¶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

Çѱ¹ÀÚ¿ø½Ä¹°ÇÐȸ / v.13, no.3, 2000³â, pp.227-242
°­¿øµµ À½³ª¹« ÀÚ»ý ÀÓºÐÀÇ ÀÔÁöȯ°æ, ½Ä»ý±¸Á¶ ¹× µ¿ÅÂ
( Site Characteristics, and Vegetation Structure, and Dynamics of Forest Communities growing Kalopanax septemlobus (Thunb.ex Murray) Koidz. in Gangwon-do )
ÀÌöȣ;ÃÖ¿µÃ¶;±è¼¼Çö;±Ç±â¿ø; ±¹¸³¼ö¸ñ¿ø ½Ä¹°Á¶»ç°ú;±¹¸³¼ö¸ñ¿ø ½Ä¹°Á¶»ç°ú;ÀÓ¾÷¿¬±¸¿ø ÀÓ¸ñÀ°Á¾ºÎ;Ãæ³²´ëÇб³ »ê¸²ÀÚ¿øÇаú;
 
ÃÊ ·Ï
À½³ª¹« ÀÚ»ýÁöÀÇ º¸Á¸°ú º¹¿øÀ» À§ÇÑ ¿¬±¸ÀÇ ÀÏȯÀ¸·Î °³Ã¼¸ñ ´ÜÀ§·Î »êÀçÇÏ¿© ¼­½ÄÇÏ´Â °ÍÀ¸·Î ¾Ë·ÁÁø À½³ª¹«ÀÇ ±ºÁýÀ» Ž»öÇϰí, ÀÎÀ§Àû °£¼·ÀÌ Àû°í º¸Àü»óŰ¡ ¾çÈ£ÇÑ °­¿øµµ ÈïÁ¤»ê, ¹ß¿Õ»ê, °¡¸®¿Õ»ê Áö¿ªÀ» ´ë»óÀ¸·Î ÁöÇü, Åä¾çƯ¼º µîÀÇ ¹°¸®Àû ȯ°æ°ú ½Ä»ý±¸Á¶¸¦ Á¶»çÇÏ¿´´Ù. 1. À½³ª¹« ÀÚ»ýÁöÀÇ ÀÔÁöȯ°æ Á¶»ç °á°ú ºÐÆ÷¹üÀ§´Â ÇØ¹ß°í 780~1,300mÀÇ ºÏ¼­, ºÏµ¿ ¹× ºÏÇâÀ» Áß½ÉÀ¸·Î °æ»ç°¡ ½ÉÇÑ »êº¹-»ç¸é¿¡ À§Ä¡ÇÏ¿´À¸¸ç, Åä¾ç »êµµ´Â 5.81($pm$0.05)·Î ºñ±³Àû Áß¼º¿¡ °¡±î¿î Åä¾çÀ̸ç, ¾çÀÌ¿Âġȯ¿ë·®(C.E.C.)Àº Æò±Õ 22.30($pm$8.1)(me/100g), À¯±â¹°ÇÔ·® 8.63($pm$0.48)%·Î ºñ¿ÁÇÑ Åä¾çÀÌ¿´´Ù. 2. À½³ª¹«ÀÇ Æò±Õ ¿¬·û »ýÀå·®Àº 1.60~2.41mm/yearÀ¸·Î ¹ß¿Õ»êÀÌ 2.41mm/year·Î °¡Àå ³ô°í, °¡¸®¿Õ»ê 1.98mm/year, ÈïÁ¤»ê 1.60mm/year ¼øÀ¸·Î »ýÀå·®À» ³ªÅ¸³Â´Ù. Ãʱâ 20³â°£ÀÇ »ýÀå·®Àº Æò±Õ »ýÀå·® º¸´Ù ÄÇÀ¸³ª, ±× ÈÄ´Â °è¼ÓÀûÀ¸·Î °¨¼ÒÇÏ´Â °æÇâÀ» ³ªÅ¸³Â´Ù. 3. TWINSPAN¿¡ ÀÇÇÑ ±ºÁýÀÇ ºÐ¸®´Â Áö¿ª°£ÀÇ ±ºÁýºÐ¸®¿¡ Áß¿äÇÏ°Ô ÀÛ¿ëÇÏ¿´À¸¸ç, À½³ª¹«¸²ÀÇ Æò±Õ »ó´ë¿ìÁ¡Ä¡ (MIV)´Â ÈïÁ¤»êÁö¿ª 24.55%, °¡¸®¿Õ»êÁö¿ª 29.25% ±×¸®°í ¹ß¿Õ»êÁö¿ª 38.28%·Î ³ªÅ¸³µÀ¸¸ç, Á¾´Ù¾çµµ´Â ÀüüÀûÀ¸·Î 1.3124~1.3992 ¹üÀ§¸¦ º¸¿© ´ëüÀûÀ¸·Î 3°³ Áö¿ª°£¿¡ Å« Â÷ÀÌ´Â º¸ÀÌÁö ¾Ê¾Ò´Ù. 4. À½³ª¹« ÃþÀ§º° ºÐÆ÷Çü(Morista's index)Àº ±³¸ñÃþ, ¾Æ±³¸ñÃþ ¹× °ü¸ñÃþÀÌ °¢°¢ 0.9629, 2.9570, 20.5419·Î ³ªÅ¸³ª ±³¸ñÃþÀº ÀÓÀÇ ºÐÆ÷ÇÏ´Â °æÇâÀ» º¸¿´À¸³ª ¾Æ±³¸ñÃþ°ú °ü¸ñÃþÀº ÁýÁßºÐÆ÷ÇÏ´Â °ÍÀ¸·Î ³ªÅ¸³µ´Ù. 5. Á¾´Ù¾ç¼º ºÐ¼® °á°ú »ó´ë¿ìÁ¡µµÀÇ ¹üÀ§°¡ 0.1476~0.2065À¸·Î ¸î¸î Á¾¿¡ ÀÇÇÑ ´Ü¼ø¸²À» ÀÌ·çÁö ¾Ê°í ´Ù¼öÀÇ Á¾¿¡ ÀÇÇØ ȥȿµÇ¾î ÀÚ»ýÇϰí ÀÖÀ¸¸ç, À¯»çµµÁö¼ö´Â 64.31~64.54% ¹üÀ§·Î 3°³ Á¶»çÁö¿ª°£¿¡ ½Ä»ýÀÇ ¿¬¼Ó¼ºÀÌ ÀÖ´Â °ÍÀ¸·Î ÆÇ´ÜµÇ¾ú´Ù. 6. Á¶»çÁöÀÇ »ó´ë¿ìÁ¡Ä¡¸¦ ÀÌ¿ëÇÑ Á¾°£ »ó°ü°ü°è¸¦ Á¶»çÇÑ °á°ú À½³ª¹«´Â »ç½º·¹³ª¹«, ¹°Âü´ë, ±îÄ¡¹Ú´Þ³ª¹« ±×¸®°í µé¸Þ³ª¹«¿Í´Â µ¿ÀÏÇÑ »ýÅÂÀû ÁöÀ§¸¦ °®´Â °ÍÀ¸·Î ³ªÅ¸³µÀ¸¸ç, ³ë¸°À糪¹« 1%, Âʵ¿¹é, °í·Î¼è ³ª¹«, ³ª·¡È¸³ª¹«, ´À¸¨³ª¹«´Â 5%¼öÁØÀÇ ºÎÀÇ »ó°ü°ü°è¸¦ º¸¿© »ýÅÂÀû ÁöÀ§°¡ ´Ù¸¥ °ÍÀ¸·Î ³ªÅ¸³µ´Ù. 7. Á÷°æ±Þ ºÐÆ÷¿¡ ÀÇÇÑ °³Ã¼±ºÀÇ »ýÀ° µ¿Å¸¦ ¿¹ÃøÇÑ °á°ú ÈïÁ¤»ê Áö¿ªÀº Á¤±ÔºÐÆ÷¸¦ º¸¿© ¾ÕÀ¸·Î Áö¼ÓÀûÀÎ À¯Áö°¡ °¡´ÉÇϸç, ¹ß¿Õ»êÀÇ °æ¿ì¿¡µµ ¼Ò°æ¸ñ¿¡¼­ ´ë°æ¸ñ¿¡ À̸£±â±îÁö °ñ°í·ç ÃâÇöÇÏ¿© À½³ª¹«¸²ÀÇ Áö¼ÓÀûÀÎ À¯Áö°¡ °¡´ÉÇÒ °ÍÀ¸·Î »ý°¢µÇ³ª °¡¸®¿Õ»êÀÇ °æ¿ì´Â Ä¡¼ö³ª ¾î¸° °³Ã¼°¡ ÃâÇöÀÌ µÇÁö ¾Ê°í Áß°æ±Þ°ú ³ôÀº Á÷°æ±ÞÀÇ °³Ã¼ÀÇ ¹Ðµµµµ ³ôÁö ¾Ê¾Æ ¾ÕÀ¸·Î ÀÌ Áý´Ü¿¡¼­´Â À½³ª¹« Áý´ÜÀÇ Áö¼ÓÀûÀÎ À¯Áö°¡ ¾î·Á¿ï °ÍÀ¸·Î »ý°¢µÈ´Ù.
Site characteristics, vegetation structure and dynamics of Kalopanax septemlobus forests in Mt. Heungjeong, Mt. Balwang and Mt. Gariwang were studied to provide the information need for national resources conservation and restoration of K. septemlobus forest in Gangwon-do of Korea. The K. septemlobus forests were distributed at 780m to 1,300m in altitude, steep slope, ridges-slope areas with facing northeast to northwest in good nutrition area. The annual diameter growth of those trees ranged 1.60mm to 2.41mm. Forty-three plots(20$ imes$20m) were set up at three natural population of Kalopanax septemlobus forest and TWINSPAN method was used for vegetation structure analysis. The result of TWINSPAN ordination show that geographical features played a role in determining community types in the study areas. Community type of the study areas classified into three groups by TWINSPAN; K. septemlobus-Quercux mongolica- Acer mono community(Mt. Balwang), K. septemlobus-Q. mongolica- Tilia amurensis community(Mt. Heungjeong), K. septemlobus-Betula costata-Q. mongolica community(Mt. Gariwang). In most of the K. septemlobus forests, major woody species appeared predominantly were Q. mongolica, T. amurensis, Acer pseudo-sieboldianum, Lindera obtusiloba, A. mono, Magnolia sieboldii, Ulmus davidiana var. japonica. And also, Those species were surveyed in all the areas. Species diversity(H') of investigated areas ranged 0.3124~0.13992 and this value relatively higher than that of other forests with similar site. The range of similarity indices between surveyed areas was 64.1~64.54%. The distribution pattern of Morista's index show that Kalopanax septemlobus distributed randomly in tree and concentrated a few sample plots in subtree layer and shurb layer. K. septemlobus occupied 37.1~58.8% of tree layer story, 8.4~17.6% of subtree layer, 0~0.38% of shurb layer each surveyed area. The association analysis showed that Kalopanax septemlobus positively associated with Betula ermani, Deutzia glabrata, Carpinus cordata, Fraxinus mandshurica and negatively associated with Symplocos chinensis var. pilosa, Styrax obassia, Acer mono, Euonymus macroptera, Ulmus davidiana var. japonica. According to the diameter distribution of Kalopanax septemlobus community, the community of Mt. Gariwang will gradually decline and replaced by Quercus community. The communities of Mt. Heungjeong and Mt. Balwang has its seedlings and saplings, so it may be sustained.
 
Ű¿öµå
Kalopanax septemlobus forest;site;annual diameter growth;Structure and dynamics;Association analysis;Mt. Heungjeong;Mt. Balwang and Mt. Gariwang;
 
Çѱ¹ÀÚ¿ø½Ä¹°ÇÐȸÁö / v.13, no.3, 2000³â, pp.227-242
Çѱ¹ÀÚ¿ø½Ä¹°ÇÐȸ
ISSN : 1226-3591
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200011921402806)
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¿