Gj. Blair et al., TRANSFORMATIONS OF SULFUR IN SOIL AND SUBSEQUENT UPTAKE BY SUBTERRANEAN CLOVER, Australian Journal of Soil Research, 32(6), 1994, pp. 1207-1214
For a soil test to be effective it must sample pools of sulfur (S) tha
t are immediately available to the plant and organic pools that turn o
ver rapidly and supply S in the longer term. An experiment was conduct
ed in two phases, the first being over 96 days to study the incorporat
ion of S from Na2 35SO4 into various soil components at two temperatur
es [18/11-degrees-C (day/night) and 27/22-degrees-C] and two S applica
tion rates (10 and 50 mug S g-1 soil) and its uptake by subclover grow
n in pots. At intervals the pots were destructively sampled and the co
mponents radioassayed. In the second phase, soil sulfate was removed f
rom the soil used in the first phase and the soil was potted and repla
nted with subclover. Soil and plant samples were taken 70 days later a
nd the plant uptake and recycling of S-35 from the labelled soil organ
ic pools were measured. Within 14 days in phase 1, at least 40% of the
applied S-35 sulfate had been incorporated into the hydriodic acid-re
ducible (HI-S) fraction. Subsequently, the S in the newly formed H-S f
raction was recycled with mean net release rates of S-35 being 26% and
38% over the next 21 and 28 day periods respectively. The mean S-35 c
ontent of the carbon bonded (C-S) fraction reached a peak of 22% after
63 days, indicating a very much slower recycling rate than the H-S fr
action. These results show the importance of the HI-S fraction and str
ess that any reliable soil testing method must at least include some e
stimate of the potential contribution from the H-S fraction as well as
the 'available' inorganic S.