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Çѱ¹ÇÏõȣ¼öÇÐȸ / v.36, no.4, 2003³â, pp.434-446
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½ÀÁö ÅðÀû¹°¿¡¼ ºñ¼ÒÀÇ ¼º»ó°ú À̵¿ ¸ðÀÇ¿¡ °üÇÑ ¼öÇÐÀû ¸ðÇü
( Modeling the Fate and Transport of Arsenic in Wetland Sediments ) |
| ¹Ú¼®¼ø;¿Õ¼ö±Õ; ÀÌÈ¿©ÀÚ´ëÇб³ ȯ°æÇаú;ÀÌÈ¿©ÀÚ´ëÇб³ ȯ°æÇаú;
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| ½ÀÁö¿¡¼ Á߱ݼÓÀ̳ª ¹æ»ç¼º ¹°ÁúÀÇ ¼º»ó°ú À̵¿Àº ÀüÀÚ¼ö¿ëü¿Í À¯±âź¼Ò¸¦ ÀÌ¿ëÇÏ´Â ¹Ì»ý¹°ÀÇ ´ë»çÀÛ¿ëÀÇ °á°ú·Î ³ªÅ¸³ª´Â ÁöÁúÈÇÐÀû ÀÛ¿ë°ú ¹ÐÁ¢ÇÑ °ü°è¸¦ °¡Áö°í ÀÖÀ¸¸ç, ÀÌ·¯ÇÑ ÁöÁúÈÇÐÀû¹ÝÀÀÀÇ °ø°£ÀûÀÎ ºÐÆ÷´Â ÁÖº¯ ȯ°æÀÇ Æ¯¼º¿¡ ÀÇÇØ ¿µÇâÀ» ¹Þ°Ô µÈ´Ù. ½ÀÁö¿¡¼ÀÇ ÀÌ·¯ÇÑ Çö»óÀ» ¼öÇÐÀûÀ¸·Î ¸ðÀÇÇϱâ À§ÇÏ¿© ½Ä¹°ÀÇ Á¸Àç ¿©ºÎ¿¡ µû¸¥ ÅðÀû¹° ³»¿¡¼ÀÇ Áß±Ý¼Ó °Åµ¿¿¡ ´ëÇÑ ÀϹÝÀûÀÎ ¼öÇÐÀû ¸ðÇüÀ» °³¹ßÇÏ¿´´Ù. º» ¸ðÇü¿¡¼ °í·ÁµÇ´Â ÁÖ¿ä ±âÀÛÀº ½ÀÁö¿¡¼ÀÇ Ä§Àû°ú ½Ä¹° »Ñ¸®ÀÇ Á¸Àç°¡ ÅðÀû¹° ³» ÁöÁúÈÇÐÀû ¹ÝÀÀ°ú ÀÌ¼Û ±âÀÛ ¹× È¥ÇÕ°úÁ¤¿¡ ¹ÌÄ¡´Â ¿µÇâ µîÀ̸ç, Á¤»ó»óÅ¿¡ °üÇÑ ¼ö½ÄµéÀÌ ÅðÀû¹° ȯ°æÀÇ ¸ðÀÇ¿¡ Àû¿ëµÇ¾ú´Ù. ¼öÄ¡¸ðÀÇ ½ÇÇèÀÇ °á°ú¿¡ µû¸£¸é, ¿°ÅµÈ ¹°¸®ÇÐÀû±âÀÛµéÀÌ ¹Ì»ý¹°ÀÇ À¯±â ź¼Ò¿ø ºÐÇØÀÛ¿ëÀÇ °á°ú·Î ³ªÅ¸³ª´Â ÀÏ·ÃÀÇ ÀüÀÚ¼ö¿ëü, ±×¿¡ µû¸¥ ¹ÝÀÀ¹°, ¸ðÇü¿¡¼ °í·ÁµÈ Áß±Ý¼Ó ¹°ÁúÀÎ ºñ¼Ò µî ÅðÀû¹°³» ÈÇÐ ¹°ÁúµéÀÇ ¼öÁ÷Àû ºÐÆ÷¿¡ Áß¿äÇÑ ¿µÇâÀ» ¹ÌÄ¡´Â °ÍÀ¸·Î ³ªÅ¸³µ´Ù. ¶ÇÇÑ º» ¸ðÇü¿¡¼´Â ƯÁ¤ÇÑ »ý¹°ÇÐÀû º¯È¯ °úÁ¤ÀÌ ¿¿ªÇÐÀûÀ¸·Î È£ÀÇÀûÀÎ ¿µ¿ª¿¡¼¸¸ ¹ß»ýÇÏ´Â °ÍÀ¸·Î °í·ÁµÇ¾úÀ½¿¡µµ, ºñ»ý¹°ÇÐÀû ÀÛ¿ë°ú È¥ÇÕ ±âÀÛ¿¡ ÀÇÇÏ¿© °¢°¢ÀÇÀüÀÚ¼ö¿ëü ºÐÆ÷ÀÇ ¼öÁ÷Àû ÁßøÀ̳ª ¿ªÀü µî ÇöÀå¿¡¼ ½ÇÁ¦ °üÃøµÇ´Â Çö»ó µéÀ» Àß ¸ð»çÇÒ ¼ö ÀÖ¾ú´Ù. |
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| The fate and transport of many trace metals, metalloids, and radionuclides in porous media is closely linked to the biogeochemical reactions that occur as a result of organic carbon being sequentially degraded by different microorganisms using a series of terminal electron acceptors. The spatial distribution of these biogeochemical reactions is affected by processes that are often unique and/or characteristic to a specific environment. Generic model formulations have been developed and applied to simulate the fate and transport of arsenic in two hydrologic settings, permanently flooded freshwater sediments, namely non-vegetated wetland sediments and vegetated wetland sediments. The key physical processes that have been considered are sedimentation, effects of roots on biogeochemistry, advective transport, and differences in mixing processes. Steady-state formulations were applied to the sedimentary environments. Results of numerical simulations show that these physical processes significantly affect the chemical profiles of different electron acceptors, their reduced species, and arsenate as well as arsenite that will result from the degradation of an organic carbon source in the sediments. Even though specific biological transformations are allowed to proceed only in zones where they are thermodynamically favorable, the results show that mixing as well as abiotic reactions can make the profiles of individual electron acceptors overlap and/or appear to reverse their expected order. |
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| Ű¿öµå |
| Wetland sediments;Geochemistry;Numerical modeling;Arsenic; |
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Çѱ¹ÇÏõȣ¼öÇÐȸÁö / v.36, no.4, 2003³â, pp.434-446
Çѱ¹ÇÏõȣ¼öÇÐȸ
ISSN : 1976-8087
UCI : G100:I100-KOI(KISTI1.1003/JNL.JAKO200318317182044)
¾ð¾î : ¿µ¾î |
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| ³í¹® Á¦°ø : KISTI Çѱ¹°úÇбâ¼úÁ¤º¸¿¬±¸¿ø |
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