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Possibilities of near infrared reflectance spectroscopy for the prediction of organic carbon concentrations in grassland soils

Published online by Cambridge University Press:  01 December 2005

C. VAN WAES
Affiliation:
Ministry of the Flemish Community, Agricultural Research Centre, Department of Crop Husbandry and Ecophysiology, Burg. Van Gansberghelaan, 109, B-9820 Merelbeke, Belgium
I. MESTDAGH
Affiliation:
Ministry of the Flemish Community, Agricultural Research Centre, Department of Crop Husbandry and Ecophysiology, Burg. Van Gansberghelaan, 109, B-9820 Merelbeke, Belgium
P. LOOTENS
Affiliation:
Ministry of the Flemish Community, Agricultural Research Centre, Department of Crop Husbandry and Ecophysiology, Burg. Van Gansberghelaan, 109, B-9820 Merelbeke, Belgium
L. CARLIER
Affiliation:
Ministry of the Flemish Community, Agricultural Research Centre, Department of Crop Husbandry and Ecophysiology, Burg. Van Gansberghelaan, 109, B-9820 Merelbeke, Belgium

Abstract

For the determination of soil organic carbon (OC) concentrations, the availability of a fast, low-cost analysis method is required. The aim of the present study was to evaluate the possibilities of near infrared reflectance spectroscopy (NIRS) to build a spectral database and to develop calibrations for the prediction of organic carbon concentrations in grassland soils. NIRS spectra of 1626 soil samples from different grasslands (both agricultural and natural) were collected between 1100 and 2500 nm. NIRS calibrations were developed with modified partial least square regression and tested with independent validation samples. The best equations were obtained with the first derivative of the spectra without scatter corrections. For the global calibration, containing the samples of all origins, the standard errors of calibration (SEC) and of prediction (SEP) were respectively 3·70 g OC/kg dry soil (R2=0·89) and 3·95 g OC/kg dry soil (R2=0·88). The ratio of the standard deviation of the reference validation data to the SEP (RPD), indicating the performance of the calibration, was 2·9. Dividing the samples into groups according to their practice (agricultural or natural grassland), improved SEP by 5·8 and 7·7%, respectively. Dividing the samples into texture groups (clay, silt, sand) improved SEP for agricultural grassland by, on average, 7·4% and for natural grassland by 16·2%.

Type
Research Article
Copyright
2005 Cambridge University Press

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