Rr. Allmaras et al., Soil organic carbon sequestration potential of adopting conservation tillage in US croplands, J SOIL WAT, 55(3), 2000, pp. 365-373
Soil organic carbon (SOC) makes up about two-thirds of the C pool in the te
rrestrial biosphere; annual C deposition and decomposition to release carbo
n dioxide (CO2) into the atmospheric constitutes about 4% of this SOC pool.
Cropland is an important, highly managed component of the biosphere. Among
the many managed components of cropland are the production of crop residue
, use of tillage systems to control crop residue placement/disturbance, and
residue decomposition. An accumulation of SOC is a C sink (a net gain from
atmospheric CO2) whereas a net loss of SOC is a C source to atmospheric CO
2. A simple three components model was developed to determine whether or no
t conservation tillage systems were changing cropland from a C source to a
C sink. Grain/oil seed yields and harvest indices have indicated a steadily
increasing supply of crop residue since 1940, and long term field experime
nts indicate SOC storage in no-tillage > non moldboard tillage > moldboard
tillage systems. According to adoption surveys, moldboard tillage dominated
until about 1970, but non moldboard systems are now used nationally on at
least 92% of planted wheat, corn, soybean, and sorghum. Consequently, since
about 1980, cropland agriculture has become a C sink. Moldboard plow syste
ms had prevented a C sink response to increases in crop residue production
that had occurred between 1940 and 1970. The model has not only facilitated
a qualitative conclusion about SOC but it has also been used to project pr
oduction, as well as soil and water conservation benefits, when a C credit
or payment to farmers is associated with the C sink in cropland agriculture
.