Da. Wardle et al., Plant removals in perennial grassland: Vegetation dynamics, decomposers, soil biodiversity, and ecosystem properties, ECOL MONOGR, 69(4), 1999, pp. 535-568
The consequences of permanent loss of species or species groups from plant
communities are poorly understood, although there is increasing evidence th
at individual species effects are important in modifying ecosystem properti
es. We conducted a field experiment in a New Zealand perennial grassland ec
osystem, creating artificial vegetation gaps and imposing manipulation trea
tments on the reestablishing vegetation. Treatments consisted of continual
removal of different subsets or "functional groups" of the flora. We monito
red vegetation and soil biotic and chemical properties over a 3-yr period.
Plant competitive effects were clear: removal of the C-3 grass Lolium peren
ne L. enhanced vegetative cover, biomass, and species richness of both the
C-4 grass and dicotyledonous weed functional groups and had either positive
or negative effects on the legume Trifolium repens L., depending on season
. Treatments significantly affected total plant cover and biomass; in parti
cular, C-4 grass removal reduced total plant biomass in summer, because no
other species had appropriate phenology. Removal of C-4 grasses reduced tot
al root biomass and drastically enhanced overall shoot-to-root biomass rati
os. Aboveground net primary productivity (NPP) was not strongly affected by
any treatment, indicating strong compensatory effects between different fu
nctional components of the flora.
Removing all plants often negatively affected three further trophic levels
of the decomposer functional food web: microflora, microbe-feeding nematode
s, and predaceous nematodes. However, as long as plants were present, we di
d not find strong effects of removal treatments, NPP, or plant biomass on t
hese trophic groupings, which instead were most closely related to spatial
variation in soil chemical properties across all trophic levels, soil N in
particular. Larger decomposer organisms, i.e., Collembola and earthworms, w
ere unresponsive to any factor other than removal of all plants, which redu
ced their populations. We also considered five functional components of the
soil biota at finer taxonomic levels: three decomposer components (microfl
ora, microbe-feeding nematodes, predaceous nematodes) and two herbivore gro
ups (nematodes and arthropods). Taxa within these five groups responded to
removal treatments, indicating that plant community composition has multitr
ophic effects at higher levels of taxonomic resolution. The principal ordin
ation axes summarizing community-level data for different trophic groups in
the soil food web were related to each other in several instances, but the
plant ordination axes were only significantly related to those of the soil
microfloral community. There were time lag effects, with ordination axes o
f soil-associated herbivorous arthropods and microbial-feeding nematodes be
ing related to ordination axes representing plant community structure at ea
rlier measurement dates. Taxonomic diversity of some soil organism groups w
as linked to plant removals or to plant diversity. For herbivorous arthropo
ds, removal of C-4 grasses enhanced diversity; there were negative correlat
ions between plant and arthropod diversity, presumably because of negative
influences of C-4 species in the most diverse treatments. There was evidenc
e of lag relationships between diversity of plants and that of the three de
composer groups, indicating multitrophic effects of altering plant diversit
y.
Relatively small effects of plant removal on the decomposer food web were a
lso apparent in soil processes regulated by this food web. Decomposition ra
tes of substrates added to soils showed no relationship with treatment, and
rates of CO2 evolution from the soil were only adversely affected when all
plants were removed. Few plant functional-group effects on soil nutrient d
ynamics were identified. Although some treatments affected temporal variabi
lity (and thus stability) of soil biotic properties (particularly CO2 relea
se) throughout the experiment, there was no evidence of destabilizing effec
ts of plant removals.
Our data provide evidence that permanent exclusion of plant species from th
e species pool can have important consequences for overall vegetation compo
sition in addition to the direct effects of vegetation removal, and various
potential effects on both the above- and belowground subsystems. The natur
e of many of these effects is driven by which plant species are lost from t
he system, which depends on the various attributes or traits of these speci
es.