Microbial dynamics and carbon and nitrogen cycling following re-wetting of soils beneath two semi-arid plant species
- 14 October 2004
- journal article
- research article
- Published by Springer Nature in Oecologia
- Vol. 142 (2) , 247-260
- https://doi.org/10.1007/s00442-004-1718-9
Abstract
Sporadic summer rainfall in semi-arid ecosystems can provide enough soil moisture to drastically increase CO2 efflux and rates of soil N cycling. The magnitudes of C and N pulses are highly variable, however, and the factors regulating these pulses are poorly understood. We examined changes in soil respiration, bacterial, fungal and microfaunal populations, and gross rates of N mineralization, nitrification, and NH4 + and NO3 − immobilization during the 10 days following wetting of dry soils collected from stands of big sagebrush (Artemisia tridentata) and cheatgrass (Bromus tectorum) in central Utah. Soil CO2 production increased more than tenfold during the 17 h immediately following wetting. The labile organic C pool released by wetting was almost completely respired within 2–3 days, and was nearly three times as large in sagebrush soil as in cheatgrass. In spite of larger labile C pools beneath sagebrush, microbial and microfaunal populations were nearly equal in the two soils. Bacterial and fungal growth coincided with depletion of labile C, and populations peaked in both soils 2 days after wetting. Protozoan populations, whose biomass was nearly 3,000-fold lower than bacteria and fungi, peaked after 2–4 days. Gross N mineralization and nitrification rates were both faster in cheatgrass soil than in sagebrush, and caused greater nitrate accumulation in cheatgrass soil. Grazing of bacteria and fungi by protozoans and nematodes could explain neither temporal trends in N mineralization rates nor differences between soil types. However, a mass balance model indicated that the initial N pulse was associated with degradation of microbial substrates that were rich in N (C:N <8.3), and that microbes had shifted to substrates with lower N contents (C:N =15–25) by day 7 of the incubation. The model also suggested that the labile organic matter in cheatgrass soil had a lower C:N ratio than in sagebrush, and this promoted faster N cycling rates and greater N availability. This study provides evidence that the high N availability often associated with wetting of cheatgrass soils is a result of cheatgrass supplying substrates to microbes that are of high decomposability and N content.Keywords
This publication has 47 references indexed in Scilit:
- Non-biomass soil organic N — the substrate for N mineralization flushes following soil drying–rewetting and for organic N rendered CaCl2-extractable upon soil dryingSoil Biology and Biochemistry, 1998
- Mineralisation of soil organic nitrogen and microbial respiration after simulated summer rainfall events in an agricultural soilSoil Research, 1998
- Rates of germ tube formation from growing and non-growing yeast cells ofCandida albicansFEMS Microbiology Letters, 1991
- An extraction method for measuring soil microbial biomass CSoil Biology and Biochemistry, 1987
- Modifications to the substrate-induced respiration method to permit measurement of microbial biomass in soils of differing water contentsJournal of Microbiological Methods, 1986
- Trophic Interactions and Nitrogen Cycling in a Semi-Arid Grassland Soil. I. Seasonal Dynamics of the Natural Populations, Their Interactions and Effects on Nitrogen CyclingJournal of Applied Ecology, 1986
- Biological Aspects of Nitrogen Mineralization in Humus from a Pine Forest Podsol Incubated under Different Moisture and Temperature ConditionsOikos, 1981
- A carbon budget for nematodes, rotifers and tardigrades in a Swedish coniferous forest soilEcography, 1979
- Trophic interactions in soils as they affect energy and nutrient dynamics. IV. Flows of metabolic and biomass carbonMicrobial Ecology, 1977
- The effect of soil drying on humus decomposition and nitrogen availabilityPlant and Soil, 1958