4.7 Article

Rewetting and litter addition influence mineralisation and microbial communities in soils from a semi-arid intermittent stream

Journal

SOIL BIOLOGY & BIOCHEMISTRY
Volume 41, Issue 1, Pages 92-101

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.soilbio.2008.09.021

Keywords

Substrate limitation; Flood pulse; Pilbara; Carbon mineralisation; Nitrogen mineralisation; Microbial biomass; Phospholipid fatty acids

Categories

Funding

  1. Australian Research Council
  2. Pilbara Iron Ply Ltd.

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Nitrogen (N) and carbon (C) mineralisation are triggered by pulses of water availability in and and semiarid systems. Intermittent streams and their associated riparian communities are obvious 'hot spots' for biogeochemical processes in and landscapes where water and often C are limiting. Stream landscapes are characterized by highly heterogeneous soils that may respond variably to rewetting. We used a laboratory incubation to quantify how N and C mineralisation in rewetted soils and sediments from an intermittent stream in the semi-arid Pilbara region of north-west Australia varied with saturation level and substrate addition (as ground Eucalyptus litter). Full (100%) saturation was defined as the maximum gravimetric moisture content (%) achieved in free-draining soils and sediments after rewetting, with 50% saturation defined as half this value. We estimated rates and amounts of N mineralised from changes in inorganic N and microbial respiration as CO2 efflux throughout the incubation. In soils and sediments subject to 50% saturation, >90% of N mineralised accumulated within the first 7 d of incubation, compared to only 48% when soils were fully saturated (100% saturation). Mineralisation rates and microbial respiration were similar in riparian and floodplain soils, and channel sediments. N mineralisation rates in litter-amended soils and sediments (0.73 mg N kg(-1) d(-1)) were only one-third that of unamended samples (3.04 mg N kg(-1) d(-1)), while cumulative microbial respiration was doubled in litteramended soils, suggesting N was more rapidly immobilized. Landscape position was less important in controlling microbial activity than soil saturation when water-filled pore space (% WFPS) was greater than 40%. Our results suggest that large pulses of water availability resulting in full soil saturation cause a slower release of mineralisation products, compared to small pulse events that stimulate a rapid cycle of C and N mineralisation-immobilization. (c) 2008 Elsevier Ltd. All rights reserved.

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