Abstract
Enhancing carbon sequestration in soil is an important means to reduce net emissions of carbon dioxide (CO 2) to the atmosphere. The soil organic carbon (SOC) pool is the net result of carbon (C) input in the form of crop residue and biomass, and output including CO 2 flux and other losses. The objectives of this study were to: (1) determine the influence of known additions of crop residue in a no till system on CO 2 flux measured with the static chamber alkali-absorption method, and (2) calculate the C budget from the CO 2 flux and C added in crop residue. The experiment was started on a Crosby silt loam (Stagnic Luvisol) in 1989. Annually 0, 2, 4, 8 and 16 Mg ha −1 wheat straw ( Triticum aestivum L.) was applied. Noon soil temperature and daily CO 2 flux were determined in 1997. Residue application rate had a significant impact on soil temperature as measured at noon, especially early in the growing season. Noon soil temperature was up to 14°C higher under unmulched compared with that of mulched treatments. Measured CO 2 flux ranged from 0.4 to 4.2 g C m −2 per day. Differences in CO 2 flux between crop residue treatments were not significant on most sampling dates, probably due to the presence of undecomposed residue in the soil which did not contribute to the CO 2 flux, and to variability in sampling. Average daily soil temperature at 5 cm depth determined on a nearby weather station explained 60% of the variation in CO 2 flux from bare plots. The C budget calculated from CO 2 flux measurements indicated a net depletion of SOC in all treatments. However, measured SOC contents indicated an increase of SOC over time in some treatments. It is likely that the annual CO 2 flux measured with the static chamber alkali-absorption method is overestimated due to omission of CO 2 measurements when soil water content is high, and perhaps other, as yet unknown factors. A comparison of the static chamber technique and improved dynamic chamber techniques and micrometeorological methods is recommended.
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