G. Guggenberger et al., LAND-USE EFFECTS ON THE COMPOSITION OF ORGANIC-MATTER IN PARTICLE-SIZE SEPARATES OF SOILS .2. CPMAS AND SOLUTION C-13 NMR ANALYSIS, European journal of soil science, 46(1), 1995, pp. 147-158
Soils from A horizons of Eutrochrepts under spruce forest (Sf), mixed
deciduous forest (Df), permanent grassland (Gp), and arable rotation (
Ar) were fractionated into clay- (<2 mu m), silt- (2-20 mu m) and sand
- (20-2000 mu m) sized separates. C-13 NMR spectroscopy was used to co
mpare SOM composition across size separates and between land-use regim
es. CPMAS C-13 NMR spectroscopy showed that the intensity of signals a
ssigned to carbohydrates (representing most O-alkyl C) and lignin (phe
nolic and methoxyl C) declined with decreasing particle size. Concurre
ntly, alkyl C and C-substitution of aromatic C increased in the order
sand, silt, clay. The amount of alkyl C correlated well with microbial
resynthesis of carbohydrates. Solution C-13 NMR spectra suggested tha
t humic acids (HA) extracted from the size separates were richer in ca
rboxyl C and aromatic C than the bulk size separates. Also HA reflecte
d increasing percentage of alkyl C with decreasing particle size. O-al
kyl C were lower in silt HA than in clay HA whereas aromatic C tended
to peak in silt HA. These results suggested that sand-sized separates
were enriched in plant residues (primary resources) whereas clay-sized
separates were dominated by products of microbial resynthesis (second
ary resources). Silt was rich in selectively preserved and microbially
transformed primary resources. C-13 NMR spectroscopy showed only smal
l differences in SOM composition between land-use regimes, except that
silt and silt HA from Ar were richer in aromatic C than those from th
e other plots. But enrichment factors (E = content in fraction/content
in whole soil) revealed differences in the distribution of C species
across the size separates. Relatively high E(aromatic) (0.9) and E(O-a
lkyl) (1.0) for sand from Gp indicated high amounts of plant residues,
probably due to intense rhizodeposition and to occlusion of plant deb
ris within aggregates. Low E(aromatic) (0.3) and E(O-alkyl) (0.3) for
sand from Ar suggested depletion of primary resources, which could be
attributed to disintegration of soil aggregates upon cultivation. A pr
onounced enrichment of alkyl C in Ar clay-sized separates (E(alkyl) =
3.1) suggested large amounts of microbial carbon. Microbial products a
ttached to clay surfaces by a variety of physico-chemical bondings app
eared more stable against mineralization induced by cultivation than p
lant residues sequestered in aggregates.