Abstract

The effects of compaction on soil porosity and soil water relations are likely to influence substrate availability and microbial activity under fluctuating soil moisture conditions. We conducted a short laboratory incubation to investigate the effects of soil compaction on substrate availability and biogenic gas (CO 2 and N 2O) production during the drying and rewetting of a fine-loamy soil. Prior to initiating the drying and wetting treatments, CO 2 production (−10 kPa soil water content) from uncompacted soil was 2.3 times that of compacted soil and corresponded with higher concentrations of microbial biomass C (MBC) and dissolved organic C (DOC). In contrast, N 2O production was 67 times higher in compacted than uncompacted soil at field capacity. Soil aeration rather than substrate availability (e.g. NO 3 − and DOC) appeared to be the most important factor affecting N 2O production during this phase. The drying of compacted soil resulted in an initial increase in CO 2 production and a nearly two-fold higher average rate of C mineralization at maximum dryness (owing to a higher water-filled pore space [WFPS]) compared to uncompacted soil. During the drying phase, N 2O production was markedly reduced (by 93–96%) in both soils, though total N 2O production remained slightly higher in compacted than uncompacted soil. The increase in CO 2 production during the first 24 h following rewetting of dry soil was about 2.5 times higher in uncompacted soil and corresponded with a much greater release of DOC than in compacted soil. MBC appeared to be the source of the DOC released from uncompacted soil but not from compacted soil. The production of N 2O during the first 24 h following rewetting of dry soil was nearly 20 times higher in compacted than uncompacted soil. Our results suggest that N 2O production from compacted soil was primarily the result of denitrification, which was limited by substrates (especially NO 3 −) made available during drying and rewetting and occurred rapidly after the onset of anoxic conditions during the rewetting phase. In contrast, N 2O production from uncompacted soil appeared to be primarily the product of nitrification that was largely associated with an accumulation of NO 3 − following rewetting of dry soil. Irrespective of compaction, the response to drying and rewetting was greater for N 2O production than for CO 2 production.

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