¶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.7, no.1, 1993³â, pp.35-48
ºÏÇÑ»ê ±¹¸³°ø¿ø »ï¸²±ºÁý±¸Á¶ÀÇ 5³â°£ º¯È­ ¿¬±¸
( A Study on the Change of the Plant Community Structure for Five years in Puk¡Çansan National Park )
ÃÖ¼ÛÇö;À̰æÀç; ¼­¿ï½Ã¸³´ëÇб³ ´ëÇпø;¼­¿ï½Ã¸³´ëÇб³ ¹®¸®°ú ´ëÇÐ;
 
ÃÊ ·Ï
º» ¿¬±¸´Â °úÁßÇÑ ÀÌ¿ë¾Ð·Â°ú ´ë±â¿À¿° ¹× »ê¼º¿ì¿¡ ÀÇÇÑ ¸¸¼ºÀû ÇÇÇØ·Î ³¯·Î ÈÑ¼ÕµÇ¾î °¡´Â ºÏÇѻ걹¸³°ø¿øÀ» ´ë»óÀ¸·Î ±â¿Õ¿¡ Á¶»çµÈ ±âÃÊÀÚ·á(¹Ú µî, 1987)¿Í ºñ±³ÇÏ¿© õÀÌÀÇ ¹ß´Þ»óŸ¦ ¾Ë¾Æº¸°íÀÚ ÇÏ¿´´Ù. ºÏÇѻ걹¸³°ø¿ø 26±ºµ¥ÀÇ Á¶»ç±¸¸¦ ¼±Á¤ÇÏ¿© ½Ä¹°±ºÁý±¸Á¶Á¶»ç¸¦ ½Ç½ÃÇÑ °á°ú ´ÙÀ½°ú °°Àº °á·ÐÀ» ¾ò¾ú´Ù. 1. ½Ä¹°±ºÁý±¸Á¶ºÐ¼®À» À§ÇØ TWINSPAN¿¡ ÀÇÇÑclassification ¹× ordination±â¹ýÁß RA, DCA, CCA¸¦ Àû¿ëÇÏ¿© ºÐ¼®ÇÑ °á°ú ºÏÇÑ»ê ±¹¸³°ø¿øÀº ÇØ¹ß°í¿¡ µû¶ó 4°³ÀÇ ±ºÁýÀ¸·Î ºÐ¸®µÇ¾ú´Ù. ºÐ¸®µÈ °¢°¢ÀÇ ±ºÁýÀº ¾Æ±î½Ã³ª¹«-Âü³ª¹«·ù±ºÁý, ȥȿ¸²±ºÁý, Á¹Âü³ª¹«±ºÁý, ½Å°¥³ª¹«±ºÁýÀ̾ú´Ù. ÃßÁ¤µÇ´Â õÀ̰迭Àº ÇØ¹ß°í 500mÀÌ»óÀÇ ±³¸ñ»óÃþ¿¡¼­ ¼Ò³ª¹«$longrightarrow$½Å°¥³ª¹«, ÇØ¹ß°í 500mÀÌÇÏ ±³¸ñ»óÃþ¿¡¼­ ¾Æ±î½Ã³ª¹«$longrightarrow$»ó¼ö¸®³ª¹«, ½Å°¥³ª¹«, »êº¢³ª¹«, ÆÏ¹è³ª¹«$longrightarrow$Á¹Âü³ª¹« ¼øÀ̾úÀ¸¸ç, ±³¸ñÇÏÃþ°ú °ü¸ñÃþ¿¡¼­´Â »êÃʳª¹«, Âü½Î¸®³ª¹«$longrightarrow$°³¿Ì³ª¹«, Áø´Þ·¡, öÂß$longrightarrow$´ç´Üdz ¼øÀ̾ú´Ù. 2. 1987³âµµÀÇ ½Ä¹°±ºÁý±¸Á¶Á¶»ç¿Í ºñ±³ÇÏ¿© õÀ̰¡ ÁøÇàµÈ ÀÚ·á´Â ¾òÀ» ¼ö ¾ø¾ú°í, Àΰ£ÀÇ °£¼·°ú ´ë±â¿À¿° µî¿¡ ÀÇÇØ õÀ̰¡ ÁøÇàµÇÁö ¸øÇÏ´Â °ÍÀ¸·Î ÃßÃøµÇ¾ú´Ù.
To compare ecological succession stage between 1987 and 1992, this study was executed in Mt. Puk'an. 26 sample plots of 500$m^2$ were set up. The results were summarized as follows; 1. To analysis plant community structure, the classification by TWINSPAN and CCA, DCA and RA ordination were applied to the study area. That of Mt. Puk'an was divided 4 groups by altitude. The dividing groups are Robinia pseudo-acacia-Quercus spp. community, mixed forest community, Q. serrata community, and Q. mongolica community. The successional trends of tree species over 500m seem to be from Pinus densiflora to Q. mongolica and below 500m in altitude seem to be from Robinia pseudo-acacia through Quercus acutissima, Q. mongolica, Prunus sargentii, Sorbus alnifolia to Q. serrata in the canopy layer. In the case of understory and shrub layer, the successional trends to be from Corylus sieboldiana, Zanthoxylum schinifolium through Rhus trichocarpa, Rhododendron mucronulatum, Rh. schlippenbachii to Acer pseudo-sieboldianum. 2. In comparing successional trends with 1987', the advanced data was not obtained in 1992. It was postulated that succession is not progressed by human disturbance and air pollution.
 
Ű¿öµå
±ºÁý±¸Á¶º¯È­;õÀÌ;TWINSPAN;RA;DCA;CCA;Community Structure Change;Successional Trends;TWINSPAN;RA;DCA;CCA;
 
Çѱ¹È¯°æ»ýÅÂÇÐȸÁö / v.7, no.1, 1993³â, pp.35-48
Çѱ¹È¯°æ»ýÅÂÇÐȸ
ISSN : 1229-3857
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO199311922083035)
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¿