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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 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
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

297 
included are 
parent dis- 
ples (Si, S2) 
Lbution a 
Lfference be- 
Dtained as 
(2) 
amber of 
an estimate 
but ion given 
(3) 
of S-| , S2 . 
(2) , has 
The second is an accurate procedure, by testing the 
normality of sample distribution, equality of 
variances and finally significance of differences in 
mean values. The samples Sj do not necessarily belong 
to a normal parent distribution and, if so, the 
variances of their parent distribution are not neces 
sarily equal. The goodness of fit of Si, S2 to a 
normal distribution can be assessed (Steel and Torrie 
1960) by calculating the value of the criterion: 
(4) 
where o^, e^ are the observed respectively expected 
occurrences in class i. To calculate e^, the normally 
distributed variable: 
(X - Xj) 
(5) 
is applied, with xj, Oj being the mean respectively 
the variance of sample Sj. Then the expected number 
of sample elements e^ in the i-th class, i.e. between 
zi and z^ + i are calculated on the basis of a normal 
distribution and of the total number of occurrences 
l i0i . Finally, the thus obtained x 2 ~value is compared 
with threshold x 2- values, corresponding with pre-set 
probabilities, to assess whether the observed dis 
tribution significantly deviates from a normal dis 
tribution. 
Assuming that the observed distributions belong to 
normal parent distributions, we have now to test the 
equality of variances. The following criterion can be 
applied (Kenney and Keeping 1959): 
F = 
(6) 
2 . 2 
where U is the larger and V the smaller estimated 
variance between: 
N 1 - 1 
and 
2 2 
s 2 = nT^-T 
(7) 
The F-value thus obtained is compared with the select 
ed threshold F, e.g.^with a probability P = 0.01 of 
F being larger than F. 
After having established that both samples belong 
to the same normal distribution, the Student's t-test 
can be applied according to the first procedure. If 
not, the following procedure has to be applied (Steel 
and Torrie 1960) : 
t = 
and 
(0) 2 _ V? + V2 
N 
1 + N 2 
(8) 
(9) 
The threshold t-value is obtained as: 
t* = 
Vi + V 2 
(10) 
with Wl = J- and w 2 = Л 
threshold t-values at the 
while t^ , t^ are the 
same level of probability 
Table 4. Goodness of fit of observed distributions 
against the normal distribution; observed values of 
TVI in field plots in the Grande Bonifica Ferrarese 
and East Sesia irrigation districts (Po valley, Italy); 
reflectance measurements obtained with the LANDSAT 
TM, band 4 and 3; x 2- values having a probability 
P = 0.05 respectively 0.01 to be exceeded are in 
dicated (s = significant, ns = not significant) 
Variable 
Plots 
ВАЗ 
CA4 
CA2 
IA2 
0B2 
Total frequency 
4 
25 
49 
25 
77 
Skewness 
-0.1 7 
-0.05 
-2.4 
-0.05 
1.41 
Kurtosis 
317.1 
664 
2289.9 
44.7 
3.81 
X 2 
0.24 
7.4 
32 
6.9 
18.4 
X 2 (P = 0.05) 
3.84 
11.1 
7.8 
6.0 
7.8 
X 2 (P = 0.01) 
Deviation from 
6.63 
15.1 
11.1 
9.2 
1 1.3 
normal distr. 
ns 
ns 
s 
ns 
s 
Table 5. Significance of differences in TVI-values, 
as obtained with LANDSAT TM 4 and TM 3 measurements 
(2 May 1985), Grande Bonifica Ferrarese, Po-valley, 
Italy; significance assessed by applying the accurate 
procedure respectively the simplified procedure 
(within brackets); ns = not significant, s = signif 
icant at probability P = 0.05, hs = highly signif 
icant at P = 0.01; for plot coding see text; largest 
observed differences in seeding dates: BB1, 30 April; 
BB2, 16 May; 0B1, 5 April; 0B2, 12 May; IB1, 10 April; 
IB2, 7 May 
Plots 
BB1 
BB2 
0B1 
0B2 
IB1 
IB2 
BB1 
hs (hs) 
hs(hs) 
hs (hs) 
hs(hs) 
hs(hs) 
BB2 
- 
hs(ns) 
s (ns) 
hs (hs) 
s( s) 
0B1 
- 
s( s) 
hs(hs) 
hs( s) 
0B2 
- 
hs (hs) 
hs( s) 
IB1 
- 
hs(hs) 
IB2 
- 
Table 6. Significance of differences in TVI-values, 
as obtained with LANDSAT TM 4 and TM 3 measurements 
(30 April 1985); East Sesia, Po-valley, Italy; for 
explanation of plot coding see text: ns = not sig 
nificant, s - significant at P - 0.05, hs = highly 
significant at P = 0.01; samples include between 20 
and 77 pixels; largest observed phenological dif 
ferences: CA1, full cover = 20 March; CA2, full cover 
= 30 April; BA1, seeding date = 15 April; BA2, seed 
ing date - 24 April; LA1, seeding date = 1 April; 
IA2, seeding date = 5 May 
Plots 
CA1 CA2 
BA1 
BA2 
IA1 
IA2 
CA1 
- s 
hs 
hs 
hs 
hs 
CA2 
- 
hs 
hs 
hs 
hs 
BA1 
- 
ns 
hs 
hs 
BA2 
- 
hs 
hs 
IA1 
- 
hs 
IA2 
-
	        

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