±ºÁý IÀº µ¢±¼¼º°ü¸ñ¸², ±ºÁý II´Â »ó·ÏȰ¿±¼ö °ü¸ñ¸², ±ºÁý IIIÀº ¼Ò°æ¸ñÀÇ »ó·ÏȰ¿±¼ö¸², ±ºÁý IV, V´Â Áß°æ¸ñÀÇ »ó·ÏȰ¿±¼ö¸², ±ºÁý ¥µÀº ´ë°æ¸ñÀÇ »ó·ÏȰ¿±¼ö¸²À̾ú´Ù. °ü¸ñ¸²ÀÇ ÃâÇöÁ¾Àº °¢°¢ 24, 28Á¾À̾ú°í ¼Ò°æ¸ñ »ó·ÏȰ¿±¼ö¸²Àº 16Á¾, Áß°æ¸ñ »ó·ÏȰ¿±¼ö¸²Àº 29, 30Á¾À̾úÀ¸¸ç ´ë°æ¸ñ »ó·ÏȰ¿±¼ö¸²Àº 27Á¾À̾ú´Ù. Àüü Á¾´Ù¾çµµÁö¼ö´Â 0.8763¡1.2630À̾úÀ¸¸ç Áß°æ¸ñ°ú ´ë°æ¸ñ »ó·ÏȰ¿±¼ö¸²°£ À¯»çµµÁö¼ö°¡ ³ô°Ô ³ªÅ¸³µ´Ù. ±ºÁý I, II, IIIÀº ¹æ¸ñÃÊÁö¿¡¼ »ó·ÏȰ¿±¼ö·Î õÀ̰¡ ÁøÇàµÈ À¯ÇüÀ̾ú°í ±ºÁý IV, V, ¥µÀº ¹æ¸ñÁö³» ÀÜÁ¸¸²À¸·Î¼ ³´ë »ó·ÏÈ®¿±¼ö¸²°ú ½Ä»ý±¸Á¶°¡ À¯»çÇÏ¿´´Ù. ¼±Èê°ù ¹æ¸ñÃÊÁöÁö¿ªÀ» »ó·ÏȰ¿±¼ö¸²À¸·Î º¹¿øÇϱâ À§ÇØ ±¸½ÇÀã¹ã³ª¹«, Á¾°¡½Ã³ª¹«±ºÁýÀ» ¸ñÇ¥·Î ÇÏ¿© ¼±Èê°ù ³» »ó·ÏȰ¿±¼ö¸²À» ¸ðµ¨¸²À¸·Î Á¦½ÃÇÏ¿´À¸¸ç º¹¿ø¸ðµ¨±ºÁýÀÇ »ýÀ°¹Ðµµ´Â ±³¸ñÃþ¿¡ ±¸½ÇÀã¹ã³ª¹«, Á¾°¡½Ã³ª¹«°¡ 100$m^2$´ç 10ÁÖ, ¾Æ±³¸ñÃþ¿¡´Â µ¿¹é³ª¹«, »ç½º·¹Çdzª¹«, Á¾°¡½Ã³ª¹«°¡ 100$m^2$´ç 14ÁÖÀ̾ú´Ù. |
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This study was achieved to present the way to restore the Seonheulgot pasture-grassland damaged by landuse and interference for a long time to evergreen broad-leaved forests as the native vegetation structure. As a result of analyzing ecological succession tendency of structure in survey area, we established the optimal restoration model. The total of survey sites were 26, and the classified plant community types were four types by M.I.P of dominant woody species. Finally we classified the four types based on diameter of dominant woody species in canopy layer. The six community types are as follows: Community I was runner-shrub forest, community II was evergreen broad-leaved shrub forest, and community III was evergreen broad-leaved forest of small diameter. Community IV and V were evergreen broad-leaved forest of middle diameter. Community ¥µ was evergreen broad-leaved forest of large diameter. The number of constituent species was 24 in community I, 28 in community II as the shrub forest, 16 as the evergreen broad-leaved forest of small diameter, 29 in community III, 30 in community IV as the evergreen broad-leaved forest of middle diameter and 27 in community ¥µ as the evergreen broad-leaved forest of large diameter. The range of Shannon's index of all communitys was from 0.8763 to 1.2630 and the Similarity index between the community composed of middle diameter woody species and large diameter woody species. The ecological succession of community I, II, and III were changed from pasture-grassland to broad-leaved forest and the structure of community IV, V, and ¥µ was similar to evergreen broad-leaved forest in warm temperate region. We suggest the restoration planting model evergreen broad-leaved forest of in Seonheulgot pasture-grassland, as follows: The target restoration vegetation were Castanopsis cuspidata var. sievoldii community and Queycus glauca community. Castanopsis cuspidata var. sievoldii and Quercus glauca should be dominant woody species in canopy layer, the number of trees was 10 per 100$m^2$, and Castanopsis cuspidata var, sievoldii, Quercus glauca, Camellia japonica, and Eurya japonica should be dominant woody species in the understory layer, the number of trees was 14 per 100$m^2$. |
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Ű¿öµå |
±¸½ÇÀã¹ã³ª¹«;Á¾°¡½Ã³ª¹«;½Ä»ý±¸Á¶;»ýÀ°¹Ðµµ;CASTANOPSIS CUSPIDATA VAR;SIEVOLDII;QUERCUS GLAUCA;VEGETATION STRUCTURE;GROWTH DENSITY; |
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Çѱ¹È¯°æ»ýÅÂÇÐȸÁö / v.18, no.4, 2004³â, pp.369-381
Çѱ¹È¯°æ»ýÅÂÇÐȸ
ISSN : 1229-3857
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200414714180780)
¾ð¾î : Çѱ¹¾î |
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³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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