Inma Lebron Robinson
2010 – Present Centre for Ecology and Hydrology, Bangor, Gwynedd
Environmental/soil chemist
2008 – 2009 University of the West Indies, Trinidad
Lecturer, Soil and Environmental Chemistry
2005 - 2008 Stanford University, USA
Consulting faculty
2004 - 2005 Utah State University, USA
Assistant Research Professor
1998 - 2004 University of California, Riverside/USDA Salinity Laboratory, USA
Assistant Research Scientist III
1992 - 1998 University of California, Riverside/USDA Salinity Laboratory, USA
Research Scientist
1989 - 1991 USDA Salinity Laboratory, USA
Visiting Scientist
1984 - 1989 Consejo S. de Investigaciones Cientificas, Spain
Research Assistant
1983 - 1984 University of Zaragoza, Spain
Laboratory manager, Teaching Assistant
Sessions
Soil pH indicates the level of acidity or alkalinity in the soil environment, influencing various biogeochemical and physical processes. Additionally, soil pH levels are
crucial in determining the bioavailability of elements such as iron, aluminium, and heavy metals which can be harmful. As such, pH is an important soil health and
degradation indicator. Although there is a well-established understanding of soil pH at localized levels, the spatial and temporal variations, as well as significant
thresholds at national and continental scales, are not sufficiently documented. Here we analyse the European topsoil pH data (LUCAS) in combination with other soil
properties from the LUCAS survey, to identify thresholds and spatial patterns of soil pH across Europe in relation to soil health and degradation. At the European scale
we found: 1) the water balance, calculated as mean annual precipitation minus potential evapotranspiration (MAP-PET), provides essential context to interpret soil
pH; 2) the shift from organic carbon-rich soils to those dominated by inorganic carbon is observed at a pH of about 7.2, however, soil moisture levels may be more
critical than pH for the accumulation of soil organic carbon; 3) we identified three distinct clusters within the multivariate regression tree: acidophiles (below pH
5.2), neutrophiles (pH 5.2–6.9) and alkaliphiles (above pH 6.9), while optimum microbial diversity occurred between pH 6 and 7. Earthworm abundance, as reported
by the sWorm database, is more nuanced and dependent on land use; 4) risk of degradation by heavy metals cannot be captured by a single pH threshold. Finally, we
identify soil pH thresholds that can aid policymakers in identifying regions that may require protection or intervention.