|
|
|
Çѱ¹È¯°æ»ýÅÂÇÐȸ / v.1, no.1, 1987³â, pp.35-45
|
ºÏÇÑ»ê ±¹¸³°ø¿øÀÇ µî»ê·Î ÈÑ¼Õ ¹× ÁÖº¯ ½Ä»ýº¯È
( Trail Damage and Vegetational Change of Trail Side in Bukhan Mountain National Park ) |
| ¿À±¸±Õ;±ÇÅÂÈ£;Àü¿ëÁØ; ¼¿ï´ëÇб³ ´ëÇпø;´ë±¸´ëÇб³ ³ó°ú´ëÇÐ;¼¿ï½Ã¸³´ëÇб³ Á¶°æ½ÇÅ¿¬±¸½Ç;
|
|
|
 |
|
| |
| ÃÊ ·Ï |
| ºÏÇѻ걹¸³°ø¿øÀÇ µî»ê·ÎÈÑ¼Õ ¹× µî»ê·ÎÁÖº¯½Ä»ýº¯È¸¦ Á¶»çÇϱâ À§ÇÏ¿© ºÏÇÑ»êÁö±¸¸¦ ´ë»óÀ¸·Î 1987³â 8¿ù¿¡ ½ÇÃøÁ¶»ç¸¦ ½Ç½ÃÇÏ¿´´Ù. µî»ê·ÎÈѼÕÀº À̿밵µ°¡ ³ôÀº ¿ìÀ̵¿°è°î°ú Á¤´É°è°î°£ µî»ê·Î 7.18km ±¸°£À» Á¶»çÇß´Ù. ½Ä»ý º¯È´Â µî»ê·Î °æ°èºÎ¿¡¼ ÀÓ³»·Î º§Æ®-Æ®¶õ ¼½Æ®¸¦ ¼³Ä¡ÇÏ¿© ¸Å¸ñÁ¶»ç¸¦ ÇÏ¿´°í, ÁÖº¯ºÎ½Ä»ýÀº µî»ê·Î°æ°èºÎ¸¦ µû¶ó º§Æ®¸¦ ¼³Ä¡Çؼ ÃâÇöÁ¾À» Á¶»çÇÏ¿´´Ù. µî»ê·Î ÈѼշ®°ú À̿밵µ´Â Á÷Á¢Àû »ó°ü°ü°è°¡ ¾ø¾ú´Ù. ÈѼյî±Þ IIµî±Þ±¸°£Àº 23.9%, IIIµî±Þ±¸°£Àº 8.0%·Î ³ªÅ¸³µÀ¸¸ç, ÀÚ¿¬µî»ê·Î II, IIIµî±Þ±¸°£(19.7%)ÀÌ ½Ã¼³µî»ê·Î II, IIIµî±Þ±¸°£(12.3%)º¸´Ù ¸¹°Ô ³ªÅ¸³µ´Ù. ºÏÇÑ»êÁö¿ª ÁÖ¿äµî»ê·Î 15.3kmÁß º¸¼öÁ¤ºñ°¡ ÇÊ¿äÇÑ µî»ê·Î IIµî±Þ±¸°£Àº 3.6km, IIIµî±Þ±¸°£Àº 1.27km·Î ÃßÁ¤µÇ¾ú´Ù. µî»ê°´ÀÇ Á÷Á¢Àû °£¼·ÀÌ ¾ø¾ú´ø µî»ê·Î ÁÖº¯ ½Ä»ýº¯È´Â 6-8m ±¸°£±îÁö ³ªÅ¸³µÀ¸¸ç, µî»ê·ÎÀÇ °£¼·ÀÌ ÀÖ¾ú´ø µî»ê·ÎÁÖº¯½Ä»ýº¯È´Â Åä¾ç°æµµº¯È¿Í ÀÏÄ¡ÇÏÁö ¾Ê°í ¾Ê¾Ò°í ±¹ÁöÀûÀ¸·Î ´Ù¸£°Ô ³ªÅ¸³µ´Ù. ´É¼±ºÎ µî»ê·Î ÁÖ¿¬ºÎ½Ä»ýÀ¸·Î¼ Remkiaer ºóµµ°è±Þ E°è±Þ¼öÁ¾Àº ½Å°¥³ª¹«, Âü½Î¸®, Áø´Þ·¡, D°è±Þ¼öÁ¾Àº º´²É³ª¹«, Á¶·Ï½Î¸®, öÂß, ÆÏ¹è³ª¹«À̾úÀ¸¸ç, Áߺ¹µî»ê·Î¿¡¼´Â ½Å°¥³ª¹«°¡ E°è±ÞÀ¸·Î, Áø´Þ·¡, Âü½Î±â, ±¹¼ö³ª¹«°¡ D°è±Þ¼öÁ¾À¸·Î ÃâÇöÇß´Ù. °è°îºÎ¿¡¼´Â Áø´Þ·¡, Á¶·Ï½Î¸®, ±¹¼ö³ª¹«°¡ D°è±Þ¼öÁ¾À¸·Î ÃâÇöÇßÀ¸¸ç ÀÚµ¿Â÷µµ·Î ¿· °è°îºÎ¿¡¼´Â Âü½Î¸®, Á¶·Ï½Î¸®, ±¹¼ö³ª¹«°¡ D°è±Þ¼öÁ¾À¸·Î ³ªÅ¸³µ´Ù. |
|
| To survey trail damage and vegetational change around trail at Bukhan Mountain National Park in Korea, field survey was executed over Bukhan mountain district during August, 1987. Trail damage was surveyed for he section of 7.18km from Ui valley to Jeongnung valley in which user's density was high. Ground vegetation was surveyed with a belt-transect method from trail edge to forest and edge species were surveyed with a belt method along trail edge. Interrelation between trail damage and user's density was not dear. Damage class II of trail showed 23.9% of the surveyed section and class III showed 8.0% and class II and III of natural trail showed 19.7% and those of facilitated trail showed 12.3%. The length of damage class II and III requiring readjustment were estimated as 3.65 km and 1.22km from the main trail course of 15.3km at Bukhan mountain district. In case of no intervention to forest by users, vegetational change around trails was appeared up to 6-8 m from trailside. But in case of intervention to forest by users, vegetational change was not coincident with the change of soil hardness and was diverse locally. Quercus mongolica, Lespedeza cyrtobotrya and Rbo-dodendron mucronulatum were appeared as Raunkiaer frequency class E, and Weigela subsessilis. Lespedeza maximowiczii, Rhododendron schlippenbachii and Sorbus alnifolid were appeared as class D at trail edge of ridge-Quercus mongolica was appeared as class E and Rhododenderon mucrounulatium. Stephanandra incisa were appeared as class D at trail edge of midslope. Rhododenron mucronulatum. Lespedeza maximowiczii and Stepanandra incisa were appeared as class D at trail edge of valley. Lespedeza cyrtobotrya. Lespedeza maximowiczii and Stephanandra incisa were appeared as class D at trail edge of valley beside motorway. |
| |
| Ű¿öµå |
|
| |
|
|
 |
|
Çѱ¹È¯°æ»ýÅÂÇÐȸÁö / v.1, no.1, 1987³â, pp.35-45
Çѱ¹È¯°æ»ýÅÂÇÐȸ
ISSN : 1229-3857
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO198711922082220)
¾ð¾î : Çѱ¹¾î |
|
| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
|
|
|
|
|
|