1. Seed input, changes in the seed bank and seedling recruitment of On
opordum were monitored over 1 year at three contrasting sites (pasture
, oat crop and hillside) within an 80-hectare paddock at Galong, New S
outh Wales, about 100 km NW of Canberra. Each site was c. 2000 m(2). T
ime constraints precluded a longer study and repetition of the samplin
g procedures at similar sites in other areas. 2. In the pasture there
were few Onopordum plants but a seed bank of c. 5000 seeds m(-2). Duri
ng the year the seed bank decreased by more than half, but the most do
rmant component remained constant at c. 800 seeds m(-2). 3. In an oat
crop nearby there were no flowering Onopordum plants and there was no
direct seed input. Nevertheless, the seed bank of c. 700 seeds m(-2) d
id not decrease. 4. At the third site, a grazed hillside, Onopordum de
nsity was high (19 plants m(-2)). The seed input of 1788 seeds m(-2) c
aused a temporary small increase in the seed bank in summer but there
was no change over the 1-year period either in the total seed bank (c.
3000 seeds m(-2)) or in its most dormant component (c. 750 seeds m(-2
)). 5. Seedlings appeared in all seasons, invariably after rain. More
than 95% of seedlings appeared in late summer or autumn, but different
management practices changed the pattern of winter establishment. 6.
For ecological studies of weeds, the population dynamics of the seeds
in the soil and of the plants above ground are equally significant. Th
is study shows that the existence of a small pool of labile seeds (c.
15% minimum) in the seed bank that can be recruited opportunistically,
together with a large, strongly persistent component, will make any f
orm of short-term control difficult.