Two field experiments were conducted using three dominant perennial sp
ecies of the Chihuahuan Desert: Hilaria mutica (a tussock grass), Larr
ea tridentata (a microphyllous shrub) and Opuntia rastrera (a flat-ste
mmed succulent cactus). Two hypotheses concerning competition in arid
plant communities were tested. (1) Marked resource partitioning with n
o interspecific competition could be expected since the three species
belong to different life-forms, and that plant growth in deserts is ba
sically limited by harsh environmental conditions. (2) Alternatively,
resource scarcity (particularly water) will result in strong plant com
petition. In a I-year removal experiment, water status and plant growt
h of the three species were monitored in twelve 10 m x 10 m plots rand
omized in three blocks and assigned to the following treatments: (a) r
emoval of all species, except H. mutica; (b) removal of all species, e
xcept L. tridentata; (c) removal of all species, except O. rastrera, a
nd (d) control without any manipulation. In a watering experiment, und
er two neighbourhood conditions (growing isolated or in associations o
f plants of the three species in plots of 20 m(2)), the water status o
f the three species and the growth of H. mutica and L. tridentata were
studied for 32 days after an irrigation equivalent to 30 mm of rain,
similar to a strong storm event at the site. In the removal experiment
, where plants were free to capture water, no evidence of competition
was observed. However, during the watering experiment, in which water
was forced into the soil, competitive effects were observed. Associate
d individuals of L. tridentata had lower xylem water potentials and os
motic potentials (OPs) and produced shorter twigs and less leaves and
nodes. Although less pronounced, neighbours also had a negative effect
on the OP in O. rastrera. According to these results, the intensity o
f the interspecific competition for water seems to depend on the level
of resource availability in the soil. Thus, the validity of the two h
ypotheses tested in this study also depends on the level of resources.
Competition could be absent or very low in years of low precipitation
, as in the year of this study (173 mm against a 25-year average of 26
4 mm). However, when soil water availability is high, e.g. following h
eavy rain, the negative interactions between species could be more int
ense.