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Remote sensing for resources development and environmental management (Volume 1)

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CC BY: Attribution 4.0 International. You can find more information here.

Bibliographic data

fullscreen: Remote sensing for resources development and environmental management (Volume 1)

Multivolume work

Persistent identifier:
856342815
Title:
Remote sensing for resources development and environmental management
Sub title:
proceedings of the 7th international Symposium, Enschede, 25 - 29 August 1986
Year of publication:
1986
Place of publication:
Rotterdam
Boston
Publisher of the original:
A. A. Balkema
Identifier (digital):
856342815
Language:
English
Additional Notes:
Volume 1-3 erschienen von 1986-1988
Editor:
Damen, M. C. J.
Document type:
Multivolume work

Volume

Persistent identifier:
856343064
Title:
Remote sensing for resources development and environmental management
Sub title:
proceedings of the 7th international Symposium, Enschede, 25 - 29 August 1986
Scope:
XV, 547 Seiten
Year of publication:
1986
Place of publication:
Rotterdam
Boston
Publisher of the original:
A. A. Balkema
Identifier (digital):
856343064
Illustration:
Illustrationen, Diagramme
Signature of the source:
ZS 312(26,7,1)
Language:
English
Usage licence:
Attribution 4.0 International (CC BY 4.0)
Editor:
Damen, M. C. J.
Publisher of the digital copy:
Technische Informationsbibliothek Hannover
Place of publication of the digital copy:
Hannover
Year of publication of the original:
2016
Document type:
Volume
Collection:
Earth sciences

Chapter

Title:
3 Spectral signatures of objects. Chairman: G. Guyot, Liaison: N. J. J. Bunnik
Document type:
Multivolume work
Structure type:
Chapter

Chapter

Title:
Multitemporal analysis of Thematic Mapper data for soil survey in Southern Tunisia. G. F. Epema
Document type:
Multivolume work
Structure type:
Chapter

Contents

Table of contents

  • Remote sensing for resources development and environmental management
  • Remote sensing for resources development and environmental management (Volume 1)
  • Cover
  • Title page
  • Title page
  • Title page
  • Preface
  • Organization of the Symposium
  • Working Groups
  • Table of contents
  • 1 Visible and infrared data. Chairman: F. Quiel, Liaison: N J. Mulder
  • 2 Microwave data. Chairman: N. Lannelongue, Liaison: L. Krul
  • 3 Spectral signatures of objects. Chairman: G. Guyot, Liaison: N. J. J. Bunnik
  • Relationship between soil and leaf metal content and Landsat MSS and TM acquired canopy reflectance data. C. Banninger
  • The conception of a project investigating the spectral reflectivity of plant targets using high spectral resolution and manifold repetitions. F. Boochs
  • CAESAR: CCD Airborne Experimental Scanner for Applications in Remote Sensing. N. J. J. Bunnik & H. Pouwels, C. Smorenburg & A. L. G. van Valkenburg
  • LANDSAT TM band combinations for crop discrimination. Sherry Chou Chen, Getulio Teixeira Batista & Antonio Tebaldi Tardin
  • The derivation of a simplified reflectance model for the estimation of LAI. J. G. P. W. Clevers
  • The application of a vegetation index in correcting the infrared reflectance for soil background. J. G. P. W. Clevers
  • The use of multispectral photography in agricultural research. J. G. P. W. Clevers
  • TURTLE and HARE, two detailed crop reflection models. J. A. den Dulk
  • Sugar beet biomass estimation using spectral data derived from colour infrared slides. Robert R. De Wulf & Roland E. Goossens
  • Multitemporal analysis of Thematic Mapper data for soil survey in Southern Tunisia. G. F. Epema
  • Insertion of hydrological decorralated data from photographic sensors of the Shuttle in a digital cartography of geophysical explorations (Spacelab 1-Metric Camera and Large Format Camera). G. Galibert
  • Spectral signature of rice fields using Landsat-5 TM in the Mediterranean coast of Spain. S. Gandia, V. Caselles, A. Gilabert & J. Meliá
  • The canopy hot-spot as crop identifier. S. A. W. Gerstl, C. Simmer & B. J. Powers
  • An evaluation of different green vegetation indices for wheat yield forecasting. A. Giovacchini
  • Spectral and botanical classification of grasslands: Auxois example. C. M. Girard
  • The use of Thematic Mapper imagery for geomorphological mapping in arid and semi-arid environments. A. R. Jones
  • Determination of spectral signatures of different forest damages from varying altitudes of multispectral scanner data. A. Kadro
  • A preliminary assessment of an airborne thermal video frame scanning system for environmental engineering surveys. T. J. M. Kennie & C. D. Dale, G. C. Stove
  • Study on the spectral radiometric characteristics and the spectrum yield model of spring wheat in the field of BeiAn city, HeilonJiang province, China (primary report). Ma-Yanyou, You-Bochung, Guo-Ruikuan, Lin-Weigang & Mo-Hong
  • Multitemporal analysis of LANDSAT Multispectral Scanner (MSS) and Thematic Mapper (TM) data to map crops in the Po valley (Italy) and in Mendoza (Argentina). M. Menenti & S. Azzali, D. A. Collado & S. Leguizamon
  • Selection of bands for a newly developed Multispectral Airborne Reference-aided Calibrated Scanner (MARCS). M. A. Mulders, A. N. de Jong, K. Schurer, D. de Hoop
  • Mapping of available solar radiation at ground. Ehrhard Raschke & Martin Rieland
  • Spectral signatures of soils and terrain conditions using lasers and spectrometers. H. Schreier
  • Relation between spectral reflectance and vegetation index. S. M. Singh
  • On the estimation of the condition of agricultural objects from spectral signatures in the VIS, NIR, MIR and TIR wavebands. R. Söllner, K.-H. Marek & H. Weichelt, H. Barsch
  • LANDSAT temporal-spectral profiles of crops on the South African Highveld. B. Turner
  • Theoretic reflection modelling of soil surface properties. B. P. J. van den Bergh & B. A. M. Bouman
  • Monitoring of renewable resources in equatorial countries. R. van Konijnenburg, Mahsum Irsyam
  • Assessment of soil properties from spectral data. G. Venkatachalam & V. K. R. Jeyasingh
  • Spectral components analysis: Rationale and results. C. L. Wiegand & A. J. Richardson
  • 4 Renewable resources in rural areas: Vegetation, forestry, agriculture, soil survey, land and water use. Chairman: J. Besenicar, Liaisons: M. Molenaar, Th. A. de Boer
  • Cover

Full text

non occured 
if all. 
a occurence 
t is also 
*ven in the 
a fourth 
jctance if 
aughness of 
on of the 
of Landsat 
Since sand 
part of the 
. present, 
a will in 
in January, 
s, where in 
to estimate 
reflectance 
have to be 
ar in place 
the surface 
n of rain, 
tion dates 
iay and 60 
¡rences in 
o days may 
lith angle 
nee at the 
lectance. 
iting these 
tterman and 
and Ohring 
hip between 
bedo (ax; 
e) can* 3 be 
985) by: 
1 (1985) to 
olar zenith 
1 a and b 
grees solar 
reflectance 
diance will 
angle and 
he two-way 
wo factors. 
wavelength 
Lbedo bands 
ant bands. 
id two-way 
L turbidity 
ingles of 29 
d by Koepke 
A soil surface is an imperfect diffuse reflector. 
Therefore the reflection behaviour will be a 
function of relative magnitude of diffuse and 
direct radiation and of solar zenith angle 
(Makarova et al (1973), after Kondratyev et al 
1981). Bartman (1980) and Larson and Barkstrom 
(1977) established maps in which the surface 
reflectance at a certain solar zenith angle is 
converted to standard reflectance. This formula 
implies a relatively large influence of solar 
zenith angle due to the non diffuse behaviour of 
natural surfaces. Applying this formula a standard 
surface reflectance of for instance 20.0 percent 
would give for a solzr zenith angle of 60 degrees a 
sun dependent reflectance of 22.0 and for 29 
degrees of 16.3 percent. These formulas are 
probably dependent of the type of surface and 
wavelength. 
With increasing solar zenith angle the amount of 
shadow will increase especially in rough areas and 
areas with a high drainage density. Although an 
higher amount of shadow at a certain sun elevation, 
will lead to a decrease in reflectance this effect 
will be counteracted by the difference between the 
solar zenith angle dependent reflectance of May and 
January. Sloping areas with various expositions 
will react different from relatively flat areas. 
Finally it must be noted that the reflectance of 
parts of the playa with hygroscopic salts are a 
function of the time of the day and hence of the 
time of Landsat overpass. 
4. CONVERSION OF JANUARY AND MAY DATA 
The reflectance values calculated for the top of 
the atmosphere cannot be compared directly. As is 
shown, these values can be converted to reflectance 
at the surface, if turbidity, as a function of 
wavelength and solar zenith angle, are known. But 
even in that case, reflectance values have to be 
corrected for sun elevation to get comparable data 
for both days. 
Since there is much uncertainty in these 
calculations other approaches are to be followed. 
These may be the assumption that the upper and 
lower limits or the PI and P99 of both data sets 
are equal. It can also be assumed that the shape of 
the feature space plots are comparable. Another way 
is the selection of reference surfaces which are 
constant for both days. 
All approaches have disadvantages: 
- Upper and lower limits for both dates are not 
necessarily the same. One of the days may have 
lower or higher reflectance values, for instance 
due to the fact that very wet surfaces or sealed 
surfaces are present in May or January. The 
advantage of using PI and P99 is laid in the fact 
that the influence of misregistrations is 
minimized. 
- The assumption of similar shapes of the feature 
space may be wrong. 
- Reflectance of reference objects may not be 
constant. 
In order to compare the results of calculations, 
reflectance values of May are converted in values 
comparable with the January data. 
Ultimately that approach has been adopted in 
which a reference object has been chosen, since 
this will give the most reliable results. A part of 
the footslope area with low relief intensity has 
been selected. There may be some changes in 
reflectance due to the influence of vegetation of 
this object. The fact that parts of the complete 
bare playa however have to be corrected in the same 
way in all bands leads to the assumption that this 
approach is still not too bad. Bands 1, 4 and 7 of 
May have to be multiplied by respectively 0.919, 
0.882 and 0.913 in order to get values comparable 
with January reflectance at the top of the 
5. RESULTS AND INTERPRETATION 
The reflectance values of May and January are made 
comparable with the aid of a reference surface. 
Apart from this radiometric transformation also 
geometrically the May image was converted with the 
January data with the aid of ground control points. 
A first order transformation has been applied, 
which gave an estimated standard error of less than 
a pixel in both directions according to the 
statistical analysis. In this way both the location 
and the reflectance values are comparable now. 
In order to study the changes a large range of 
images and plots can be made. The construction and 
interpretation of 1, 4, 7 combinations of both 
data, with a linear stretch between the same 
limits, is a good first approach. A compariéon of 
both images will give a good overview of spatial 
dynamics. 
It is also possible to make multitemporal 
combinations or perform division or subtraction of 
bands of the two days after the geometrical and 
radiometrical corrections. Three types of 
multitemporal images can be discriminated: a colour 
combination, a ratio and a difference product. 
Again the use of band 1, 4 and 7 is most promising. 
- colour combinations 
Useful products are combinations in which a primary 
colour is assigned to one day and a secondary 
colour to the other day. An example is a 
combination of band 1 of May in red and band 1 of 
January in cyan. If no changes occur, the grey 
tones represent the relative reflectance. 
- ratio 
A division of one band in May (corrected) by the 
same band in January will give a ratio of 1 for 
pixels with unchanged reflectance, above 1 for 
pixels with a relatively high reflectance in May 
and below 1 for a high January value of 
reflectance. Lines with a constant ratio in plots 
connect points with the same relative decrease or 
increase in reflectance. 
- difference 
An image made by subtraction of January from May 
(corrected) would also give a value of 1 in the 
case of no change, above 1 for a relatively high 
reflectance in May, and below 1 for a low May 
reflectance. Still there is an important difference 
between the ratio and difference image. In this 
latter image the same value will be found for all 
points with the same absolute decrease or increase 
in reflectance. The choice out of the two latter 
products will depend on the type and cause of 
change. For a simplified hypothetical example the 
difference will be explained (table 2). Assume the 
reflectance of surface 1 to be 0 % and the 
reflectacne of two surfaces with a different 
mineralogical composition respectively 20 % and 40 
%. If due to a special event, surface 2 and 3 
changes in such a way that both surfaces are 
covered for 50 % with surface cover type A, the 
reflectance will change to respectively 10 % and 20 
%. A ratio image will give in this case the same 
value for this identical change. A comparable 
example will be given for the difference image. 
Again the reflectance of the three surfaces are 
respectively 0 %, 20 % and 40 %. However the 
reflectance of surface 2 is now made up for 50 % of 
surface cover A and 50 % of surface B. If the 
amount of cover with A increases for both surface 2 
and 3 with 50 % the reflectance will change 
respectively to 0 % and 20 %. A difference image 
will give now the same value for this identical 
change. The second hypothetical example is also
	        

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Damen, M. .C. .J. Remote Sensing for Resources Development and Environmental Management. A. A. Balkema, 1986.
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