Identifying 'functional' pools of soil organic matter and understanding the
ir response to tillage remains elusive. We have studied the effect of tilla
ge on the enriched labile fraction, thought to derive from microbes and hav
ing an intermediate turnover time. Four soils, each under three regimes, lo
ng-term arable use without tillage (NT), long-term arable under conventiona
l tillage (CT), and native vegetation (NV), were separated into four aggreg
ate size classes. Particle size fractions of macro- (250-2000 mu m) and mic
roaggregates (53-250 mu m) were isolated by sonication and sieving. Subsequ
ently, densiometric and chemical analyses were made on fine-silt-sized (2-2
0 mu m) particles to isolate and identify the enriched labile fraction. Acr
oss soils, the amounts of C and N in the particle size fractions were highl
y variable and were strongly influenced by mineralogy, specifically by the
contents of Fe and Al oxides. This evidence indicates that the fractionatio
n procedure cannot be standardized across soils. In one soil, C associated
with fine-silt-sized particles derived from macroaggregates was 567 g C m(-
2) under NV, 541 g C m(-2) under NT, and 135 g C m(-2) under CT, whereas C
associated with fine-silt-sized particles derived from microaggregates was
552, 1018, 1302 g C m(-2) in NV, NT and CT, respectively. These and other d
ata indicate that carbon associated with fine-silt-sized particles is not s
ignificantly affected by tillage. Its location is simply shifted from macro
aggregates to microaggregates with increasing tillage intensity. Natural ab
undance C-13 analyses indicated that the enriched labile fraction was the o
ldest fraction isolated from both macro- and microaggregates. We conclude t
hat the enriched labile fraction is a 'passive' pool of soil organic matter
in the soil and is not derived from microbes nor sensitive to cultivation.