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Though the locale of the missing carbon sink is currently being sought, it is known that the soil organic carbon pools maintain twice as much carbon than the atmosphere, and three times the carbon hoarded by vegetation. (Andrews and Schlesinger 2001). This does not mean that all of terrestrial earth is a sink. The difference between carbon sequestration and soil respiration determines whether a particular area is a source or a sink. In fact, soil microbial respiration "constitutes a carbon flux 10 times greater than that from fossil fuel combustion and 2.5 times greater than the delivery of litter to the soil surface (Andrews and Schlesinger 2001)." A positive difference between sequestration and respiration indicates a source while a negative difference implicates a sink. To complicate things further, climate variability can differentially affect rates of sequestration and respiration rendering a source a sink and vice versa.
Plant partitioning under elevated carbon dioxide may result in a greater percentage of carbon stored in roots belowground (Norby 1993). Zak et. al 1993 contend fine root production and overall subterranean biomass may result. This biomass increase coupled with addition of above and belowground detritus could potentially increase the C soil inputs. The question then becomes what is the effect of these carbon inputs on belowground carbon cycling? How is the soil organic carbon pool affected? 13C Stable isotope analysis of soil carbon inputs proves useful in these determination. Under conditions of deforestation, soil organic matter (SOM) simultaneously changes in two ways: 1. Mineralization of native humus continues and is not renewed upon deforestation 2. Input of C into SOM from crop remains coupled with the native C loss from deforestation If the deforested vegetation are of the C3 photsynthetic pathway, reforestation with C4 plants yields a different 13C signature. This is because C3 plants have a d13C = -28 vs C4 = -13. Cerri et. al 1990 describe such a system in which a forest has been replaced with sugar cane crop: Figure 1:
Gerzabeck et.al 1990 use 13C to characterize soil humus dynamnics. They found that high molecular weight fractions of humus in the Ol and Ah horizons exhibited less negative d13C in two locations, with the low molecular weight in the Ol horizon exhibiting a more positive d13C. Non-humic substances in both horizons "were isotopically heavier than the humic substances of the second maximum," suggesting greater microbial action and hence enhanced 13C (Gerzabeck et.al 1990). Figure 2:
Andrews and Schlesinger 2001 examined soil dynamics
over a three year study of Free-Air CO2 Enrichment (FACE) in
sections of the Duke Forest. The researchers subjected three of six 30m
diameter plots populated with 15-year-old Loblolly pine to elevated CO2
levels relative to the other 3 ambient CO2 plots. 13C label
in the experimental plots appeared belowground from enhanced root and
microbial respiration. In fact the 55% increase in atmospheric carbon
translated into a maximum daily soil respiration increase up to 131%.
Overall Schlesinger and Andrews observed a 27% increase in soil respiration
(Andrews and Schlesinger 2001). They also found
that the greater soil CO2 concentration enhances both soil weathering
and acidification by increasing mineral cations by 271% and alkalinity
by 162%. That soils respired 27% more implies soils may not be an effective
global warming carbon sink despite enhanced belowground biomass storage. |
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