World’s Soil Resources

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Figure A 19 (a) A Kastanozem profile and (b) the associated landscape in Mongolia. a Photo by O. Bathkhishig b Photo by O. Bathkhishig Status of the World’s Soil Resources | Main Report Annex | Soil groups, characteristics, 564 distribution and ecosystem services
PHAEOZEMS (Udolls and Albolls) Phaeozems are soils with a mollic horizon which occur most frequently in the transitional areas between boreal forests and steppes, or in forest-free plains with temperate semi-humid climate (tall-grass prairies) on unconsolidated base-rich sediments, mostly loess or loess-like material. They may also occur locally under sparse herbaceous forests in the mountains (Figure A 20). They cover approximately 2 million km 2 , and their largest areas are found in the United States (Great Plains) and Canada, in the Argentinian Pampas, and in Manchuria. Mountainous variants were described in Southern Siberia and Northern Mongolia on gentle slopes with colluvium, under larch forests with a rich forb-grass cover (Zech et al., 2014; Vostokova and Gunin, 2005). Phaeozems are formed under milder and more humid climates than Chernozems; the vegetation is mesophytic with less pronounced seasonal rhythms. Typically, natural grassland cover is mostly replaced by high-quality farmland, or may be modified by grazing. Phaeozems are among the most fertile soils owing to their favourable physical and chemical properties, along with moisture and thermic regimes (udic and mesic). The most conspicuous feature of Phaeozems is their dark, mostly thick, mollic horizon with traces of burrowing mammal activity, weakly acid to neutral, base saturation ranging within 50-100 percent. Phaeozems include some of the traditional forest-steppe Chernozems with deep secondary carbonates, and in this case they have a chernic horizon with its coprogenic structure underlain by a cambic or argic horizon. In the rest of Phaeozems, the subsoil horizons may be diverse: argic, cambic, calcic and petrocalcic; the latter phenomenon is common in Argentinian Phaeozems – a specific hard tosca layer that may occur within 1 m from the soil surface and be a limitation for plant growth (Moscatelli, 1991; Pazos, 2012). Some other properties were described in Phaeozems as well: albic material and uncoated silt grains, clay coatings, stagnic colour pattern, and sodic features (FAO, 2014). This broad array of properties is explained by the occurrence of Phaeozems in different environments providing for the development of additional pedogenic processes, some of them being limitations for farming. The global significance of Phaeozems is their high agricultural potential, as well as the prominent reserves of organic carbon accumulated in their topsoils. The limitations are not strong: they include wind erosion in dry years, water erosion on uplands, and water stagnation either during short rainy events or in case of high groundwater. In Manchuria, deep freezing and slow thawing are common. Local manifestations of sodicity have been recorded in Argentina and Western Siberia (Gerasimova, 2002). Status of the World’s Soil Resources | Main Report Annex | Soil groups, characteristics, 565 distribution and ecosystem services
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Status of the World’s Main Report
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Dick, Warren Dos Santos Baptista, I
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Table of contents Disclaimer and co
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4.1 | Current land cover and land u
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6.5.5 | Responses | 126 6.6 | Soil
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7.7.3 | Soil and drought hazard | 1
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9.5.2 | South Africa | 266 9.6 | Su
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12.3.8 | Soil acidification | 373 1
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14.5.4 | Nutrient imbalance | 464 1
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Foreword This document presents the
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Preface | Scope of The State of the
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Acknowledgments The Status of the W
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CACILM CAMRE CAZRI CBD CBM-CFS CCAF
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FDNPS FFS FIA FSI FSR GAP GDP GEF G
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LU MA MADRPM MAF MAFF MDBA MDGS MEN
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SKM SLAM SLC SLM SMAP SMOS SOC SOE
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List of tables Table 1.1 | Chronolo
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List of figures Figure 2.1 | Overvi
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Figure 6.15 | Factors controlling s
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Figure 11.4 | Soil map and soil deg
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colored diaper associated with micr
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Preface The main objectives of The
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Global soil resources Coordinating
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The balance between the supporting
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1.2 | Basic concepts Prior to the 2
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Soil functions and ecosystem servic
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Climate regulation ∑ Regulation o
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2 | The role of soils in ecosystem
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2.1.2 | Nature and formation of soi
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2.1.4 | Factors influencing soil C
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In coming years, human population a
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Management practices need to be imp
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Another important role of soil wate
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The development of molecular techno
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Fierer, N., Ladau, J., Clemente, J.
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Sato, T., Qadir, M., Yamamoto, S.,
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3 | Global Soil Resources 3.1 | The
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Fridland’s was the first attempt
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Soil management has a considerable
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Accumulation of water soluble salts
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and increases infiltration, which r
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Figure 3.7 Soil suitability for cro
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3.7 | Global assessments of soil ch
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3.7.2 | LADA-GLADIS: the ecosystem
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References AFES. 2008. Réferentiel
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Neustuev, S.S. 1931. Elements of So
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75% crops Mixed >50% artificial 50-
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or increasing forest areas. Between
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Degrading land covers approximately
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70 60 (A) soil carbon 50 Soil
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A meta-analysis of 57 publications
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the nutrient inputs remain in the c
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Livestock density Livestock product
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4.3.3 | Land use change resulting i
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Impact of land take Land take, by i
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Photo by F. Macias Photo by J.C. Fe
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The formation of sulfidic material
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are however strongly dependent on t
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Figure 4.10 Global distribution of
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Bardgett, R.D. & van der Putten, W.
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Dentener, F., Drevet, J., Lamarque,
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Hettelingh, J.P., Sliggers, J., van
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Magnani, F., Mencuccini, M., Borghe
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Pugh, T.A.M., Arneth, A., Olin, S.,
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Van Aardenne, J.A., Dentener, F.J.,
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5 | Drivers of global soil change D
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5.1.2 | Urbanization In tandem with
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Large areas of arable land have bee
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most affected zone with 15 million
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(Brito et al., 2005). This has impl
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MA. 2005. Ecosystems and Human Well
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6.1.2 | Status of Soil Erosion Over
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Figure 6.2 Location of active and f
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High soil erosion rates will also h
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Near-surface soil water content has
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6.2 | Global soil organic carbon st
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where the drainage in the 1960’s
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6.2.4 | Spatial distribution of car
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Vegetation Classes Topsoil Subsoil
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Soil Order Historic Area 10 6 ha Pr
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6.3 | Soil contamination status and
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and Uruguay. The number of exposed
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products increase soil acidity (Bar
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availability and inhibit plant grow
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In several Asian countries, a blend
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underlines the need for global-scal
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Figure 6.10 Urbanisation of the bes
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Figure 6.11 Major components of the
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Within the same continent, large va
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Box 6.2 | Nutrient balances in urba
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is among the top options in the por
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The quality of the soil’s water i
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At continental scales, the only pra
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Figure 6.16 (a) Global distribution
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Engineering in Japan, 5: 157-174. A
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Chadwick, D., Sommer, S., Thorman,
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Drechsel, Pay, Giordano, Mark, Gyie
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Gardner, T., Acosta-Martinez, V., C
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Hue, N.V. & Licudine, D.L. 1999. Am
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Liski, J., Ilvesniemi, H., Mäkelä
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Ng, H. 2010. Regional Assessment: S
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Reheis, M. 1997. Dust deposition do
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Smith, K.A., McTaggart, I.P. & Tsur
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United Nations. 2008. World Urbaniz
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Wood, M.K. & Blackburn, W.H. 1984.
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7 | The impact of soil change on ec
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Rockström et al. (2009) suggest we
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0.0 Response 1.0 Water quality Soil
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One approach to maintaining soil he
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Author Database Used Extent Estimat
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salinization. Safe design and opera
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The second limitation to prediction
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Figure 7.6 Some soil-related feedba
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soils occurs on largely unmanaged a
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extremes several weeks in advance (
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The direct effect of aerosols on th
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capacity declines as N loads increa
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The concept of the critical load of
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as it indicates that management and
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10-year frequency Ten-year frequenc
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phenomena such as the onset of mass
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Although poorly explored, diversity
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affect the health of humans and ani
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Bever, J.D., Westover, K.M. & Anton
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Damoah, R., Spichtinger, N., Servra
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Fenn, M.E., Poth, M.A., Aber, J.D.,
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Heimann, M. & Reichstein, M. 2008.
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Koster, R.D., Dirmeyer, P.A., Guo,
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Naeem, S., Bunker, D.E., Hector, A.
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Raufman, Y.J. & Fraser, R.S. 1997.
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Sheffield, J. & Wood, E.F. 2007. Pr
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UNEP. 2012. Policy Implications of
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8 | Governance and policy responses
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contemporary challenge for policy m
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Year 1982 FAO World Soil Charter 19
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Ensure integrated management of pes
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8.4 | Regional soil policies 8.4.1
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while in areas with fertile soils t
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In New Zealand, there are few regul
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The SEEA Central Framework identifi
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EC. 2013. Decision No 1386/2013/EU
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World Bank. 2011. Rising Global Int
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9.1 | Introduction Land degradation
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Figure 9.1 Agro-ecological zones in
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The soils are strongly weathered an
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It exposes the soil to the erosive
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In many African cultures, harvestin
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Maputo accounts for 83 percent of t
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Poverty: General poverty of the far
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Considering that over 80 percent of
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Extent of SOM decline in the region
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Many farmers do not follow recommen
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9.5 | Case studies 9.5.1 | Senegal
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Figure 9.7 Extent of dominant degra
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management, it is important to note
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From 2006, several further national
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Figure 9.12 Actual water erosion pr
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Figure 9.13 Topsoil pH derived from
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Figure 9.14 Change in land-cover be
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Waterlogging Compaction Soil sealin
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Birru, T.C. 2002. Organic matter re
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Hein, L. & De Ridder, N. 2006. Dese
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Meyer, J.H., Harding, R., Rampersad
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Smith P. 2008. Soil organic carbon
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10 | Regional Assessment of Soil Ch
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Figure 10.1 Length of the available
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Figure 10.2 Threats to soils in the
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10.3.4 | Soil acidification There i
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In paddy rice cultivation and uplan
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10.3.10 | Sealing and capping Seali
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practices. On low slopes, agronomic
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(Valentin et al., 2008). For peatla
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in Laos (59 kg N ha -1 ). On the ot
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Sub-Regions. Inceptisols are the do
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10.5.2 | Case study for Indonesia T
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Peat fire is another important proc
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An agricultural soil monitoring pro
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The Basic Soil-Environmental Monito
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Figure 10.8 Estimate CH 4 emission
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Threat to soil function Soil erosio
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References Aggarwal, G.C., Sidhu, A
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FAO. 2012. FAOSTAT. Rome, FAO. (Als
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Kukal, S.S. & Aggarwal, G.C. 2003.
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Piao, S., Fang, J., Ciais, P., Peyl
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Taniyama, I. 2003. Study of soil fa
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Zhao, Y., Duan, L., Xing, J., Larss
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11.1 | Introduction The majority of
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The internal stratification within
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Mediterranean zone This zone by def
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(5) Salinization and sodification I
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The real extent of diffuse soil con
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While there is no harmonised exhaus
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Prepared by I. Alyabina Figure 11.2
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This is due to the country’s geo-
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Future changes in climate and land
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Considering an increase of industri
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Comparison of cultivated soils with
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Figure 11.3 Some types and extent o
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The plains in the basins of Amu Dar
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Threat to soil function Soil sealin
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References Acosta, J.A., Faz, A., J
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Inisheva, L.I. (ed.). 2005. Concept
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van Lynden, G.W.J. 1997. Guidelines
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12.1 | Introduction This chapter di
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Figure 12.1 Biomes in Latin America
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Temperate Grasslands, Savannahs and
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humid. The most common soil groups
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12.3.6 | Compaction In LAC there ar
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New regional information has been g
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Primary forests have higher carbon
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Prepared by C. Cruz-Gaistardo Figur
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The salinity of soils on the cultiv
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Figure 12.6 Expansion of the agricu
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Figure 12.7 Percentage of areas aff
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Figure 12.8 Predominant types of la
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Boddey, R.M., Alves, B.J.R, Jantali
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Gardi, C., Angelini, M., Barceló,
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Nogueira, M.A., Albino, U.B., Brand
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Spavorek, G., Bemdes, G., Barreto,
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13 | Regional Assessment of Soil Ch
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The Arab Centre for the Study of Ar
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Poverty within this system is exten
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Wind erosion A review conducted by
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13.3.5 | Soil salinization/sodifica
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13.3.9 | Compaction Soil compaction
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13.4 | Major soil threats in the re
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In Sudan, studies showed that in ar
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2002). There are few studies on the
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Consequences of salinization Salini
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Rates of C change are influenced no
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Figure 13.3 Layout of the project s
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13.5 | Case studies 13.5.1 | Case s
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Studies show that both climatic and
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2 - Land degradation assessment map
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Figure 13.9 Type of ecosystem servi
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References Abahussain, A.A., Abdu,
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Badraoui, M. 1998. Effects of inten
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FAO. 2004. Regional Workshop on Pro
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Mamdouh Nasr. 1999. Assessing Deser
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Yaghi, B. & Abdul-Wahab, S.A. 2004.
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14.1 | Introduction Although Canada
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The area of forested land in Canada
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14.3 | Soil threats This section fo
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Figure 14.2 Map of Superfund sites
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Figure 14.3 Areas in United States
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The drivers for soil sealing in Can
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14.4.1 | Soil erosion Soil erosion
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The relationship between soil prope
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14.4.4 | Soil biodiversity Soil bio
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Figure 14.5 Risk of water erosion i
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Figure 14.7 Soil organic carbon cha
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Figure 14.8 Residual soil N in Cana
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14.6 | Conclusions and recommendati
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Compaction Sealing and land take Sa
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Clearwater, R.L., Martin, T., Hoppe
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Kurz, W.A., Dymond, C.C., White, T.
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USDA. 2011. Resource Conservation A
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15.1 | Introduction The Southwest P
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of the country. The undulating and
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The broad area of Near Oceania (inc
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Country and land-use driver Implica
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15.5 | Threats to soils in the regi
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egenerating soils. The South Island
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New Zealand The importance of soil
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Fertilizers Impurities in fertilize
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The main onsite effects of acidific
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Saltwater intrusion Saltwater intru
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Phosphorus is naturally deficient a
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Canterbury region. There has been a
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Figure 15.3 (a) Trends in winter ra
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Figure 15.5 Agricultural lime sales
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The management of water is also fun
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The DustWatch network Australia has
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Soil sealing and capping Contaminat
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Bui, E.N., Hancock, G.J. & Wilkinso
Page 555 and 556: Hartemink, A.E. 1998b. Acidificatio
Page 557 and 558: Moorehead, A. (ed.). 2011. Forests
Page 559 and 560: Robertson, M.J., George, R.J., O’
Page 561 and 562: Wilson, B.R. & Lonergan, V.E. 2013.
Page 563 and 564: 16.1 | Antarctic soils and environm
Page 565 and 566: 16.3 | Response All activities in A
Page 567 and 568: IAATO. 2014. Tourism statistics. In
Page 569 and 570: Annex | Soil groups, characteristic
Page 571 and 572: a Photo by C. Tarnocai b Photo by S
Page 573 and 574: Figure A 2 (a) An Anthrosol (Plagge
Page 575 and 576: a Photo by P. Charzyński Figure A
Page 577 and 578: a Photo by A. Filaretova b Photo by
Page 579 and 580: Figure A 5 (a) A Leptosol profile i
Page 581 and 582: a Photo by L. Wilding b Photo by L.
Page 583 and 584: Figure A 7 (a) A Solonetz profile a
Page 585 and 586: a Photo by T. Toth b Photo by S. Kh
Page 587 and 588: Figure A 9 (a) A Podzol profile and
Page 589 and 590: FERRALSOLS (OXISOLS) Ferralsols (Fi
Page 591 and 592: NITISOLS (Alfisols, Ultisols, Incep
Page 593 and 594: PLINTHOSOLS (Plinthic sub-groups) P
Page 595 and 596: PLANOSOLS (Albaqualfs, Albaquults a
Page 597 and 598: GLEYSOLS (Aquic suborder and Endoaq
Page 599 and 600: STAGNOSOLS (Aquic Suborders and Epi
Page 601 and 602: ANDOSOLS (ANDISOLS) Andosols (Figur
Page 603 and 604: 5 | Soils with accumulation of orga
Page 605: KASTANOZEMS (Ustolls and Xerolls) K
Page 609 and 610: UMBRISOLS (Umbric Great Group in Aq
Page 611 and 612: 6 | Soils with accumulation of mode
Page 613 and 614: CALCISOLS (Calcids, Argids, Cambids
Page 615 and 616: GYPSISOLS (Gypsids) Gypsisols are c
Page 617 and 618: 7 | Soils with a clay-enriched subs
Page 619 and 620: ACRISOLS (Kan- great groups of Ulti
Page 621 and 622: LIXISOLS (Kan - great groups of Alf
Page 623 and 624: ALISOLS (Ultisols with an argillic
Page 625 and 626: LUVISOLS (Alfisols with an argillic
Page 627 and 628: 8 | Soils with little or no profile
Page 629 and 630: REGOSOLS (Orthents) Regisols are th
Page 631 and 632: ARENOSOLS (Psamments) Arenosols are
Page 633 and 634: FLUVISOLS (Fluvents, Fluv-Subroups)
Page 635 and 636: 9 | Permanently flooded soils WASSE
Page 637 and 638: Kastanozems Histosols Gypsisols Gre
Page 639 and 640: Jones, A., Breuning-Madsen, H., Bro
Page 641 and 642: Glossary of technical terms Aerobic
Page 643 and 644: Topsoil: the upper part of a natura
Page 645 and 646: Broll, Gabrielle Bruulsma, Tom Bunn
Page 647 and 648: Leys, John Lobb, David Ma, Lin Maci
Page 649: Urquiaga Caballero, Segundo Urquiza
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World’s Soil Resources

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