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Technical Commission VIII (B8)

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Bibliographic data

fullscreen: Technical Commission VIII (B8)

Multivolume work

Persistent identifier:
1663813779
Title:
XXII ISPRS Congress 2012
Sub title:
Melbourne, Australia, 25 August-1 September 2012
Year of publication:
2013
Place of publication:
Red Hook, NY
Publisher of the original:
Curran Associates, Inc.
Identifier (digital):
1663813779
Language:
English
Additional Notes:
Kongress-Thema: Imaging a sustainable future
Corporations:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Adapter:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Founder of work:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Other corporate:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Document type:
Multivolume work

Volume

Persistent identifier:
1663822514
Title:
Technical Commission VIII
Scope:
590 Seiten
Year of publication:
2014
Place of publication:
Red Hook, NY
Publisher of the original:
Curran Associates, Inc.
Identifier (digital):
1663822514
Illustration:
Illustrationen, Diagramme
Signature of the source:
ZS 312(39,B8)
Language:
English
Additional Notes:
Erscheinungsdatum des Originals ist ermittelt.
Literaturangaben
Usage licence:
Attribution 4.0 International (CC BY 4.0)
Editor:
Shortis, M.
Shimoda, H.
Cho, K.
Corporations:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Adapter:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Founder of work:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Other corporate:
International Society for Photogrammetry and Remote Sensing, Congress, 22., 2012, Melbourne
International Society for Photogrammetry and Remote Sensing
Publisher of the digital copy:
Technische Informationsbibliothek Hannover
Place of publication of the digital copy:
Hannover
Year of publication of the original:
2019
Document type:
Volume
Collection:
Earth sciences

Chapter

Title:
[VIII/8: Land]
Document type:
Multivolume work
Structure type:
Chapter

Chapter

Title:
SEDIMENT YIELD ESTIMATION AND PRIORITIZATION OF WATERSHED USING REMOTE SENSING AND GIS Sreenivasulu Vemu, Udaya Bhaskar Pinnamaneni
Document type:
Multivolume work
Structure type:
Chapter

Contents

Table of contents

  • XXII ISPRS Congress 2012
  • Technical Commission VIII (B8)
  • Cover
  • Title page
  • [Inhaltsverzeichnis]
  • [VIII/1:]
  • [VIII/2: Health]
  • [VIII/3: Atmosphere, Climate and Weather]
  • [VIII/4: Water]
  • [VIII/5: Energy and Solid Earth]
  • [VIII/6: Agriculture, Ecosystems and Bio-Diversity]
  • [VIII/7: Forestry]
  • [VIII/8: Land]
  • CLASSIFICATION AND MODELLING OF URBAN MICRO-CLIMATES USING MULTISENSORAL AND MULTITEMPORAL REMOTE SENSING DATA B. Bechtel, T. Langkamp, J. Böhner, C. Daneke, J. Oßenbrügge, S. Schempp
  • GULLIES, GOOGLE EARTH AND THE GREAT BARRIER REEF: A REMOTE SENSING METHODOLOGY FOR MAPPING GULLIES OVER EXTENSIVE AREAS U. Gilad, R. Denham and D. Tindall
  • IMPROVEMENT OF THERMAL ESTIMATION AT LAND COVER BOUNDARY BY USING QUANTILE Tsukasa Hosomura
  • TRAJECTORY ANALYSIS OF FOREST CHANGES IN NORTHERN AREA OF CHANGBAI MOUNTAINS, CHINA FROM LANDSAT TM IMAGE F. Huang, H. J. Zhang, P. Wang
  • DEVELOPMENTS IN MONITORING RANGELANDS USING REMOTELY-SENSED CROSS-FENCE COMPARISONS Adam D. Kilpatrick, Stephen C. Warren-Smith, John L. Read, Megan M. Lewis, Bertram Ostendorf
  • OPERATIONAL OBSERVATION OF AUSTRALIAN BIOREGIONS WITH BANDS 8-19 OF MODIS B. K. McAtee, M. Gray, M. Broomhall, M. Lynch, P. Fearns
  • SPECTRAL UNMIXING OF BLENDED REFLECTANCE FOR DENSER TIME-SERIES MAPPING OF WETLANDS Ryo Michishita, Zhiben Jiang, Bing Xu
  • AUTOMATED CONSTRUCTION OF COVERAGE CATALOGUES OF ASTER SATELLITE IMAGE FOR URBAN AREAS OF THE WORLD Hiroyuki Miyazaki, Koki Iwao, Ryosuke Shibasaki
  • QUANTIFYING LAND USE/COVER CHANGE AND LANDSCAPE FRAGMENTATION IN DANANG CITY, VIETNAM: 1979-2009 N. H. K. Linh, S. Erasmi, M. Kappas
  • HIGH TEMPORAL FREQUENCY BIOPHYSICAL AND STRUCTURAL VEGETATION INFORMATION FROM MULTIPLE REMOTE SENSING SENSORS CAN SUPPORT MODELLING OF EVENT BASED HILLSLOPE EROSION IN QUEENSLAND B. Schoettker, R. Searle, M. Schmidt, S. Phinn
  • REMOTE SENSING TECHNIQUES AS A TOOL FOR ENVIRONMENTAL MONITORING Kamil Faisal, Mohamed AlAhmad, Ahmed Shaker
  • DETECTING SLUMS FROM QUICK BIRD DATA IN PUNE USING AN OBJECT ORIENTED APPROACH Sulochana Shekhar
  • GLOBAL LAND COVER CLASSIFICATION USING MODIS SURFACE REFLECTANCE PRODUCTS Haruhisa Shimoda, Kiyonari Fukue
  • SEDIMENT YIELD ESTIMATION AND PRIORITIZATION OF WATERSHED USING REMOTE SENSING AND GIS Sreenivasulu Vemu, Udaya Bhaskar Pinnamaneni
  • CLOUD DETECTION BASED ON DECISION TREE OVER TIBETAN PLATEAU WITH MODIS DATA Lina Xu, Shenghui Fang, Ruiging Niu, Jiong Li
  • [VIII/9: Oceans]
  • [VIII/10: Cryosphere]
  • Cover

Full text

2. STUDY AREA 
The Indravati is one of the northern tributaries of the Godavari 
in its lower reach. The Indravati catchment lies between 
latitudes 18 27' N to 20 41' N and longitudes 80° 05" E to 83° 
07° E (Figure 1). The river Indravati rises at an altitude of about 
914 m near Thuamal Rampur village in the Kalahandi district 
of Orissa on the western slopes of the Eastern Ghats and joins 
Godavari at an altitude of about 125 m. The main river flows 
for a length of about 477 Km. The Indravati basin with a 
catchment area of 41285 Km? constitutes 13.32 % of the total 
Godavari basin. The basin has high hills, deep valleys and large 
plateaus. The mean annual rainfall in of this area is about 1288 
mm, most of which occurs between May and September. 
Average potential evaporation rates are 6.5 mm per day, while 
average minimum and maximum temperature are 13°C and 39 
‘C respectively. There are no major irrigation projects existing 
in the study area. The major land covers in the catchment are 
forest (68 %), followed by agriculture (22 96). Agriculture is the 
main occupation of the people in the area. 
  
Basin-sub basin map of India 
Godavari Basin 
  
  
XC NS 
60 km 
  
  
  
  
  
  
Figure 1. Location map of Indravati Catchment 
3. METHODOLOGY 
3.1 Soil Erosion Model - USLE 
Techniques for prediction of soil loss have evolved over the 
years. The most widely used equation for soil loss prediction of 
the catchment is the Universal Soil Loss Equation (USLE). The 
USLE equation computes average annual soil loss (A) which is 
a product of five different factors that affect soil loss, and is 
given by: 
A-RKLSCP (1) 
  
     
    
   
     
    
    
   
    
  
  
  
   
   
    
    
   
  
  
    
  
  
  
   
    
   
  
  
  
  
  
  
  
    
   
  
   
    
  
    
   
   
     
   
   
  
  
    
  
   
   
International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XXXIX-B8, 2012 
XXII ISPRS Congress, 25 August - 01 September 2012, Melbourne, Australia 
Where, À = average annual soil loss in tons per hectare, R = 
rainfall-runoff erosivity factor (MJ/ha.mm/h), K = soil 
erodibility factor (t.ha.h/ha/MJ/mm), LS = topographic or slope 
length/steepness factor, C = cover and cropping-management 
factor, P = supporting practices (land use) factor. All of the 
factors are dimensionless, with the exception of R and K. The 
preparation of spatial data base for this model is explained 
below. 
3.1.1 Rainfall Erosivity Factor (R): The erosivity factor 
R is often determined from rainfall intensity if such data are 
available. In majority of cases rainfall intensity data are very 
rare, consequently attempts have been made to determine 
erosivity from daily rainfall data (Jain er al., 2001). In River 
Indravati catchment, no station has rainfall intensity data. 
Therefore R is determined using mean annual rainfall as 
recommended by Morgan and Davidson (1991). The expression 
is given below. 
R=P*05 Q) 
Where, P = mean annual rainfall in mm and R = rainfall 
erosivity factor in MJ/ha.mm/h. A 20-year time series of 
monthly girded average precipitation dataset from the Climatic 
Research Unit -Average Climatology 2.0 (CRU-CL 2.0) 
(http-//Www.cru.uea.ac.uk/cru/data/tmc.htm) from 1982 to 2002 
is used in preparing R factor layer. Inverse distance method, 
which is very fast and efficient weighted average interpolation 
method in ILWIS, is used to show spatial distribution of mean 
R factor values in Indravati catchment. 
3.1.2 Soil Erodibility Factor (K): The soil erodibility 
factor (K) represents both susceptibility of soil to erosion and 
the amount and rate of runoff, as measured under standard plot 
condition. In the study area no detailed soil map in the large 
scale is available. The soil map prepared by National Atlas and 
Thematic Mapping Organization, Department of Science and 
Technology, Government of India on 1: 2 Million scale is used 
to prepare K factor. 
3.1.3 Slope length and steepness factor (LS): The 
topography affects the runoff characteristics and transport 
processes of sediment on a watershed scale. A 90 m resolution 
DEM from the Shuttle Radar Topography Mission (SRTM) is 
downloaded from ftp;//eOmss21u.ecs.nasa.gov/srtm/ , and gaps 
of no data is filled with coarser Gtopo 30 DEM 
(http/pdaac.usgs.gov/etopo30/hvdro/index.asp).This rectified 
90 m resolution DEM is used to prepare the LS factor as 
discussed below. 
Slope Length Factor (L); Mc Cool et al. (1987) presented 
the following relationship to compute the slope length or L 
factor: 
L = (W22.1)" (3) 
where L = slope length factor; À = field slope length (m); m = 
dimensionless exponent that depends on slope steepness, being 
0.5 for slopes exceeding 5 percent, 0.4 for 4 percent slopes and 
0.3 for slopes less than 3 percent. A grid size of 100 m is used 
as field slope length (4). Similar assumption of field slope 
   
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