Mineralization of Amino Acids Applied to Soils Impact of Soil Sieving, Storage, and Inorganic Nitrogen Additions

The effect of inorganic N additions on the biodegradation and microbial use of organic N pools in soil is poorly understood. To examine the effects of inorganic N on the mineralization rates of amino acids, four soils under contrasting management regimes were subjected to increasing loadings of NH 4 NO 3 , ranging from 0 to 120 kg N ha −1 In addition, the effect of soil sieving and storage temperature and time on amino acid mineralization was also investigated. At times ranging from 1 to 40 d after the addition of the inorganic N, the mineralization kinetics of an equimolar mixture of fifteen 14 C‐labeled amino acids was followed for a subsequent 24‐h period. The rate of 14 CO 2 evolution was soil dependent, with half‐lives ranging from 2 h for topsoils to 25 h for subsoils. For all soils, at all times, and at all inorganic‐N loadings, the addition of inorganic N appeared to have little effect on the mineralization kinetics of the amino acids to 14 CO 2 In addition, the presence of inorganic N also had no major effect on the C use efficiency of the microbial biomass. It is speculated that N release from the amino acids into the soil by the microbial biomass may also be little affected by inorganic‐N additions. Sieving and storage of soil at either 4 or 18°C for up to 40 d had little impact on amino acid mineralization rate. Experiments with potential microbial disrupting agents (autoclaving, CHCl 3 fumigation, HgCl 2 , and freeze–thaw) all indicated that the observed mineralization of amino acid C was due to microbial activity. We conclude therefore that inorganic N and soil storage has little effect on the microbial use of readily assimilatable amino acids.