초록
인공강우발생장치를 이용하여 4년간 대구 동구지역에 발생한 산불발생지를 대상으로 산불발생지사면의 토양침식량을 계량화하기 위하여 산불발생 후 경과년수에 띠라 각 지역에 대한 강우강도 및 경사별로 토양침식량을 관측하여 산불발생지의 토양침식 특성을 구명하고, 또한 토양침식량과 강우강도, 경사, 경과년수와의 관계를 분석한 결과는 다음과 같다. 1. 산불발생연도별 토양침식량은 강우강도가 30 mm/hr씩 증가함에 따라서 1.9~5.7배 증가하였고, 경사가 $10^{\circ}$씩 증가함에 따라서는 1.4~14.2배 증가하였다. 2. 산불발생당년에는 강우강도 80 mm/hr, 경사 $30^{\circ}$에 대해 초기 강우 10분 동안 토양침식이 많이 발생하였으며, 시간이 경과할수록 점차 그 양이 감소하는 경향을 보였고, 산불발생 후 2년 뒤부터는 강우강도 및 경사별로 경과시간에 따른 토양침식량은 거의 일정하였다. 3. 산불발생 후 경과년수에 따라 강우강도 및 경사별 토양침식량은 산불발생 3년 후의 경우 발생당년에 비해 28.9%~94.1%로 감소하였고, 산불발생당년에는 강우강도 및 경사별로 토양침식량이 많았으며, 산불발생 후 2년 뒤부터 점차 토양침식량의 감소추세가 둔화되었다. 4. 산불발생지사면에서의 토양침식량에 대해 각 인자간의 영향성을 분석한 결과, 강우강도, 경사, 경과년수의 각각의 주효과와 강우강도${\times}$경사, 강우강도${\times}$경과년수의 상호작용 효과에 대해서는 차이를 보였고, 경사${\times}$경과년수, 강우강도${\times}$경사${\times}$경과년수의 상호작용 효과에 대해서는 차이가 없었다. 토양침식량에 영향을 미치는 인자의 영향도는 강우강도가 가장 큰 영향을 미치고 다음이 경사, 경과년수의 순이었다. 5. 토양침식량과 이에 영향을 미치는 인자들과의 상관관계에 있어서, 강우강도, 경사간에는 1%수준에서 유의적인 정(+)의 상관관계가 있었고, 경과년수는 1%수준에서 유의적인 부(-)의 상관관계가 나타났다. 6. 토양침식량과 이에 영향을 미치는 인자들과의 회귀분석 결과, 산불발생지사면에서 토양침식량을 설명하는데 유의한 인자는 강우강도, 경사, 경과년수이었다. 7. 강우강도, 경사, 경과년수를 이용하여 다음과 같은 토양침식량 추정식을 산출하였다. S.E = 0.092R.I + 0.211D.S - 0.942E.Y(S.E : 토양침식량, R.I: 강우강도, D.S: 경사, E.Y: 경과년수)
The purpose of study is to measure soil erosion quantity for elapsed four years from the fire on forest fired sites of Dong-gu, Daegu. This study was conducted to investigate the characteristics of soil erosion by fire occurrence influencing on the soil erosion were. Also analysis result follows that the relations between soil erosion quantity and rainfall intensity, the slope and elapsed year. The results analysed were as follows: 1. Soil erosion by year of occurrence of forest fire was increased 1.9 to 5.7 times as rainfall intensity was increased by 30 m/hr, and 1.4 to 14.2% as degree of slope was increased by $10^{\circ}$. 2. In the first year of forest fire occurrence, soil erosion was fairly heavy for 10 minutes of initial rainfall of which rainfall intensity was 80 m/hr and degree of slope was $30^{\circ}$. The amount of soil erosion was gradually reduced as elapsed time. From two years after fire, the amount of soil erosion by rainfall intensity and degree of slope was nearly constant. 3. The amount of soil erosion by rainfall intensity and slope in accordance with elapsed time after fire was reduced 28.9 to 94.1% in three years after occurrence of forest fire as compared to the first year of fire. Soil erosion was fairly heavy by rainfall intensity and slope in the first year of fire, but it was gradually reduced from two years after fire. 4. In the analysis on influences of each factors on the amount of soil erosion on forest fired sites, the amount of soil erosion was significant differences in major impacts of each rainfall intensity, degree of slope and elapsed year after fire and interaction of rainfall intensity${\times}$degree of slope and rainfall intensity${\times}$elapsed year after fire, but no differences were observed in interaction of degree of slope${\times}$elapsed year after fire and rainfall intensity${\times}$degree of slope${\times}$elapsed year after fire. Rainfall intensity was the most affecting factor on the amount of soil erosion and followed by degree of slope and elapsed year after fire. 5. For correlation between soil erosion and affecting three factors, soil erosion showed significant positive relation with rainfall intensity and degree of slope at I % level, and significant negative relation with elapsed year after fire at 1 % level. 6. As a result of regression of affecting three factors on soil erosion. rainfall intensity was most significant impact factor in explaining the amount of soil erosion on forest fired sites, followed by degree of slope and elapsed year after forest fire. 7. The formula for estimating soil erosion using rainfall intensity, degree of slope and elapsed year after forest fire occurrence was made. S.E = 0.092R.I + 0.211D.S - 0.942E.Y(S.E : Soil erosion, R.I : Rainfall intensity, D.S : Degree of slope, E.Y : Elapsed year after forest fire occurrence)