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World’s Soil Resources

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Box 6.2 | Nutrient balances in urban vegetable production in West African cities<br />

Based on a two year study of urban gardening sites in Niamey (Niger), it was found that N, P and K<br />

balances were all positive, with values for high and low input gardens respectively of 1133 and 290 kg ha -1<br />

for N; 223 and 125 kg ha -1 for P; and 312 and 351 kg ha<br />

-1 for K. Similar N and P balances were reported for<br />

urban vegetable gardens in Kano (Nigeria), Bobo Dioulasso (Burkina Faso) and Sikasso (Mali). However, at<br />

these latter sites, K balances tended to be negative. Overall, urban vegetable production sites appear to be<br />

major nutrient sinks from which large environmental externalities can be expected.<br />

Bouwman, Beusen and Billen (2009) evaluated the impact of four future development scenarios on<br />

nutrient balances for the year 2050. The scenarios, describing contrasting future development in agriculture<br />

nutrient use under changing climate, are based on the Millennium Ecosystem Assessment. In the most<br />

pessimistic case, the global N balance may increase by 50 percent in the coming decades. In case of proactive<br />

policies aiming at closing the nutrient balance, the N balance is expected to remain constant at 150 Tg yr -1 .<br />

Regarding P, all scenarios predict a future increase in global soil P balance. These global balances hide large<br />

variations across regions and even across land uses. Unfertilized rangelands are likely to maintain negative<br />

P balances. Scenarios with a reactive approach to environmental problems portray significant increases in N<br />

and P balances in Asia, Central and South America and Africa, which can be strongly reduced by a proactive<br />

approach. For North America, Europe and Oceania, a shift from reactive to proactive environmental policies<br />

could allow limiting the increase in N and P balances, or even a decrease in the overall nutrient balance.<br />

Whereas large positive nutrient balances sustained for extended periods of time in industrialized countries<br />

have resulted in negative environmental externalities, positive nutrient balances should not be viewed as<br />

necessarily environmentally harmful. Indeed, in many developing regions (e.g. sub-Saharan Africa), positive<br />

P balances are needed to restore soil fertility potential depleted by long lasting nutrient mining and to boost<br />

the often very low crop yields. Inputs of N in organic form may also be beneficial as part of a strategy to restore<br />

the soils’ organic carbon stocks. Possible negative environmental externalities should be weighed against the<br />

benefits of food security, economic welfare and social well-being. To minimize the negative externalities, the<br />

best nutrient management approaches should be promoted through judicious policies.<br />

6.9 | <strong>Soil</strong> compaction status and trends<br />

<strong>Soil</strong> compaction is an important problem affecting productivity of soils across the globe. A hidden problem<br />

of soils occurring on or below the surface, compaction impairs the function of the subsoil by impeding<br />

root penetration and water and gaseous exchanges (McGarry and Sharp, 2003). <strong>Soil</strong> compaction reduces soil<br />

macroporosity e.g. from an optimum of 6 to 17 percent, and hence reduces pasture and crop yield (Drewry,<br />

Cameron and Buchan, 2008).<br />

<strong>Soil</strong> compaction in most circumstances is a function of soil type (texture, mineralogy, organic matter),<br />

soil-water content and land management (e.g. tillage practices, traffic, grazing intensity). The problem is not<br />

limited to crop land but is also prevalent in rangelands and grazing fields, and even in natural non-disturbed<br />

systems. <strong>Soil</strong> compaction occurs when compressible soils are subjected to traction e.g. in forest harvesting,<br />

amenity land use, pipeline installation, land restoration, wildlife trampling (Batey, 2009) or winter grazing<br />

(Tracy and Zhang, 2008).<br />

Trampling mechanically disrupts soil aggregates and reduces aggregate stability (Warren et al., 1986) and<br />

its effect increases with stocking intensity (Willatt and Pullar, 1983). The degree of damage associated with<br />

Status of the <strong>World’s</strong> <strong>Soil</strong> <strong>Resources</strong> | Main Report Global soil status, processes and trends<br />

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