Virgin krasnozems contain about 6% C from 0-15 cm and, while the C con
tent is less at depth, the total C reserves may exceed 200 t ha(-1) to
about Im depth. Highest organic matter contents occur where the annua
l rainfall is 1500+/-200 mm. At higher rainfalls, the C contents are l
ess. There is a negative correlation between organic C and N content a
nd mean annual temperature. Krasnozems contain more C than other soils
in the same climate and are comparatively more fertile. Correlations
of C contents with clay contents are confounded by the contents of fre
e iron oxides. While data are fragmented, it is evident that the clear
ing of rainforests and replacement by pastures or other agricultural a
nd horticultural pursuits have led to losses of up to 50% of the organ
ic C over several decades. A simple model illustrates that this is cau
sed by lower inputs of C to the soil in most situations except perhaps
long term productive pastures where inputs may be greater than under
rainforests. Studies using natural isotopes of C have shown the persis
tence of some C in krasnozems for hundreds of years. Some of this is p
articulate organic matter occluded in aggregates but most of it appear
s to be associated with clays, particularly at depth. The chemistry of
organic matter in krasnozems appears similar to that of other soils,
although solid state C-13 nuclear magnetic resonance has shown more al
iphatic materials in krasnozems than other soils, but the reason for t
his is not clear. There is little information on biota in krasnozems.
The deep well structured soils are a good habitat for organisms and th
eir high fertility guarantees a good supply of substrate for fauna and
flora. It is important to maintain the organic matter contents of kra
snozems to maintain cation exchange capacity, mineralization of N and
other elements, to decrease phosphate sorption and to stabilize larger
aggregates and thus macro porosity.