There is an important need to better understand how the soil organic carbon (SOC) stocks affect the global atmospheric C balance. Grasslands represent 40% of the earth’s land surface but efficiently and effectively quantifying their SOC stocks and their changes is a challenge. Although factors influencing the variability of grassland SOC stocks such as climate, management, or topography have been investigated, very few studies have quantified the uncertainty of SOC stock measurement. Quantifying this uncertainty is critical to determine our ability to detect changes in space or time, and ultimately to develop guidance to help designing appropriate measurement strategies for quantifying carbon stocks and stock changes. SOC stock measurement may be performed at various spatial scales, from local (≤1km2) to broader scale (≥100km2) applications. In addition, the recommended sampling depth for SOC measurement varies according to project purposes, national circumstances, and land use. To our knowledge, the assessment based on world literature of the effect of spatial scale (i.e. size of the measured area) and sampling depth on the uncertainty of SOC stock measurement in grasslands has never been performed. We quantified the uncertainty of SOC stock measurement from a global analysis of 51 research articles meeting strict requirements of rigour of SOC measurements, totaling 177 grasslands from 19 countries, to assess the effects of the spatial scale and the sampling depth of soil profile on this uncertainty, and to explore the implications for SOC stock change detection involving future sampling.We observed that spatial scale and soil profile depth combined to explain 44% of the variability of SOC stock uncertainty, as measured by the coefficient of variation (CV). More specifically, the CV increased with the spatial scale and soil profile depth measured. However, the sampling depth effect is less certain due to lack of data at deeper depths. This uncertainty associated with SOC stock measurements has ramifications for SOC stock change detection. For example, at a fixed 0–30cm soil profile depth, the minimum detectable change (MDC) of SOC stocks between two sampling dates (50 samples) was 14, 20 and 29% at 0.1, 10 and 10 000km2, respectively. At a fixed spatial scale of 0.1km2, the MDC was 12, 14 and 18% for soil profiles of 0–10, 0–30 and 0–100cm, respectively. Finally, this study provides global estimates of the uncertainty that will be useful for planning sampling strategies for SOC stock measurement in various projects across the world and to evaluate the feasibility of SOC stock measurement for different investment levels and timescales.
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