TW200419045A - Sediment yield estimation expert system (SedExpert) - Google Patents

Sediment yield estimation expert system (SedExpert) Download PDF

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TW200419045A
TW200419045A TW92106874A TW92106874A TW200419045A TW 200419045 A TW200419045 A TW 200419045A TW 92106874 A TW92106874 A TW 92106874A TW 92106874 A TW92106874 A TW 92106874A TW 200419045 A TW200419045 A TW 200419045A
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soil
slope
mud
sand
factor
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TW92106874A
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Chinese (zh)
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Chao-Yuan Lin
Wen-Tzu Lin
Wen-Chieh Chou
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Chao-Yuan Lin
Wen-Tzu Lin
Wen-Chieh Chou
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Priority to TW92106874A priority Critical patent/TW200419045A/en
Publication of TW200419045A publication Critical patent/TW200419045A/en

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Abstract

In the Soil and Water Conservation Technical Regulations published by Council of Agriculture, Executive Yuan, Republic of China, chapter 2 basic data investigation and analyses, section 8 soil erosion, 62th rule indicates the soil erosion estimation of slope land may use Universal Soil Loss Equation (USLE), the formula can be calculated as: Am=Rm.Km.L.S.C.P, where Am is the average annual soil loss (t/ha per year), Rm the rainfall erosivity factor (MJ/hammh), Km the soil erodibility factor (t/MJ h mm), L the slope length factor, S the slope steepness factor, C the cover-management factor and P is the supporting practice factor. During an early stage, soil loss in small agricultural plots could be obtained through the field survey. With the fast progress in computer technology, soil erosion can be scaled up from slope to the large-scale watershed by combining the USLE and the techniques of GIS and RS. The objective of the patent is to integrate USLE, mentioned-above techniques and digital elevation to automatically extract the soil erosion factors and calculate sediment delivery ratio, and then developed the sediment yield estimation system to calculate the spatial information and distribution of sediment yield in the watershed. The analyzed result can be used as the reference of sediment control in the watershed.

Description

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五、發明說明(1) 本發明之泥砂量推估專家系統(Sed Expert ),係以集水區 自動劃分理論結合G I S、R S技術與D E Μ資料,自動萃取土 °° 沖蝕因子,並結合坡面泥砂遞移率概念,推估集水區泥紗 產量之軟體,其技術領域、内容及實施方式說明如下:夕 一、技術領域 本發明之技術領域係屬於水土保持規劃設計及地理資訊系 統之空間分析領域之軟體發明。 二、先前技術V. Description of the invention (1) The silt amount estimation expert system (Sed Expert) of the present invention is based on the automatic division theory of catchment area, combined with GIS, RS technology and DE M data, and automatically extracts soil °° erosion factor, and combines The concept of the mud-sand transfer rate on the slope is used to estimate the software of mud yarn production in the catchment area. The technical fields, contents and implementation methods are described as follows: Xiyi Technical Field The technical field of the present invention belongs to soil and water conservation planning and design and geographic information systems. Software invention in the field of spatial analysis. Second, the prior art

通用 土壤流失公式(Universal Soil Loss Equation,Universal Soil Loss Equation (Universal Soil Loss Equation,

U S L E ),是目前世界各國最被廣泛使用之土壤沖钱預測公 式。其土壤沖蝕過程係由一系列因子量化和概算,在美國 應用的相當成功,其舆理論模式(如WEPP)不相同,無法適 用於任何地區,故在台灣地區使用此一公式評估土壤沖餘 量時,宜對沖蝕參數做適當之修正,使其配合台灣之自然 環境條件。早期土壤流失量評估係以小試驗樣區為對象,' 其因子取得大都來自於現場量測,隨著電腦科技之進步, 土壤沖餘模式結合G I S及R S技術已廣泛應用於大面積集水 區之評估,然目前評估方式仍以整個集水區或子集水區為 評估單元,其因子之代表性較為粗略,加上其參數因子未 能合理推求,而無法計算較精確之量化資訊(Wischmeier, 1 9 7 6 ;Wilson,1 986 ;Moore and Wilson,1 9 92 )。本發 明之集水區泥砂產量推估系統,為改進上述缺點,係以集 水區自動劃分理論為基礎,結合USLE模式及泥砂遞移率概U S L E) is currently the most widely used soil cash forecasting formula in countries around the world. The soil erosion process is quantified and estimated by a series of factors. It has been applied successfully in the United States. Its theoretical model (such as WEPP) is different and cannot be applied to any region. Therefore, this formula is used to evaluate soil erosion balance in Taiwan. When measuring, it is advisable to make appropriate corrections to the erosion parameters to match the natural environmental conditions in Taiwan. Early soil loss assessment was based on small test plots, and most of its factors were obtained from field measurements. With the advancement of computer technology, the soil surplus model combined with GIS and RS technology has been widely used in large-scale watersheds. Evaluation, but the current assessment method still uses the entire catchment area or sub-catchment area as the evaluation unit, and its factors are relatively rough. In addition, its parameter factors cannot be reasonably derived, and more accurate quantitative information cannot be calculated (Wischmeier , 1 9 7 6; Wilson, 1 986; Moore and Wilson, 1 9 92). In order to improve the above shortcomings, the silt production estimation system of the catchment area of the present invention is based on the theory of automatic division of catchment area, combined with the USLE model and the sediment transfer rate.

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* 1 I I 五、發明說明(2) 念進行泥砂量推估之軟體。 三、集水區坡面泥砂產量推估之内容 (一)坡面泥砂產量計算 土壤沖蝕模式可分為經驗模式(EmP iri cal Model )與理論 模式(Physical Model) wσ別您π取廣的υπϋ即為在 驗公式,其土壤沖姓過程係由一系列因子量化和概算,在 美國應用的相當成功,其與理論模式(如WEPP)不相同,無 法適用於任何地區,故在台灣地區使用此一公式評估土壤* 1 I I V. Description of the invention (2) Software for estimating the amount of mud and sand. 3. Contents of Estimation of Slope and Sand Yield in Catchment Area (I) Calculation of Slope and Sand Yield The soil erosion model can be divided into empirical model (EmP iri cal Model) and theoretical model (Physical Model). υπϋ is the formula under test. Its soil surname process is quantified and estimated by a series of factors. It is quite successful in the United States. It is different from the theoretical model (such as WEPP) and cannot be applied to any region. Therefore, it is used in Taiwan. This formula evaluates soil

沖蝕量時,宜對沖蝕參數做適當之修正,使其配合台灣之 自然環境條件。早期土壤流失量評估係以小試驗樣區為對 象’其因子取得大都來自於現場量測,隨著電腦科技之進 步’土壤沖触模式結合G IS及RS技術已廣泛應用於大面積 集水區之評估,目前評估方式仍以整個集水區或子集水區 為評估單元,其因子之代表性較為粗略,若將上述模 = 合G IS、RS技術與DEM資料之網格特性,以及利用集水^ = 水流向概念,則能有效地建立沖蝕因子資料庫二 砂災害之敏感區位。 釆I區泥 為能建立本土化之集水區泥 導之集水區自動劃分理論, USLE及泥砂遞移率概念,發 評估系統,並以圖形視窗介 方便操作之使用環境,以及 敏感區之決策資訊。本發明 砂產量評估系統,利用自行推 以集水區為評估單元,纟士人 展土壤流失量及坡面泥砂產旦 面為發展平台’提供初學者 管理者可迅速€得集“環境 之集水區泥砂推估以概念如In the case of erosion, appropriate modification of erosion parameters should be made to match the natural environmental conditions in Taiwan. Early soil loss assessment was based on small test plots. Most of its factors were obtained from field measurements. With the advancement of computer technology, the soil impact model combined with G IS and RS technology has been widely used in large-scale watersheds. In the current evaluation method, the entire catchment area or sub-catchment area is still used as the evaluation unit. The representativeness of the factors is relatively rough. If the above model is combined with the grid characteristics of G IS, RS technology and DEM data, and the use of Catchment ^ = water flow direction concept can effectively establish the sensitive area of the second sand disaster in the erosion factor database.泥 I mud is a theory of automatic division of water catchment area that can establish localized water catchment area. The concept of USLE and mud-sand transfer rate, development evaluation system, and graphical operating environment are used to facilitate the operation environment and sensitive area. Decision information. The sand production evaluation system of the present invention utilizes a self-propelled water catchment area as an evaluation unit, and the soil loss amount and the mud and sand production on the slopes are developed for the development platform. Water area sediment estimation is based on concepts such as

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五、發明說明(3) 圖一,其推估流程說明如下: 1 ·以目前台灣地區D Ε Μ資料之4 0 X 4 0 m網格大小為基礎’藉 由集水區自動劃分理論,計算無窪地流向、劃定集水區範 圍及萃取真實水系網分布,並分析集水區之地文水文資 訊,做為泥砂推估所需之空間資訊來源。 2·利用DEM及衛星影像資料,結合G IS及RS技術建立土壤沖 蝕因子資料庫,包括以線性克利金法内插集水區之降雨沖 蝕指數及土壤沖蝕指數;利用空間分析方法自動萃取網格 之漫地流長度及坡度,代入Wischmeier and Smith (1 9 7 8 )之公式,計算坡長及坡度因子;由衛星影像資料配 合土地利用資料’建立植生覆蓋因子(C)與帅¥1之轉換公 式,以迅速取得C因子資料庫。 3·以土壤流失量公式(USLE)計算集水區之土壤流失量,將 其乘上泥砂遞移率求得集水區之坡面泥砂產量,其空間分 布及量化資訊可進行分級,並配合衛星影像分類集水區主 要土地利用資料(林地、果樹類、蔬菜類、裸露地、水域 及雲),探討泥砂來源敏感區位,作為泥砂控制之決策參 (一)土壤沖钱模式及泥砂遞移率 _ 1 · 土壤沖蝕模式 (1 )降雨沖#指數(Rm) 降雨沖蝕指數之計算,係利用黃俊德(1 9 79 )所 沖蝕指數資料,以地理統計方法建立台灣地區 之降雨 °σ <年平均降V. Description of the invention (3) Figure 1. The estimation process is explained as follows: 1 Based on the current grid size of 40 × 40 m in D EM data in Taiwan, based on the theory of automatic division of catchment area, calculation The flow direction of non-depression, delineate the catchment area and extract the distribution of real water network, and analyze the geological and hydrological information of the catchment area as the source of spatial information needed for silt estimation. 2. Establish a soil erosion factor database using DEM and satellite imagery data, combined with G IS and RS technologies, including interpolation of rainfall erosion index and soil erosion index in the catchment area by linear Kriging method; use spatial analysis method to automatically Extract the diffuse flow length and slope of the grid and substitute it into the formula of Wischmeier and Smith (1978) to calculate the slope length and slope factor. Satellite image data and land use data are used to establish the vegetative cover factor (C) and Shuai. 1 conversion formula to quickly obtain the C-factor database. 3. Calculate the amount of soil loss in the catchment area by using the soil loss formula (USLE) and multiply it by the mud-sand transfer rate to obtain the mud-sand yield on the slope of the catchment area. The spatial distribution and quantitative information can be classified and coordinated. Satellite image classification of main land-use data in the catchment area (forest land, fruit trees, vegetables, bare land, waters and clouds), and to explore the sensitive locations of mud and sand sources as decision-making parameters for mud and sand control (I) Soil erosion model and mud transfer Rate _ 1 · Soil erosion model (1) Rainfall erosion index (Rm) The calculation of rainfall erosion index is based on the erosion index data from Huang Junde (1 79), and it is used to establish the rainfall in Taiwan by geostatistical method ° σ < annual average drop

200419045 五、發明說明(4) 雨沖餘指數等值圖。 (2) 土壤沖蝕性指數(Km) 土壤沖蝕性指數之計算係採用萬鑫森、黃俊義(丨98 i、 1 9 8 9 )所調查之台灣坡地土壤沖钱指數值,並以地理統計 方法建立台灣地區之土壤沖蝕指數等值圖。 (3 )坡長因子(L )200419045 V. Description of the invention (4) Equivalent graph of rain wash surplus index. (2) Soil erosion index (Km) The calculation of soil erosion index is based on the value of the soil erosion index in Taiwan slope land surveyed by Wan Xinsen and Huang Junyi (丨 98 i, 1 89). Methods Establish the equivalent map of soil erosion index in Taiwan. (3) Slope length factor (L)

Wi schmei er ( 1 9 76 )指出有效坡長為漫地流起點至坡度減緩 之處或至渠道之距離,通常不包含渠道之部份,且坡長易 受坡度減緩或土地利用改變等因素而截斷。wi ls〇n( 1 9 86 ) ,指出USLE之有效坡長常受到建物、道路或人工排水系統 等影響,其長度不會太長。一般而言,集水區坡面受到地 面窪蓄、入滲等作用,以及山溝、道路排水側溝等截流, 地表漫地流之流長甚少超過1〇〇ιη,加上一般坡地安全排 水,超過100m即需分段排水,否則逕流集中易形成蝕溝; 因此^發明利用數值高程模型資料,配合排水流向之觀 f ’萃取集水區漫地流與渠道流(為安全與方便計算,地 流長若超過1〇〇1"時,可視為渠道流)之空間分布。 =漫地流之流長,利用USLE坡長因子之算式,自 ί區之坡長因+,供坡面土壤流失量及泥砂產量 之合理评估(林昭遠、林文賜,1 9 9 9 )。 座ΐ 由於5平估集水區之地形丨I > 故““二用台灣地區數值高程模型,絪 格解析度為4 0 m X 4 0 m所產味 ^ 、、周 k π >从e \ ^ 玄可視為漫地流,以此來估篡隹 水區之坡長分布;累計流E初 异集 長超過兩個網格時視為渠道流。Wi schmeier (1976) pointed out that the effective slope length is the distance from the start of the diffuse flow to the place where the slope slows down or to the channel, which usually does not include the part of the channel, and the slope length is susceptible to factors such as slope slowdown or land use change. Truncate. wi lsoon (1986) pointed out that the effective slope length of USLE is often affected by buildings, roads or artificial drainage systems, and its length will not be too long. Generally speaking, the slope of the catchment area is affected by ground storage and infiltration, as well as the interception of ravines, road drainage side ditches, etc. The length of the diffuse surface flow is rarely more than 100m, plus the general safe drainage of slopes. If it exceeds 100m, drainage is needed in sections, otherwise runoff concentration is easy to form eroded ditch. Therefore, ^ the invention uses numerical elevation model data in conjunction with the observation of drainage flow direction f 'to extract the diffuse and canal flow in the catchment area (for safety and convenience calculation, the ground If the stream length exceeds 1001 ", it can be regarded as the channel distribution). = The length of the diffuse flow, using the formula of the USLE slope length factor, from the slope length factor + of the district, a reasonable assessment of the amount of soil loss and silt production on the slope surface (Lin Zhaoyuan, Lin Wenci, 1 9 9 9). Block ΐ Because the terrain of the catchment area is estimated at 5 levels 丨 I > "" Using a numerical elevation model in Taiwan, the resolution of the grid is 40 m X 4 0 m. ^,, Week k π > Xuan can be regarded as a diffuse flow to estimate the slope length distribution of the weird water area; the cumulative flow E is considered as a channel flow when the initial heterogeneous set length exceeds two grids.

200419045 I '·. 五、發明說明(5) (4) 坡度因子(S) 坡度因子係計算各網格之平均坡度(0)(Burrough,1986), 再代入S = 65.4sin20+4.56sin 0+0.0654 公式,以求得S值。 (5) 覆蓋與管理因子(C)200419045 I '.. V. Description of the invention (5) (4) Slope factor (S) The slope factor is used to calculate the average slope of each grid (0) (Burrough, 1986), and then substitute S = 65.4sin20 + 4.56sin 0+ 0.0654 formula to find the S value. (5) Coverage and management factor (C)

由於台灣地區之C值尚無資料庫可資利用,目前C因子取得 方式已逐漸由遙測影像來取代,利用土地利用判釋結果轉 換為C值,然影像判釋工作需專業之遙測操作人員及耗費 時間方能取得所需資訊,若能藉由綠色植生量之評估來產 生所需之C.值資料庫,將有效地縮短評估c值所需時間。本 發明,能,速取得C因子,利用遙測理論之植生指標來計 算覆盍與管理因子,有關NDVI值與C值之轉換公式為 C={( 1 -NDVI)/2}^(1+NDVI) (6 )水土保持處理因子(p) 水土 = 因子係以最危險狀態為考量,即假設在無任 何水土保持處理之狀態下(Ρ = 1)進行評估。 .泥砂遞移率 本研究之泥砂遞移 算坡面泥砂之遞移 所帶動,運移至渠 遞移率之定義,泥 點之泥砂貢獻量, 示,則網格上游流 率計算係採用網格分 率’假設坡面泥砂主 道(常流水)而流失。 砂遞移率可視為某格 若將泥砂貢獻量用網 入面積愈大,其產生 析方式,為簡易計 要係由坡面地表水 依此一假設及泥砂 點對最接近渠道袼 格上游流入面積表 的逕流量亦愈大,Since there is no database available for the C value in Taiwan, the current method of obtaining the C factor has been gradually replaced by telemetry images. The use of land use interpretation results is converted to C values. However, the interpretation of images requires professional telemetry operators and It takes time to obtain the required information. If the C. value database can be generated through the assessment of green vegetation, it will effectively reduce the time required to evaluate the c value. According to the present invention, the C factor can be obtained quickly, and the coverage and management factors are calculated using the vegetation index of the telemetry theory. The conversion formula of the NDVI value and the C value is C = {(1 -NDVI) / 2} ^ (1 + NDVI ) (6) Soil and water conservation treatment factors (p) Soil and water = Factors are considered in the most dangerous state, that is, the evaluation is performed without any soil and water conservation treatment (P = 1). Silt transfer rate The mud transfer in this study is driven by the transfer of the mud on the slope. The migration to the canal is defined by the transfer rate of mud and mud. The division rate 'assumes that the main road (often flowing water) on the slope is lost. The rate of sand migration can be regarded as a grid. If the contribution of mud and sand is used to increase the net area, the analysis method is generated. For simple calculation, it is based on the assumption that the surface water of the slope surface and the mud and sand point pair flow closest to the channel channel. The area table's runoff is also larger,

第12頁 200419045 五、發明說明(6) 愈能將泥砂帶至河道。因此,集水區坡面上任一格點之泥 砂遞移率,可視為該格點上游流入面積(A g r i d )與該格點 流至最接近渠道之上游流入面積(A t o t a 1 )之比值 (SDR = Agrid/Atotal)如圖二;意即濱水區愈靠近渠道之格 點,其坡面沖蝕之泥砂愈容易進入渠道,而增加河道之泥 砂產量,故泥砂遞移率愈高。集水區之坡面泥砂產量(Y s ) 可由集水區坡面土壤流失量(Am)與坡面泥砂遞移率(SDR) 之乘積(Ys = Am*SDR)來推算,藉由網格之排水流向可計算 每個網格之泥砂遞移率及泥砂量。 四、泥砂量推估專家系統 本軟體之研發係以集水區自動劃分理論為基礎,利用USLE 模式及泥砂遞移率概念,結合DEM資料及衛星影像資料, 利用專家系統推理介面,以程式撰寫泥砂量推估專家系統 (參圖三、四、五及六),其成果主要應用在土壤流失量及 坡面泥砂產量之推估,並以德基水庫集水區進行實例分析 (參圖七、八、九及十),可為驗證本發明之實用性。Page 12 200419045 V. Description of the invention (6) The mud and sand can be brought to the river channel more and more. Therefore, the sediment transfer rate of any grid point on the slope of the catchment area can be regarded as the ratio of the upstream inflow area (A grid) of the grid point to the upstream inflow area (A tota 1) of the grid flow to the closest channel ( (SDR = Agrid / Atotal) is shown in Figure 2. This means that the closer the waterfront is to the grid point of the channel, the easier it is for the erosion of the sand on the slope to enter the channel, and increase the sediment production of the river, so the mud transfer rate is higher. Yield (Y s) on the slope of the catchment area can be calculated from the product of the slope soil loss (Am) and the slope sediment transfer rate (SDR) (Ys = Am * SDR) in the catchment area. The drainage flow direction can calculate the sediment transfer rate and the amount of sediment in each grid. 4. Sediment estimation expert system The development of this software is based on the theory of automatic division of catchment area, using the USLE model and the concept of sediment transfer rate, combining DEM data and satellite image data, using the inference interface of the expert system, and writing the program The silt volume estimation expert system (see Figures 3, 4, 5, and 6), the results of which are mainly applied to the estimation of soil erosion and slope sediment production, and the example analysis of the watershed of Deji Reservoir (see Figure 7) , Eight, nine and ten), can be used to verify the practicality of the present invention.

第13頁 200419045Page 13 200419045

第14頁 200419045 圖式簡單說明Page 14 200419045 Schematic description

?......................................................... 疒狳、齡游似?私.鮮久兄叫贫祕 Γ——__·—·..· —^………m •••/AWAWAWAW·····:*»書. ::v::::5 C资?•孤效·ί^Χ:<·綱? ?、心%««贫杯 3 [ '3 承上..# | \ ·,,,··· •SSSVA气、為·· V ····,·· ν^ΛνΛΜΛ·^^Λ(ΜΛ·ιΛήΛί· ,· · •,//·>·············,·····················»·····‘·【· 圖三、泥砂量推估專家系統(Rm及Km因子)? ....................................... ........ 疒 、, like you? You private. Xianjiu brother called poor secret Γ ——__ · — · .. · — ^ ……… m ••• / AWAWAWAW ···· :: * »书. :: v :::: 5 C resource? • Solitary effect · ί ^ Χ: < · Gang? 、 Heart% «« Poor Cup 3 ['3 承 上 .. ## \ \ ,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,,, SSSSVA ιΛήΛί ····, // · > ····························· ··· '· [· Figure 3. Expert system for estimating sediment volume (Rm and Km factors)

_圖四、泥砂量推估專家系統(L及S因子) iBi 第15頁 200419045 圖式簡單說明_Figure 4. Expert system for estimating the amount of mud and sand (L and S factors) iBi Page 15 200419045 Schematic illustration

圖五、泥砂量推估專家系統(C及P因子)Figure 5. Expert system for estimation of sediment volume (C and P factors)

_圖六、泥砂量推估專家系統(沖蝕深度計算) IHi 第16頁 200419045 圖式簡單說明_Figure 6. Expert system for estimating the amount of mud and sand (calculation of erosion depth) IHi Page 16 200419045 Schematic description

圖七、德基水庫集水區之C值分布圖Figure VII. C value distribution of Deji reservoir catchment area

_圖八、德基水庫集水區之泥砂遞移率分布 1B1 第17頁 200419045 圖式簡單說明_Figure 8. Distribution of mud and sand transfer rate in the catchment area of Deji Reservoir 1B1 page 17 200419045

土壤波失發 Or祕、ki/jc〇 <m 29mm 縱屬娜说 wzm 狐篇.¾ 11 »!〇(» \m.m _ >腦!0期4 {%) M-7S% ZSi% ^26% 475% 3麗 m.n% 圖九、德基水庫集水區土壤流失量分佈圖 /rf:S4 π ^ m· ·...…· jiS\._~#奮气身、⑼ □—::㈣::臟^ S S 5:S 30^ mm om寫 驪S澀S \:/ m_ 贫分比 {%) t,/w 圖十、德基水庫集水區坡面泥秒產量分布圖Soil wave loss Or secret, ki / jc〇 < m 29mm Longitudinal Na said wzm Fox articles. ¾ 11 »! 〇 (» \ mm _ > Brain! 0 period 4 (%) M-7S% ZSi% ^ 26% 475% 3% mn% Figure IX. Distribution map of soil loss in the watershed of Deji Reservoir / rf: S4 π ^ m · · ...... jiS \ ._ ~ # fenqi body, ⑼ ————: : ㈣ :: dirty ^ SS 5: S 30 ^ mm om write 骊 S 涩 S \: / m_ lean fraction ratio (%) t, / w Figure 10: Distribution of mud-second output on the slope of Deji Reservoir watershed

第18頁 200419045Page 18 200419045

1· USLE模式因子之分析 目前有關USLE模式因子之公也 f m 、U于之77析大都以子集水區或整個集水 之空間分析技術,萨由刚之/並、“地理=貝訊系統 + Λ“ π而η 9 Μ貝枓及衛星影像資料自動萃取 "' 而*子,並由集水區自動劃分理論將尺度延伸 至集水區,推估集水區之土壌沖蝕之空間分布情形。 2 ·坡面泥砂遞移率 _ 長期以來,有關泥砂遞移率之計算係以河川為±,並以概 略值代表整個集水區,本發明由泥砂遞移率定義推導面積 比概念,肖合DEM資料,配合排水流向資料以網格分析方、 式自動計算坡面泥砂遞移率,乘以上述之土壤沖蝕量,可 推估坡面泥砂產量及計算集水區之土壤沖蝕深度。 3 ·坡面泥砂產量推估 利用自行推導之集水區自動劃分理論,以集水區為評估單 元結合USLE及泥砂遞移率概念,發展土壤流失量及坡面 泥砂產量評估系統,並以圖形視窗介面為發展平台,提供 初學者可方便操作之使用環境,以及管理者可迅速獲得集 水區環境敏感區之決策資訊。 4 ·由於本發明可改進以往的缺點,實屬可靠且易推廣的方 並配合專家系統概念進行程式撰寫建立泥砂量推估專 家系統(SedExpert),運用上述方法結合DEM資料,可迅速1. Analysis of USLE model factors The current analysis of USLE model factors is fm and U. Most of them use spatial analysis techniques of subcatchments or the entire catchment. + Λ "π and η 9 Μ 枓 and automatic extraction of satellite image data" "and *, and the theory of automatic division of the catchment area extends the scale to the catchment area to estimate the soil erosion space in the catchment area Distribution situation. 2 · Slope silt transfer rate _ For a long time, the calculation of silt transfer rate is based on the river ±, and represents the entire catchment area with rough values. The present invention derives the concept of area ratio from the definition of silt transfer rate. Xiao He DEM data, combined with drainage flow direction data, automatically calculates the slope sediment transfer rate in a grid analysis method and multiplies the above-mentioned soil erosion amount to estimate the slope sediment yield and calculate the soil erosion depth in the catchment area. 3. Estimation of slope mud production Using the self-derived automatic catchment area division theory, taking the catchment area as the evaluation unit and combining the concepts of USLE and mud transfer rate, develop a system for evaluating soil erosion and slope mud production, and use graphics The window interface is a development platform, providing a convenient operating environment for beginners, and managers can quickly obtain decision-making information on environmentally sensitive areas in the catchment area. 4 · Since the present invention can improve the past disadvantages, it is a reliable and easy to popularize method. It can cooperate with the concept of the expert system to write a program and establish an expert system for estimating sediment volume (SedExpert).

第19頁 200419045 六、申請專利範圍 推估集水區土壤流失量、坡面泥砂產量之量化資訊及空間 分布,做為集水區泥砂控制及治理之參考依據。Page 19 200419045 VI. Scope of patent application Quantitative information and spatial distribution of soil loss in the catchment area and silt production on the slope are estimated as the reference basis for sediment control and treatment in the catchment area.

Claims (1)

200419045 六、申請專利範圍 1· 一種用於計算土壤沖蝕因子(USLE因子)之網袼分析方 法 目岫有關USLE模式因子之分析大都以子集水區或整個集水 區為單元’本發明係以網格為單元,並結合地理資訊系統 之空間分析技術,藉由DEM資料及衛星影像資料自動萃取 土壤冲餘所需因子’並由集水區自動劃分理論將尺度延伸 至集水區,推估集水區之土壤沖蝕之空間分布情形。 2 · —種用於計算坡面泥砂遞移率之方法 長期以來,有關泥砂遞移率之計算係以河川為主,並以概 略值代表整個集水區,本發明由泥砂遞移率定義推導面積 比概念,結合DEM資料,配合排水流向資料以網格分析方、 式自動計算坡面泥砂遞移率,乘以上述之土壤沖蝕量, 推估坡面泥砂產量及計算集水區之土壤沖蝕深度。 3. 種_用於推估集水區坡面泥砂產重之方法 利用i:推導之集水區自動劃分理論,以集水區為評估覃 “、、二usiE及泥砂遞移率概念,發展土壤流失ϊ::: =二 > 二=#二統,並以圖形視窗介面為發展平台,提# 年刀學者可方便择彳々 從供 7Jc P ^ r 之使用環境,以及管理者可迅速獲得隹 水區裱境敏感區之決策資1 〜侍集 4 ·如申請專利範 之逐步推理機制 園第1項至第3項的方法,結合專家系統 以程式撰寫整合上述方法建立泥砂量'推200419045 VI. Scope of patent application 1. A network analysis method for calculating soil erosion factor (USLE factor). The analysis of USLE model factors is mostly based on sub-catchments or the entire catchment. The grid is used as a unit, combined with the geographic analysis system's spatial analysis technology. The DEM data and satellite image data are used to automatically extract the factors required for soil surplus and the automatic catchment theory is used to extend the scale to the catchment area. Estimate the spatial distribution of soil erosion in the catchment area. 2 · —A method for calculating the rate of mud and sand transfer on slopes For a long time, the calculation of the rate of mud and sand transfer has been dominated by rivers and represents the entire catchment area with rough values. The invention derives from the definition of mud and sand transfer rate Area ratio concept, combined with DEM data, combined with drainage flow data, automatically calculates the slope sediment transfer rate by grid analysis method, multiplies the soil erosion amount mentioned above, estimates the slope sediment production and calculates the soil in the catchment area Erosion depth. 3. Kind of method for estimating the weight of mud and sand on the slope of the catchment area. Using i: Derived theory of automatic division of catchment area, taking the catchment area as an assessment of the concepts of Tan, UsiE, and the rate of mud-sand migration, develop Soil Erosion ::: = 二 > 二 = # 二 统, and using the graphical window interface as a development platform, #niandao scholars can easily choose from the use environment for 7Jc P ^ r, and managers can quickly Obtain decision-making resources 1 ~ 4 in the sensitive area of Laishui District 4 · For example, the method of item 1 to 3 of the step-by-step reasoning mechanism park for patent application, combined with the expert system to programmatically integrate the above method to establish the amount of mud and sand 第18頁 2004d9045 六、申請專利範圍 佑專家系統(SedExpert),結合DEM資料及衛星影像資料, 可迅速推估集水區土壤流失量、坡面泥砂產量之量化資訊 及空間分布,做為集水區泥砂控制及治理之參考依據。Page 18 2004d9045 VI. Patent application scope SedExpert, combined with DEM data and satellite image data, can quickly estimate the quantitative information and spatial distribution of soil erosion in the catchment area and the amount of mud and sand on the slope, as the catchment The reference basis for the area's sand control and treatment. 第19頁Page 19
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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103942408A (en) * 2014-02-19 2014-07-23 西北农林科技大学 Annual erosion sediment yield model calculation method of mesoscale drainage basin of loess plateau
TWI476620B (en) * 2009-03-05 2015-03-11 Univ Nat Chunghsing Estimation method and system of soil erosion in catchment area
US20150105984A1 (en) * 2013-10-15 2015-04-16 Deere & Company Agricultural harvester configured to control a biomass harvesting rate based upon soil effects
CN107860890A (en) * 2017-11-03 2018-03-30 中国农业科学院农业环境与可持续发展研究所 A kind of sloping upland topsoil soils quality diagnosis method
CN108896473A (en) * 2018-06-06 2018-11-27 黄河水利委员会黄河水利科学研究院 Couple the Erosion and Sediment Production in Watershed amount prediction technique of different time and space scales model
CN108896735A (en) * 2018-06-29 2018-11-27 中国水利水电科学研究院 A kind of rainfall erosivity factor improved method and system calculated towards the soil erosion
CN109239309A (en) * 2018-08-13 2019-01-18 重庆工商大学 A kind of prediction soil erosion modulus method that GIS and deep learning combine
CN109632254A (en) * 2018-11-23 2019-04-16 西安理工大学 River load infusion route under a kind of Influence of Water Conservancy Projects of dam library determines method
CN109682952A (en) * 2019-02-21 2019-04-26 生态环境部南京环境科学研究所 Pollution of area source measures system

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI476620B (en) * 2009-03-05 2015-03-11 Univ Nat Chunghsing Estimation method and system of soil erosion in catchment area
US20150105984A1 (en) * 2013-10-15 2015-04-16 Deere & Company Agricultural harvester configured to control a biomass harvesting rate based upon soil effects
US10362733B2 (en) * 2013-10-15 2019-07-30 Deere & Company Agricultural harvester configured to control a biomass harvesting rate based upon soil effects
CN103942408A (en) * 2014-02-19 2014-07-23 西北农林科技大学 Annual erosion sediment yield model calculation method of mesoscale drainage basin of loess plateau
CN107860890A (en) * 2017-11-03 2018-03-30 中国农业科学院农业环境与可持续发展研究所 A kind of sloping upland topsoil soils quality diagnosis method
CN108896473A (en) * 2018-06-06 2018-11-27 黄河水利委员会黄河水利科学研究院 Couple the Erosion and Sediment Production in Watershed amount prediction technique of different time and space scales model
CN108896473B (en) * 2018-06-06 2021-01-01 黄河水利委员会黄河水利科学研究院 River basin erosion sand yield prediction method coupled with different space-time scale models
CN108896735A (en) * 2018-06-29 2018-11-27 中国水利水电科学研究院 A kind of rainfall erosivity factor improved method and system calculated towards the soil erosion
CN109239309A (en) * 2018-08-13 2019-01-18 重庆工商大学 A kind of prediction soil erosion modulus method that GIS and deep learning combine
CN109632254A (en) * 2018-11-23 2019-04-16 西安理工大学 River load infusion route under a kind of Influence of Water Conservancy Projects of dam library determines method
CN109682952A (en) * 2019-02-21 2019-04-26 生态环境部南京环境科学研究所 Pollution of area source measures system

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