Fire can cause severe nitrogen (N) losses from grassland, chaparral, and te
mperate and boreal forest ecosystems. Paradoxically, soil ammonium levels a
re markedly increased by fire, resulting in high rates of primary productio
n in re-establishing plant communities. In a manipulative experiment, we ex
amined the influence of wild-fire ash residues on soil, microbial and plant
N pools in a recently burned Californian bishop pine (Pinus muricata D. Do
n) forest. Ash stimulated post-fire primary production and ecosystem N rete
ntion through direct N inputs from ash to soils, as well as indirect ash ef
fects on soil N availability to plants. These results suggest that redistri
bution of surface ash after fire by wind or water may cause substantial het
erogeneity in soil N availability to plants? and could be an important mech
anism contributing to vegetation patchiness in fire-prone ecosystems. In ad
dition, we investigated the impact of fire on ecosystem N cycling by compar
ing N-15 natural abundance values from recently burned and nearby unburned
P. muricata forest communities. At the burned site, N-15 natural abundance
in recolonising species was similar to that in bulk soil organic matter. By
contrast, there was a marked N-15 depletion in the same species relative t
o the total soil N pool at the unburned site. These results suggest that pl
ant uptake of nitrate (which tends to be strongly depleted in N-15 because
of fractionation during nitrification) is low in recently burned forest com
munities but could be an important component of ecosystem N cycling in matu
re conifer stands.