Abstract

Grasslands cover up to 40.5% of the world's landmass and store 30% terrestrial carbon (C). Various practices, including mineral fertilization and liming, are used to manage these ecosystems with potential long-term effects on the size and distribution of soil aggregates and inevitably carbon dynamics. The objective of this study was to examine the long-term effects of nitrogen fertilization and liming on soil carbon storage and its dynamics in water-stable aggregates of a semi-arid grassland. Soil samples (0–10 cm) were collected from Ukulinga long-term grassland trial in Pietermaritzburg, South Africa where nitrogen fertilizers have been applied annually and lime every five years for 70 years. Ten treatments were studied: the control (0 kgN/ha and unlimited), lime at 2250 kg/ha (L), ammonium sulphate at 70 kg/ha (AS70) and 211 kg/ha (AS211); ammonium nitrate at 70 kg/ha (AN70) and 211 kg/ha (AN211); AS70 + lime (AS70L); AS211 + lime (AS211L); AN70 + lime (AN70L) and AN211 + lime (AN211L).Nitrogen fertilizers significantly reduced soil pH and increased total soil N. Liming increased soil pH with no effect on total soil N. Lime and lime + N fertilizer treatments had no effect on mean weight diameter (MWD) while separate N application decreased MWD and large macro-aggregates (LMA). Lime only treatment had no effect on water stable aggregate (WSA) fractions. Nitrogen fertilization and liming (separately or in combination) did not affect total C concentration and stocks. Overall, soils had very high total soil organic carbon ranging from 49.7 – 57.6 g/kg across treatments. Nitrogen fertilization decreased organic carbon in LMA in AS70 (1.52%) and AN211 (1.67%) treatments compared to the control (3.40%) which was in concert with increases in C associated with small macro-aggregates (SMA) and micro-aggregates (MiA and SCA). Organic carbon in SMA was 2.67 % (AS70); AS211 (2.62 %); AN70 (2.02 %); AN211 (2.49 %) compared to 1.26 % in the control. Lime + N fertilizer treatments increased C storage in all aggregate fractions compared to N fertilizer only treatments. The lack of response in total SOC to 70 years of N fertilization and liming suggests possible C saturation given the high soil C concentration. Changes in C associated with WSA fractions suggests their importance as diagnostic indicators of N fertilization and liming induced changes in SOC. Findings also show that ammonium-based N fertilization is associated with soil acidification, dispersion of LMA resulting in an increase of microaggregates and C stored in them. Liming can counteracts acidifying and the dispersive effect on NH4+ associated with ammonium-based fertilizers thus restoring macro-aggregation in N fertilized grasslands. These findings suggests that long-term N addition may result in poor soil physical condition and possible stabilization of C in stable fractions.

Highlights

  • Grasslands are considered among the worlds’ largest ecosystems consisting of rangelands, shrublands, pastureland and croplands sown with pasture and fodder crops (Rumpel et al, 2015)

  • This study focused on nitrogen, applied annually as ammonium nitrate and ammonium sulphate at 70 and 211 kg N/ha and dolomite lime applied at 2250 kg/ha every five years

  • The findings of this study showed that long-term N addition resulted in soil acidification and redistribution of organic C in water-stable aggregates at Ukulinga grassland

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Summary

Introduction

Grasslands are considered among the worlds’ largest ecosystems consisting of rangelands, shrublands, pastureland and croplands sown with pasture and fodder crops (Rumpel et al, 2015). These ecosystems are estimated to cover up to 52.5 million square kilometres (Suttie et al, 2005), which make up to 40.5 % of the terrestrial area. Grasslands store about 30 % of terrestrial C (Cenini et al, 2015) and contribute significantly to carbon and nutrient cycling Management practices such as liming and nitrogen fertilization, widely used on often N-limited grasslands, affect soil physicochemical properties of this ecosystem. Nitrogen availability has a major control on soil C cycling and storage (Averill and Waring, 2018)

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