비점오염제어에 있어서 상대적으로 지하수오염의 가능성이 높은 지역을 선별하고 주된 오염원을 파악하는 것은 그 기여도가 대단히 크다. 이 연구는 제주도를 연구지역으로 하였으며, 현재...
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https://www.riss.kr/link?id=A100294151
2009
English
KCI등재
학술저널
37-45(9쪽)
0
0
상세조회0
다운로드국문 초록 (Abstract)
비점오염제어에 있어서 상대적으로 지하수오염의 가능성이 높은 지역을 선별하고 주된 오염원을 파악하는 것은 그 기여도가 대단히 크다. 이 연구는 제주도를 연구지역으로 하였으며, 현재...
비점오염제어에 있어서 상대적으로 지하수오염의 가능성이 높은 지역을 선별하고 주된 오염원을 파악하는 것은 그 기여도가 대단히 크다. 이 연구는 제주도를 연구지역으로 하였으며, 현재 가장 중요한 오염물질 중의 하나인 질산태 질소를 대상오염물질로 하였다. 기존 및 실제 조사에 의한 토양정보를 토대로 pedotransfer function과 수분이동 모델을 이용하여 토양통별로 산출된 질산태질소오염 민감도 지수를 통해 민감도분포도를 작성하였으며(semi process-based 법), 이를 실제 모니터링된 2,020개의 수질자료와 비교하였고 제안된 semi process-based 법은 기존의 전문가의 의견과 판단에 의존하거나 방대한 파라메터를 요구하는 기존방법들의 단점을 극복하고 충분한 지형적 해상력을 제공하였을 뿐만 아니라, 알려진 질산태 질소 모니터링 자료와도 대부분 잘 부합하였다. 본 연구를 통해 얻어진 결과들은 오염민감성이 높은 지역을 우선 선정하여 주의와 관리대책을 세우는 동시에 주요한 오염원을 파악함으로써 지하수자원을 합리적이고 효율적으로 보호하는데 있어서 유용한 수단이 될 것으로 판단되었다.
다국어 초록 (Multilingual Abstract)
Susceptibility assessment of groundwater contamination is a useful tool for many aspects of regional and local groundwater resources planning and management. It can be used to direct regulatory, monitoring, educational, and policy-making efforts to hi...
Susceptibility assessment of groundwater contamination is a useful tool for many aspects of regional and local groundwater resources planning and management. It can be used to direct regulatory, monitoring, educational, and policy-making efforts to highly vulnerable areas. In this study, a semi process-based was proposed to evaluate relative susceptibilities to groundwater contamination by nitrate on a regional scale. Numerical simulation based on data from each soil series was done to model water flow within soil profiles that were related to groundwater contamination by nitrate. Relative vulnerability indices for each soilseries were produced by manipulation of amount of leaching flux, amount of average water storage in a soil profile, and amount of average water storage change. These indices were designed to convey the trend of leaching flux and to maximize spatial resolution. The resulting vulnerability distribution map was used to locate highly vulnerable sites easily with an appropriate grouping the indices, and was then compared with those from groundwater nitrate concentrations monitored. An excellent agreement was obtained across nitrate concentrations from the highly vulnerable regions and those from the low to stable regions.
목차 (Table of Contents)
참고문헌 (Reference)
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4 Riggle, M.A, "The Wisconsin groundwater contamination susceptibility map" 3 : 85-88, 1991
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6 Yoo, S.H, "Soil and water contamination issues in the Republic of Korea" Chinese Association of Science, Beijing, China, and Korean Associationof Scienceand Technology 1999
7 Pettyjohn, W.A., "Regional Assessment of Aquifer Vulnerability and Sensitivity in the conterminous UnitedStates" Roberst S. Kerr Environmental Research Laboratory 1991
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1 Richards, R., "Wellwaterquality, wellvulnerability, and agricultural contamination in the midwestern United States" 25 : 389-402, 1996
2 Jury, W.A., "Water flow in unsaturated soil In Soil Physics 5th" John Wiley & Sons, Inc. 87-112, 1991
3 Vanclooster, M., "WAVE Reference and User's Manual (Release 2.0)"
4 Riggle, M.A, "The Wisconsin groundwater contamination susceptibility map" 3 : 85-88, 1991
5 Rundquist, D.C., "Statewide groundwater-vulnerability assessment in Nebraska using the DRASTIC/GIS model" 2 : 51-58, 1991
6 Yoo, S.H, "Soil and water contamination issues in the Republic of Korea" Chinese Association of Science, Beijing, China, and Korean Associationof Scienceand Technology 1999
7 Pettyjohn, W.A., "Regional Assessment of Aquifer Vulnerability and Sensitivity in the conterminous UnitedStates" Roberst S. Kerr Environmental Research Laboratory 1991
8 Navulur, K.C.S, "Predicting spatial distribution of vulnerability of Indiana state aquifer systems to nitrate leaching usinga GIS" U.S. National Center for Geographic Information and Analysis 1996
9 Cohen, S., "Potential for pesticide contamination of groundwater resulting from agricultural uses In Treatment and Disposal of Pesticide Waste" American Chemical Society 1984
10 ASI(Agricultural Sciences Institute), "Phosphorus In Soil Chemical Analysis"
11 Olsen, S.R, "Phosphorus In Methods of Soil Analysis, Part 2. Chemical and Microbiological Properties"
12 Domagalski, J, "Pesticide residues in ground water of the San Joaquin valley" 130 : 299-338, 1992
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19 Lee, C.B, "Groundwater resources of Korea and development strategies (In Korean)" Rural Development Corporation 1994
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26 Thomas,G.W, "Assessment of the potential of land areas in Kentucky for groundwater contamination from use of fertilizer nitrogen, agricultural chemicals, and animal manure In Agricultural Chemical Use Impacts on Kentucky Groundwater Resources, 1991 Status Report. College of Agriculture, Kentucky Geological Survey" Institute for Mining and Minerals Research, University of Kentucky 25-34, 1992
27 Song,K.C, "Andic Properties of Major Soils in ChejuIsland (In Korean)" Seoul National Univ. 1989
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Contamination Source Assessment of Groundwater Nitrate in a Complex Terrain
An Introduction of Korean Soil Information System
Phosphate Solubilization and Plant Growth Promotion by Crop Associated Bacteria
학술지 이력
연월일 | 이력구분 | 이력상세 | 등재구분 |
---|---|---|---|
2026 | 평가예정 | 재인증평가 신청대상 (재인증) | |
2020-01-01 | 평가 | 등재학술지 유지 (재인증) | ![]() |
2017-01-01 | 평가 | 등재학술지 유지 (계속평가) | ![]() |
2013-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2010-01-01 | 평가 | 등재 1차 FAIL (등재유지) | ![]() |
2008-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2007-05-25 | 학술지명변경 | 한글명 : Korean Journal of Soil Science and Fertilizer -> 한국토양비료학회지(Korean Journal of Soil Science and Fertilizer) | ![]() |
2006-06-20 | 학술지명변경 | 한글명 : Korean Journal of Soil Science & Fertilizer -> Korean Journal of Soil Science and Fertilizer | ![]() |
2006-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2003-01-01 | 평가 | 등재학술지 선정 (등재후보2차) | ![]() |
2002-01-01 | 평가 | 등재후보 1차 PASS (등재후보1차) | ![]() |
2000-07-01 | 평가 | 등재후보학술지 선정 (신규평가) | ![]() |
학술지 인용정보
기준연도 | WOS-KCI 통합IF(2년) | KCIF(2년) | KCIF(3년) |
---|---|---|---|
2016 | 0.37 | 0.37 | 0.36 |
KCIF(4년) | KCIF(5년) | 중심성지수(3년) | 즉시성지수 |
0.38 | 0.41 | 0.544 | 0.08 |
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