The loss of plant species from terrestrial ecosystems may cause changes in
soil decomposer communities and in decomposition of organic material with p
otential further consequences for other ecosystem processes. This was teste
d in experimental communities of 1, 2, 4, 8, 32 plant species and of 1, 2 o
r 3 functional groups (grasses, legumes and non-leguminous forbs). As plant
species richness was reduced from the highest species richness to monocult
ures, mean aboveground plant biomass decreased by 150%, but microbial bioma
ss (measured by substrate induced respiration) decreased by only 15% (P = 0
.05). Irrespective of plant species richness, the absence of legumes (acros
s diversity levels) caused microbial biomass to decrease by 15% (P = 0.02).
No effect of plant species richness or composition was detected on the mic
robial metabolic quotient (qCO(2)) and no plant species richness effect was
found on feeding activity of the mesofauna (assessed with a bait-lamina-te
st). Decomposition of cellulose and birchwood sticks was also not affected
by plant species richness, but when legumes were absent, cellulose samples
were decomposed more slowly (16% in 1996, 27% in 1997, P = 0.006). A signif
icant decrease in earthworm population density of 63% and in total earthwor
m biomass by 84% was the single most prominent response to the reduction of
plant species richness, largely due to a 50% reduction in biomass of the d
ominant 'anecic' earthworms. Voles (Arvicola terrestris L.) also had a clea
r preference for high-diversity plots. Soil moisture during the growing sea
son was unaffected by plant species richness or the number of functional gr
oups present. In contrast, soil temperature was 2 K higher in monocultures
compared with the most diverse mixtures on a bright day at peak season. We
conclude that the lower abundance and activity of decomposers with reduced
plant species richness was related to altered substrate quantity, a signal
which is not reflected in rates of decomposition of standard test material.
The presence of nitrogen fixers seemed to be the most important component
of the plant diversity manipulation for soil heterotrophs. The reduction in
plant biomass due to the simulated loss of plant species had more pronounc
ed effects on voles and earthworms than on microbes, suggesting that higher
trophic levels are more strongly affected than lower trophic levels.