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World’s Soil Resources

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List of figures<br />

Figure 2.1 | Overview of ecosystem processes involved in determining the soil C balance. | 14<br />

Figure 2.3 | Global (a) nitrogen (N) and (b) phosphorus (P) fertilizer use between 1961 and 2012 split for<br />

the different continents in Mt P per year. Source: FAO, 2015. | 19<br />

Figure 2.4 | Applied and excess nitrogen and phosphorus in croplands. Nitrogen and phosphorus<br />

inputs and excess were calculated using a simple mass balance model, extended to include 175 crops.<br />

To account for both the rate and spatial extent of croplands, the data are presented as kg per ha of the<br />

landscape: (a) applied nitrogen, including N deposition; (b) applied phosphorus; (c) excess nitrogen;<br />

and (d) excess phosphorus. Source: West et al., 2014. | 20<br />

Figure 3.1 | Nutrient availability in soils. Source: Fischer et al., 2008. | 36<br />

Figure 3.2 | Global soil rooting conditions. Source: Fischer et al., 2008. | 36<br />

Figure 3.3 | <strong>Soil</strong> Moisture storage capacity. Source: Van Engelen, 2012. | 38<br />

Figure 3.4 | <strong>Soil</strong> Organic Carbon pool (tonnes C ha -1 ). | 39<br />

Figure 3.5 | <strong>Soil</strong> erodibility as characterized by the k factor. Source: Nachtergaele and Petri, 2011. | 40<br />

Figure 3.6 | <strong>Soil</strong> workability derived from HWSD. Source: Fischer et al., 2008. | 40<br />

Figure 3.7 | <strong>Soil</strong> suitability for cropping at low input, based on the global agro-ecological zones study.<br />

Source: Fischer et al., 2008. | 41<br />

Figure 3.8 | GLASOD results. Source: Oldeman, Hakkeling and Sombroek, 1991. | 44<br />

Figure 3.9 | Example of the effect of land use on indicative factors for ecosystem goods and services | 45<br />

Figure 3.10 | <strong>Soil</strong> compaction risk derived from intensity of tractor use in crop land and from livestock<br />

density in grasslands. Source: Nachtergaele et al., 2011 | 46<br />

Figure 4.1 | Global Land Cover. Source: Latham et al., 2014. | 51<br />

Figure 4.2 | Distribution of land cover in different regions. Source: Latham et al., 2014. | 51<br />

Figure 4.3 | Historical land use change 1000 – 2005. Source: Klein Goldewijk et al., 2011. | 54<br />

Figure 4.4 | <strong>Soil</strong> carbon and nitrogen under different land cover types. Source: Smith et al. (in press). | 57<br />

Figure 4.5 | Maps of change in soil carbon due to land use change and land management from 1860 to<br />

2010 from three vegetation models. Pink indicates loss of soil carbon, blue indicates carbon gain. The<br />

models were run with historical land use change. This was compared to a model run with only natural<br />

vegetation cover to diagnose the difference in soil carbon due to land cover change. Both model runs<br />

included historical climate and CO 2<br />

change. Source: Smith et al. (in press). | 58<br />

Figure 4.6 | Schematic diagram showing areas sealed (B) as a result of infrastructure development for<br />

a settlement (A). Source: European Union, 2012. | 66<br />

Figure 4.7 | (A) Panoramic view of Las Medulas opencast gold mine (NW Spain). The Roman extractive<br />

technique – known as ‘ruina montis’ – involved the massive use of water that resulted in important<br />

geomorphological changes; (B) Weathered gossan of the Rio Tinto Cu mine, considered the birthplace<br />

of the Copper and Bronze Ages; (C) typical colour of Rio Tinto (‘red river’ in Spanish), one of the best<br />

known examples of formation of acid mine waters. These are inhabited by extremophile organisms.<br />

| 69<br />

Status of the <strong>World’s</strong> <strong>Soil</strong> <strong>Resources</strong> | Main Report<br />

XXXV

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