• 한국지역지리학회지
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• 제3권2호
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• pp.195-208
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• 1997

1910년대 지형도와 1990년대 지형도 및 위성영상을 기본도로 하여 한국의 각 지역별 간석지 분포와 간척 현황을 GIS로서 계량하고 지역별 간석지 발달조건을 고찰했다. 그 결과 우리나라 간석지 자원은 1910년대 이후 간척된 것을 포함하여 약 $3,800km^2$이고 전남 서해안, 경기만, 아산만, 전남남해안, 군산만, 천수만, 경남부산해안 순으로 넓게 형성되어 있으며, 현재 공사중인 것까지 합하면 50% 이상 간척되고 있다. 간석지 발달조건의 측면에서 경기 아산만은 모든 조건이 고루 갖추어져 있고, 군산만은 육상퇴적물 공급체계가, 전남 해안은 해안선 조건이 각각 두드러지게 양호하여 간석지가 발달했다. 군산만을 사례로 간석지 발달의 경년변화를 살펴본 결과 간석지 모양은 계속 변해가고 있으며, 면적이 조금씩 늘고 있다. 그러나 20C 전반부에는 면적증가율이 비교적 높은 데 비하여 후반부에는 훨씬 낮아져 거의 정체상태에 있는 것으로 나타났다.

• 한국환경복원기술학회지
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• 제20권4호
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• pp.29-42
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• 2017

As the "Guidelines for GHG Environmental Assessment" was revised, it pointed out that the developers should evaluate GHG sequestration and storage of the developing site. However, the current guidelines only taking into account the quantitative reduction lost within the development site, and did not consider the qualitative decrease in the carbon sequestration capacity of forest edge produced by developments. In order to assess the quantitative and qualitative effects of vegetation carbon uptake, the CASA-NPP model and satellite image spatial-temporal fusion were used to estimate the annual net primary production in 2005 and 2015. The development projects between 2006 and 2014 were examined for evaluate quantitative changes in development site and qualitative changes in surroundings by development types. The RMSE value of the satellite image fusion results is less than 0.1 and approaches 0, and the correlation coefficient is more than 0.6, which shows relatively high prediction accuracy. The NPP estimation results range from 0 to $1335.53g\;C/m^2$ year before development and from 0 to $1333.77g\;C/m^2$ year after development. As a result of analyzing NPP reduction amount within the development area by type of forest development, the difference is not significant by type of development but it shows the lowest change in the sports facilities development. It was also found that the vegetation was most affected by the edge vegetation of industrial development. This suggests that the industrial development causes additional development in the surrounding area and indirectly influences the carbon sequestration function of edge vegetaion due to the increase of the edge and influx of disturbed species. The NPP calculation method and results presented in this study can be applied to quantitative and qualitative impact assessment of before and after development, and it can be applied to policies related to greenhouse gas in environmental impact assessment.