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World’s Soil Resources

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Following GLASOD, the need for more detailed and more country-specific degradation assessments<br />

became apparent. In 1993, the members of the Asian Network on Problem <strong>Soil</strong>s recommended the preparation<br />

of a qualitative assessment for South and Southeast Asia at a scale of 1:5 million. This recommendation was<br />

acknowledged by FAO and UNEP. FAO assigned ISRIC to prepare a new physiographic map and database<br />

at 1:5 million scale. UNEP prepared and implemented the Assessment of the Status of Human-Induced <strong>Soil</strong><br />

Degradation in South and Southeast Asia (ASSOD). Sixteen national institutions for natural resources in the<br />

region collaborated on the project under the coordination of ISRIC. The ASSOD project published revised subregional<br />

Guidelines for General Assessment of the Status of Human-Induced <strong>Soil</strong> Degradation and produced<br />

regional maps on the status of human-induced soil degradation at a scale of 1:5M together with digitized<br />

version of the map (van Lynden and Oldeman, 1997).<br />

The different soil degradation types inventoried by ASSOD are described below and shown in Figure 10.2:<br />

• Water erosion: Water erosion covers 21 percent of the total land area in the region (or 46 percent of the<br />

total degraded area). It is predominant in large parts of China (>180 million ha) except for the northern<br />

parts, on the Indian subcontinent (>90 million ha) and in the sloping parts of Indochina (40 million ha),<br />

the Philippines (10 million ha) and Indonesia (22.5 million ha). In relative terms, as a percentage of the<br />

total country area, moderate to extreme water erosion is particularly important in India (10 percent),<br />

the Philippines (38 percent), Pakistan (12.5 percent), Thailand (15 percent) and Vietnam (10 percent).<br />

• Wind erosion: Wind erosion (9 percent of the total area, 20 percent of all degradation) is concentrated<br />

mainly in the most western and northern arid and semi-arid desert regions of Pakistan (>9 million ha<br />

on-site and >2 million ha off-site), India (20 million ha on-site, 3.6 million ha offsite) and China (>70<br />

million ha on-site, >8.5 million ha off-site). Although large parts of these regions may be considered<br />

deserts, some human-induced wind erosion was also reported.<br />

• Chemical deterioration: Chemical deterioration is distributed in patches, probably also partly due to<br />

different perceptions of this type of degradation. About 11 percent of the total area (or 24 percent of the<br />

degraded area) is affected by some kind of chemical deterioration. High relative extents of chemical<br />

deterioration (>30 percent of total country area) can be observed in Bangladesh, Cambodia, Sri Lanka,<br />

Malaysia, Pakistan and Thailand, generally with negligible to light impact.<br />

• Physical deterioration: Occurrence of physical deterioration (affecting about 4 percent of the total<br />

area or 9 percent of the total degraded area) is even more dispersed and infrequent than chemical<br />

deterioration. Waterlogging and aridification are the main subtypes, in particular in Bangladesh,<br />

China, India and Pakistan. Compaction or crusting/sealing is relatively unimportant except in Thailand<br />

and the Philippines, although they occur in most countries. Waterlogging and compaction as a result<br />

of paddy cultivation are not considered as degradation. Loss of productive function as a result of<br />

urbanisation, industrialisation and infrastructure has been indicated for only a few countries although<br />

this phenomenon is on the rise.<br />

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

290<br />

in Asia

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