F. Domingo et al., MEASUREMENT AND MODELING OF RAINFALL INTERCEPTION BY 3 SEMIARID CANOPIES, Agricultural and forest meteorology, 91(3-4), 1998, pp. 275-292
The main aims of this study were, firstly, to adapt the rainfall inter
ception model of Rutter et al. (Agric. Meterology, 1971, 9, 367-384) t
o individual plants of two semiarid shrubs (Anthyllis cytisoides L. an
d Retama sphaerocarpa (L.) Boiss.) and a tussock grass (Stipa tenaciss
ima L,) and secondly, to understand how the different canopy structure
s influence rainfall partitioning by individual plants. The selected s
pecies represent contrasting canopy types typical of vegetation of sem
iarid areas. Free throughfall coefficients were estimated from field m
easurements of low volume rainfall events and vertical photographs tak
en beneath the plant canopy. Canopy drainage curves were measured by c
ontinuous weighing of wetted plants. Canopy boundary layer conductance
s were calculated by measuring the evaporation of water from wet canop
ies, Field measurements of gross rainfall, throughfall and stemflow we
re taken for each rainfall event for A. cytisoides and R. sphaerocarpa
. The Rutter type model of rainfall interception was adapted for indiv
idual shrubs and tested with measured rainfall events showing a good a
greement between observed and predicted values for R. sphaerocarpa and
for A. cytisoides. The interception model was then run to simulate in
terception loss during actual rainfall events, using atmospheric condi
tions measured every 5 s. The results from this simulation showed sign
ificant differences in interception loss between species, which can be
explained by differences in canopy drainage and boundary layer conduc
tance, and are caused primarily by the structural differences in their
canopies. R. sphaerocarpa gave lower interception than the other two
species, S. tenacissima gave higher interception, while A. cytisoidesh
ad an intermediate value. The low interception loss by R. sphaerocarpa
can be explained by its low total area index, thus, high free through
fall and high canopy drainage rate per unit projected canopy area. On
the other hand, S. tenacissima and A. cytisoides, show a low free thro
ughfall and drainage rate per unit projected canopy area because of th
eir higher aerial biomass density. The ecological implications of thes
e adaptations are discussed. (C) 1998 Elsevier Science B,V, All rights
reserved.