Y. Nouvellon et al., Time course of radiation use efficiency in a shortgrass ecosystem: Consequences for remotely sensed estimation of primary production, REMOT SEN E, 71(1), 2000, pp. 43-55
A reliable estimation of primary production of terrestrial ecosystems is of
ten a prerequisite for land survey and management, while being important al
so in ecological and climatological studies. At a regional scale, grassland
primary production estimates are increasingly being made with the use of s
atellite data. In a currently used approach, regional gross, net, and above
ground net primary productivity (GPP, NPP, and ANPP) are derived from the p
arametric model of Monteith and are calculated as the product of the fracti
on of incident photosynthetically active radiation absorbed by the canopy (
f(APAR)) and gross, net, and aboveground net production (radiation-use) eff
iciencies (epsilon(g), epsilon(n), and epsilon(an)); f(APAR) being derived
from indices calculated from satellite-measured reflectances in the red and
near infrared. The accuracy and realism of the primary production values e
stimated by this approach therefore largely depend on an accurate estimatio
n of epsilon(g), epsilon(n), and epsilon(an). However, data are scarce for
production efficiencies of semiarid grasslands, and their time and spatial
variations are poorly documented, often leading to large errors for the est
imates. In this paper, a modelling approach taking into account relevant ec
osystem processes and based on extensive field data was used to estimate ti
me variations of epsilon(g), epsilon(n), and epsilon(an) of a shortgrass si
te in Arizona. These variations were explained by variations in plant water
stress, temperature, leaf aging, and processes such as a respiration and c
hanges in allocation pattern between above- and below-ground compartments.
Over the 3 study years, averaged values of epsilon(g), epsilon(n), and epsi
lon(an) were found to be 1.92, 0.74, and 0.29 g DM (MJ IPAR)(-1), respectiv
ely. epsilon(g) and epsilon(n) exhibited large interannual and seasonal var
iations mainly due to changes in water limitations during the growing seaso
n. Interannual variations of epsilon(an) were much less important. However,
for shorter periods, epsilon(an) exhibited very contrasting values from re
growth to senescence. The calculation of ANPP seems less prone to errors du
e to environmental effects when computed on an annual basis. When estimatin
g GPP and NPP, better results are expected if water limitations are taken i
nto account. This could be possible through the estimation of water-stress
factor by using surface temperature or other indices derived from thermal i
nfrared remote sensing data. The limitations due to temporally varying effi
ciencies, shown here for shortgrass ecosystems, are also relevant to all dr
ought-exposed ecosystems, particularly those with abundant evergreen or per
ennial species. Published by Elsevier Science Inc.