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Çѱ¹Á¶°æÇÐȸ / v.36, no.2, 2008³â, pp.60-68
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³óÃÌ Á¶°ÇºÒ¸®Áö¿ªÀÇ °æ°ü°³¼±À» À§ÇÑ Á¢±Ù
( An Approach to Enhance the Unfair Area in the Rural Landscape ) |
| Àå°©¼ö;¹ÚÀÎȯ; Ãæ³²¹ßÀü¿¬±¸¿ø ȯ°æ»ýÅ¿¬±¸ÆÀ;°æºÏ´ëÇб³ Á¶°æÇаú;
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| °æ»ó³²µµ â³ç±º À̹æ¸éÀ» ´ë»óÀ¸·Î ÅäÁöÀÌ¿ë Á¦ÇÑÀÎÀÚÀÎ È«¼öÇÇÇØ, Åä¾çħ½Ä ±×¸®°í ÈÞ°æ ÀáÀ缺À» Á¾ÇÕÇÑ ÅäÁöÆò°¡¿¡ µû¶ó Á¶°ÇºÒ¸®Áö¿ªÀ¸·Î ¼±Á¤µÈ Áö¿ª¿¡ ´ëÇÏ¿© °æ°üº¹¿øÀ» À§ÇÑ Á¦¾ðÀ» Çϰí, À̸¦ ¹ÙÅÁÀ¸·Î °æ°üº¹¿ø ÀüÈÄÀÇ °æ°ü±¸Á¶ ºñ±³¸¦ ÅëÇÏ¿© °æ°ü°³¼± È¿°ú¸¦ Æò°¡ÇÏ¿´´Âµ¥, ±× °á°ú´Â ´ÙÀ½°ú °°´Ù. ù°, ÅäÁöÆò°¡ °á°ú ¿¬±¸Áö¿ª ³» ³ó°æÁö ¸éÀû 2,924.34ha Áß 1±ÞÁö´Â 388.560a, 2±ÞÁö´Â 623.25haÁ¸ÀçÇÏ¿´°í, 3±ÞÁö´Â 138.08ha, 4±ÞÁö´Â 230.4ha, ±×¸®°í 5±ÞÁö´Â 67.91ha Á¸ÀçÇÏ¿´´Ù. ÀÌ Áß 3±ÞÁö¿Í 4±ÞÁö¿¡ ÇØ´çÇÏ´Â Áö¿ªÀº Á¶°ÇºÒ¸®Áö¿ªÀ¸·Î °£ÁÖÇÏ¿© °æ°ü°³¼±À» À§ÇÑ Á¦¾ÈÀ» ÇÏ¿´´Ù. µÑ°, ħ¼öÀáÀ缺À» °¡Áø Á¶°ÇºÒ¸®Áö¿ªÀº ½ÀÁö¿Í ±× ¿ÏÃæÁö¿ªÀ¸·ÎÀÇ º¹¿øÀ» Á¦¾ÈÇÏ¿´°í, ÀÌ ¶§ º¹¿ø´ë»ó ÅäÁöÀÇ ¼ÒÀ¯ÁÖ¿¡°Ô´Â °æ°üº¸ÀüÁ÷Á¢ÁöºÒÁ¦¿¡ ÀÇÇÑ º¸»óÀÌ ÀÌ·ç¾îÁú ¼ö ÀÖÀ» °ÍÀ¸·Î ÆÇ´ÜÇÏ¿´´Ù. Åä¾çħ½ÄÀáÀ缺À» °¡Áø Á¶°ÇºÒ¸®Áö ¿ª ÀÇ °æ¿ì, ÃÊ»ýÀç¹è, ´ë»ó½Ä»ý, ÀáÀçÀÚ¿¬½Ä»ýÀ¸·ÎÀÇ ÀüȯÀ» ÅëÇÑ Áö·Âº¸° ¹æ¹ýÀ» Á¦¾ÈÇÏ¿´´Ù. ¼Â°, Á¶°ÇºÒ¸®Áö¿ªÀÇ °æ°üº¹¿ø¿¡ ´ëÇÑ Á¦¾È¿¡ µû¶ó °æ°üº¹¿ø ÀüÈÄÀÇ °æ°ü±¸Á¶¸¦ Æò°¡ÇÑ °á°ú, »ê¸²Àº ±× ÆÐÄ¡ÀÇ ¼ö, °æ°üºñÀ², ÃÖ´ëÆÐÄ¡Áö¼ö, °æ°üÇüÅÂÁö¼ö, »êÀç º´·ÄÁö¼ö, ±×¸®°í ÇÙ½ÉÁö¿ª ¸éÀû¿¡¼ ¸ðµÎ Áõ°¡ÇÑ ¹Ý¸é, ³í ¹ç°ú °ú¼ö¿ø¿¡¼´Â ÆÐÄ¡¼ö, °æ°üÇüÅÂÁö¼ö¸¦ Á¦¿ÜÇÑ ´ëºÎºÐÀÇ Áö¼ö¿¡¼ °¨¼ÒÇÏ´Â °ÍÀ¸·Î È®ÀÎÇÏ¿´´Ù. ¿ì¸®³ª¶ó »ê¸²Àº °ú°Å ³ó¾÷ÀÌ °æÀï·ÂÀ» °¡Áú ´ç½Ã¿¡ Áö³ªÄ¡°Ô È®ÀåµÇ¾î ÇöÀç È«¼öÇÇÇØ, ÈÞ°æ µî ¿©·¯ °¡Áö ¿¾ÇÇÑ ¿©°ÇÀ» °¡Áö°í ÀÖÀ¸¹Ç·Î À̸¦ °³¼±Çϱâ À§ÇÑ ³ë·ÂÀÌ ÇÊ¿äÇÏ´Ù°í º¸¸ç, ±×·± Àǹ̿¡¼ º» ¿¬±¸°¡ ³ª¸§ÀÇ Àǹ̰¡ ÀÖ´Ù°í »ç·áµÈ´Ù. |
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| Three land-use limitations including water hazard, soil erosion and fallow potential were evaluated to define an unfair area. Landscape indices in the unfair areas, defined by evaluations before and after landscape enhancement, were computed by Fragstats v3.3 and compared in order to propose a landscape enhancement plan. The results are as follows: First, as a result of the land evaluation, 388.56ha was analyzed for the 1st class(S1), 623.25ha for the 2nd class(S2), 138.08ha(S3s: 82.47ha, S3e: 51.88ha) for the 3rd class(S3), 230.44ha(N1w: 194.91ha, N1e: 23.09ha, N1es: 13.94ha) for the 4th class(N1), and 67.91ha(N2w: 60. 89ha, N2es: 7.02ha) for the 5th class(N2). The classes under the 3rd class(including the 3rd class) were determined as an unfair area, and proposed landscape enhancement for them. Second, it was proposed that unfair areas with potential water hazards(N1 w, N2w) be restored as a wetland and buffer zone. At this point, the farmers owning these fields could be compensated using the direct payment for landscape conservation(DPLC). Areas witha relatively lower slope(S3e) or a steep slope(N1e) containing soil erodibility potential were proposed to be restored as a sod-culture-applied field and substitute vegetation or potentially natural vegetation, respectively. The unfair areas having fallow potential(S3s, N1es, N2es) were proposed to apply special use crops for the S3s fields, native plants for the N1es fields, and intended fallow for the N2es fields. Third, after landscape enhancement, theforest had higher values in the indices of NP, PLAND, LSI, IJI, and TCA, while paddy and upland had lower values in most indices except NP and LSI. The forest patches increased and were more plentiful with their restoration and had much greater possibility to join with nearby patches. With continued restoration, forest patches will have a large core area and small number of patches due to the conglomeration of patches, which positively influences the species of diversity in the forest patches. |
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| Ű¿öµå |
| °æ°üÆÐÄ¡;ÅäÁöÆò°¡;°æ°ü ÆÄÆíÈ;°æ°üÁö¼ö;Landscape Patch;Land Evaluation;Landscape Fragmentation;Landscape Index; |
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Çѱ¹Á¶°æÇÐȸÁö / v.36, no.2, 2008³â, pp.60-68
Çѱ¹Á¶°æÇÐȸ
ISSN : 1225-1755
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200827448607947)
¾ð¾î : Çѱ¹¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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