05.12.2015 Views

World’s Soil Resources

FAO-world_soils-report-COMPLETE

FAO-world_soils-report-COMPLETE

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

7.2.2 | <strong>Soil</strong> sealing<br />

<strong>Soil</strong> sealing is most commonly associated with the expansion of urban areas and leads to a permanent,<br />

non-reversible loss of agricultural land. Yields are eliminated, not just reduced and the soil, if completely<br />

sealed, becomes effectively non-soil. Urbanization of agricultural land should thus be considered as a threat<br />

to future food production, not only for the loss of good quality agricultural land but also because of the risk<br />

of soil pollution through waste disposal and acid deposition from urban air pollution (Chen, 2007; Hubacek<br />

et al., 2009; Clavero, Villero and Brotons, 2011). Blum and Nortcliff (2013) provide a very rough estimate of<br />

daily losses of soil due to sealing at the global scale of 250-300 km 2 , and suggest this rate could increase due<br />

to continuing migration of rural dwellers to urban areas. Thus, new policies that favour sustainable rural<br />

development, oriented to avoid rural-urban migration as well as to support the return to rural areas of people<br />

living in the cities, could avoid soil degradation and promote food security.<br />

7.2.3 | <strong>Soil</strong> contamination<br />

<strong>Soil</strong> contamination reduces food security both by reducing yields of crops due to toxic levels of contaminants<br />

and by causing the crops that are produced to be unsafe to consume. As summarized in Chapter 6 (Section<br />

6.3), there are worldwide tens of thousands of known contaminated sites due to local or point-source<br />

contamination. In regions with a long-standing industrial base, the expansion of contamination is limited, but<br />

in countries undergoing rapid industrialization or resource development the potential for the further spread<br />

of contamination is great. The tremendous expansion of industry in China is one example of this: 20 million<br />

ha of China’s farmland (approximately one fifth of China’s total farmland) is estimated to be contaminated<br />

by heavy metals, and this may lead to a significant reduction in food availability (see also Section 6.3 above).<br />

Contamination is also severe due to point sources such as Cs pollution from the Fukushima Dai-ichi nuclear<br />

power plant and the Chernobyl disaster of 1983. Diffuse soil contamination occurs in many regions (Blum<br />

and Nortcliff, 2013), but is more commonly linked with concerns about food safety rather than significant<br />

decreases in crop yields.<br />

7.2.4 | Acidification<br />

Acidification of agricultural soils is primarily associated with the net removal of base cations (e.g. product<br />

removal without replacement with ameliorants such as lime) and the direct addition of acidifying inputs (e.g.<br />

ammonium-based N fertilizer) to inherently low-pH soils, which have a low capacity to buffer added acidity. It<br />

is most prevalent on ancient, highly weathered soils. Acidification is a significant regional threat in countries<br />

such as Australia and Vietnam (see Chapters 10 and 15). Liming is an effective response to control acidity of<br />

surface horizons, but rates of lime addition lag behind required levels even in developed countries like Australia<br />

(SOE, 2011) and continuing loss of yield occurs.<br />

7.2.5 | Salinization<br />

Salinization in a soil progressively reduces crop yields; beyond a certain crop-specific threshold, growth of<br />

a given crop may fail entirely. The regional summaries in Chapters 9 to 16 illustrate how difficult it often is to<br />

separate the causes of salinization: whether the saline soils are naturally occurring (primary salinization) or<br />

the salinization has been caused by inappropriate management, which is often the case with poorly executed<br />

irrigation programmes (secondary salinization). Estimates from the 1990s place the land area affected by<br />

primary salinization at approximately one billion ha, and the area of land with secondary salinization at 77<br />

million ha (Ghassemi, Jakeman and Nix, 1995).<br />

Salinization is typically associated with arid and semi-arid areas, and may be exacerbated by climate<br />

change (see also Section 6.5). An increase in irrigated land is commonly suggested as a means to increase<br />

food production, but poorly designed and implemented irrigation schemes can readily cause an increase in<br />

Status of the <strong>World’s</strong> <strong>Soil</strong> <strong>Resources</strong> | Main Report The impact of soil change on ecosystem services<br />

178

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!