The long-term effects of elevated CO₂ on soil organic carbon sequestration, partitioning and persistence in a grazed pasture : a thesis presented in partial fulfilment of the requirements for the degree of Doctor in Philosophy in Soil Science at Massey University, Manawatu, New Zealand
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2024-03-04
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Massey University
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Abstract
The increased concentration of atmospheric carbon dioxide (CO₂) is a significant driver for climate change and also influences the cycling of soil organic carbon (OC) in ecosystems. Despite the importance of grassland soils as a sink for CO₂, the effect of long-term exposure to elevated CO₂ (eCO₂) on OC sequestration, partitioning and persistence in grazed grassland soils is poorly understood. This thesis aimed to investigate the effect of eCO₂ on soil OC stocks, the partitioning of OC in soil fractions and persistence in a grazed legume-based pasture at the New Zealand (NZ) Free Air CO₂ Enrichment (FACE) facility. The NZ-FACE, established in 1997, is the only FACE experiment worldwide that includes the influence of grazing practices on the above- and below-ground components of the OC cycle. The effect of eCO₂ on soil OC persistence and stability was assessed by measuring changes in soil OC stock, in the distribution of soil OC in the soil fractions by wet fractionation analysis and in the soil OC decomposition pathways by determining the molecular composition of soil organic matter (OM) by pyrolysis analysis followed by gas chromatography/mass spectroscopy (GC-MS) and thermally assisted hydrolysis methylation-GC-MS (THM-GC-MS) analysis to a soil depth of 250 mm.
In Chapter 3, we assessed OC storage and persistence in the soil fractions in a grazed legume- based pasture exposed to eCO₂ for 22 years on Pukepuke soil (Mollic Psammaquent) at three soil depths. Our study revealed that after 22 years of exposure to eCO₂ there were no significant changes in the stocks of OC and N as well as the partitioning of OC within different soil fractions in the Pukepuke soil. Interestingly, in the last 10 years at the NZ-FACE facility, there has been a sharp reduction of OC and N stocks in the Pukepuke soil, independent of the CO₂ treatment. We suggest that in the sandy Pukepuke soil under conditions of warmer temperatures and a wetter system, the deficiency that has emerged in soil nutrient availability, the environmentally enhanced plant growth and the larger amounts of fresh OM input has caused a positive priming effect, mainly in the labile fraction. Even though eCO₂ did not change the soil OC stocks nor OC content in the soil fractions in any soil layer, it did modify the soil nutrient status (phosphate in particular) and did increase polysaccharides and aliphatic proportions in the coarse particulate organic matter and micro-aggregates indicating that the priming was further enhanced in eCO₂ soils with this effect being especially prominent in the 50 – 150 mm soil layer (Chapter 3).
In Chapter 4, the hypothesis that grazing animals, by returning nutrients in urine, dung, and plant litter trampled into the soil surface, would contribute to an increase in soil OC and N stocks under eCO₂ was investigated and rejected. Despite not finding any interaction effect between eCO₂ and defoliation treatment on the soil OC stocks and partitioning in the soil fractions, the presence of an interaction effect in the soil OM molecular composition suggests that distinctly different OC decomposition pathways exist depending on pastures management under eCO₂. Our study showed that under grazing there was an accumulation of lignin-derived OM, which reveals a higher proportion of shoot-derived rather than root- derived OC under eCO₂.
In Chapter 5, the influence of the inherent properties of a soil – which might enhance or limit the effects of eCO₂ on soil OC persistence and stability – was examined in two contrasting soils (Pukepuke and Stratford; a Entic Dystrandept) in mesocosms installed at the NZ-FACE in May 2005 and extracted after 15 years. Our results showed that over the course of the mesocosm study, OC and N contents and stocks (to 150 mm soil depth) in the Pukepuke soil declined by 16 t ha-1 under ambient CO₂ atmosphere, possibly as a result of soil disturbance during the establishment of the mesocosms. In the Stratford soil, with the ability to strongly preserve OM through mineral associations, the decline in soil OC was much smaller (5 t ha-1). Elevated CO₂ interacted with soil type and after 15 years of exposure to eCO₂, the Pukepuke soil had 6.5 t ha-1 more OC stocks, compared to the same soil under ambient CO₂ conditions, while no differences were found in the OC stocks of the Stratford soil (Chapter 4). These findings indicate that in the Pukepuke soil the eCO₂ treatment might have (i) helped overcome the impact of disturbance by favouring plant growth and generating a larger plant detritus input to the soil that enabled the partial replenishment of the OC loss at the time of mesocosm establishment, or (ii) limited the impact of disturbance, as eCO₂ often improves soil aggregation. It is crucial to consider that (i) the Stratford soil was subjected to ~50% less precipitation at the NZ-FACE compared to its original location and (ii) the mesocosm might have introduced new variables due to physical barriers. Thus, extrapolating the findings to field conditions at the NZ-FACE facility and elsewhere requires cautious interpretation.
The findings presented in this thesis contribute significantly to enhancing our understanding of the mechanistic processes underlying the influence of eCO₂ on the stabilization and mineralization of soil OM. These insights have direct implications for the development of sustainable agricultural management practices in response to a changing environment.
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elevated CO₂, FACE facility, grazing, soil organic carbon, carbon sequestration, Soil biochemistry, Pastures, Soils, Carbon dioxide sinks, Carbon sequestration, New Zealand