World’s Soil Resources

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At present, no national or regional assessment on loss of biodiversity can be made for North America, but there are signs that such an assessment may be possible in the future. The Global Soil Biodiversity Initiative (GSBI) was launched in 2011 and provides a welcome platform for the coordination of research in this area (GSBI, 2014). 14.5 | Case study: Canada As discussed in the Introduction (14.1), there are no existing regional maps for threats to soil functions for North America. In this section the maps produced under the Canadian Agri-Environmental Indicators programme (Clearwater et al., 2015) for wind and water erosion, SOC change and nutrient imbalance (residual soil N and P-source risk classes) are presented so that the linkage between drivers and threats to soil functions can be illustrated. The maps focus on agricultural impacts on soil functions. No comparable products exist for other soil threats. The major changes to drivers in Canada have been discussed in detail in Section 14.3 above. There are distinct differences across the main ecoregions of Canada that experience concentrated human impact. The main drivers can be summarized as: • Intensification of agriculture e.g. reduced pasture area, increased area of maize and soybean production, higher fertilizer inputs in the Mixed Wood Plains ecoregion in southern Ontario and Quebec and in the agricultural areas of eastern Canada e.g. in New Brunswick, Nova Scotia, and Prince Edward Island. • Significant reductions in the area of tillage summerfallow in the Temperate Plains and West-Central Semi-Arid ecoregions. • Widespread adoption of conservation tillage practices in most cropping systems in Canada. 14.5.1 | Water and wind erosion In Canada, the Soil Erosion Risk Indicator was used as part of the Agri-Environmental Indicators programme to assess the risk of soil erosion from the combined effects of wind, water and tillage on cultivated agricultural lands (Figure 14.5). This indicator and its component indicators for wind, water and tillage erosion reflect the characteristics of the climate, soil and topography and correspond to changes in farming practices over the 30-year period from 1981 to 2011. Wind and water erosion are the primary focus of this summary. For details on calculation of the indicators, see Li et al. (2008), McConkey, Li and Black, (2008), and Huang and Lobb (2013). The erosion indicator calculation estimates the rate of soil loss. These values are reported in five classes. Areas in the very low risk class are considered capable of sustaining long-term crop production and maintaining agri-environmental health under current conditions. The other four classes represent the degrees of risk of unsustainable conditions that call for soil conservation practices to support crop production over the long term and to reduce risk to soil quality. The risk of soil erosion on Canadian cropland has steadily declined between 1981 and 2011. The majority of this change occurred between 1991 and 2006. In 2011, 61 percent of cropland area was in the very low risk class overall, a considerable improvement over 1981 when only 29 percent was in this risk class. This decrease in water and wind erosion risk was most pronounced in the Temperate Prairie and West-Central Semi-Arid ecoregions in Alberta and Saskatchewan (Figure 14.5 and 14.6). Much of the improvement in erosion risk is from reductions due to the reduction in tillage summer fallow. A second driver is the increased adoption of direct seeding and conservation tillage, which is largely responsible for the decrease in tillage intensity and soil erosion. Status of the World’s Soil Resources | Main Report Regional Assessment of Soil Changes 460 in North America
Figure 14.5 Risk of water erosion in Canada 2011. Source: Clearwater et al., 2015. Status of the World’s Soil Resources | Main Report Regional Assessment of Soil Changes 461 in North America
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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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Threat to soil function Soil erosio
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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
Page 451 and 452: 13.3.9 | Compaction Soil compaction
Page 453 and 454: 13.4 | Major soil threats in the re
Page 455 and 456: In Sudan, studies showed that in ar
Page 457 and 458: 2002). There are few studies on the
Page 459 and 460: Consequences of salinization Salini
Page 461 and 462: Rates of C change are influenced no
Page 463 and 464: Figure 13.3 Layout of the project s
Page 465 and 466: 13.5 | Case studies 13.5.1 | Case s
Page 467 and 468: Studies show that both climatic and
Page 469 and 470: 2 - Land degradation assessment map
Page 471 and 472: Figure 13.9 Type of ecosystem servi
Page 473 and 474: Threat to soil function Soil erosio
Page 475 and 476: References Abahussain, A.A., Abdu,
Page 477 and 478: Badraoui, M. 1998. Effects of inten
Page 479 and 480: FAO. 2004. Regional Workshop on Pro
Page 481 and 482: Mamdouh Nasr. 1999. Assessing Deser
Page 483 and 484: Yaghi, B. & Abdul-Wahab, S.A. 2004.
Page 485 and 486: 14.1 | Introduction Although Canada
Page 487 and 488: The area of forested land in Canada
Page 489 and 490: 14.3 | Soil threats This section fo
Page 491 and 492: Figure 14.2 Map of Superfund sites
Page 493 and 494: Figure 14.3 Areas in United States
Page 495 and 496: The drivers for soil sealing in Can
Page 497 and 498: 14.4.1 | Soil erosion Soil erosion
Page 499 and 500: The relationship between soil prope
Page 501: 14.4.4 | Soil biodiversity Soil bio
Page 505 and 506: Figure 14.7 Soil organic carbon cha
Page 507 and 508: Figure 14.8 Residual soil N in Cana
Page 509 and 510: 14.6 | Conclusions and recommendati
Page 511 and 512: Compaction Sealing and land take Sa
Page 513 and 514: Clearwater, R.L., Martin, T., Hoppe
Page 515 and 516: Kurz, W.A., Dymond, C.C., White, T.
Page 517 and 518: USDA. 2011. Resource Conservation A
Page 519 and 520: 15.1 | Introduction The Southwest P
Page 521 and 522: of the country. The undulating and
Page 523 and 524: The broad area of Near Oceania (inc
Page 525 and 526: Country and land-use driver Implica
Page 527 and 528: 15.5 | Threats to soils in the regi
Page 529 and 530: egenerating soils. The South Island
Page 531 and 532: New Zealand The importance of soil
Page 533 and 534: Fertilizers Impurities in fertilize
Page 535 and 536: The main onsite effects of acidific
Page 537 and 538: Saltwater intrusion Saltwater intru
Page 539 and 540: Phosphorus is naturally deficient a
Page 541 and 542: Canterbury region. There has been a
Page 543 and 544: Figure 15.3 (a) Trends in winter ra
Page 545 and 546: Figure 15.5 Agricultural lime sales
Page 547 and 548: The management of water is also fun
Page 549 and 550: The DustWatch network Australia has
Page 551 and 552: Soil sealing and capping Contaminat
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Bui, E.N., Hancock, G.J. & Wilkinso
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Hartemink, A.E. 1998b. Acidificatio
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Moorehead, A. (ed.). 2011. Forests
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Robertson, M.J., George, R.J., O’
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Wilson, B.R. & Lonergan, V.E. 2013.
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16.1 | Antarctic soils and environm
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16.3 | Response All activities in A
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IAATO. 2014. Tourism statistics. In
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Annex | Soil groups, characteristic
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a Photo by C. Tarnocai b Photo by S
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Figure A 2 (a) An Anthrosol (Plagge
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a Photo by P. Charzyński Figure A
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a Photo by A. Filaretova b Photo by
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Figure A 5 (a) A Leptosol profile i
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a Photo by L. Wilding b Photo by L.
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Figure A 7 (a) A Solonetz profile a
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a Photo by T. Toth b Photo by S. Kh
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Figure A 9 (a) A Podzol profile and
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FERRALSOLS (OXISOLS) Ferralsols (Fi
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NITISOLS (Alfisols, Ultisols, Incep
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PLINTHOSOLS (Plinthic sub-groups) P
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PLANOSOLS (Albaqualfs, Albaquults a
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GLEYSOLS (Aquic suborder and Endoaq
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STAGNOSOLS (Aquic Suborders and Epi
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ANDOSOLS (ANDISOLS) Andosols (Figur
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5 | Soils with accumulation of orga
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KASTANOZEMS (Ustolls and Xerolls) K
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PHAEOZEMS (Udolls and Albolls) Phae
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UMBRISOLS (Umbric Great Group in Aq
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6 | Soils with accumulation of mode
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CALCISOLS (Calcids, Argids, Cambids
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GYPSISOLS (Gypsids) Gypsisols are c
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7 | Soils with a clay-enriched subs
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ACRISOLS (Kan- great groups of Ulti
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LIXISOLS (Kan - great groups of Alf
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ALISOLS (Ultisols with an argillic
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LUVISOLS (Alfisols with an argillic
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8 | Soils with little or no profile
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REGOSOLS (Orthents) Regisols are th
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ARENOSOLS (Psamments) Arenosols are
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FLUVISOLS (Fluvents, Fluv-Subroups)
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9 | Permanently flooded soils WASSE
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Kastanozems Histosols Gypsisols Gre
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Jones, A., Breuning-Madsen, H., Bro
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Glossary of technical terms Aerobic
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Topsoil: the upper part of a natura
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Broll, Gabrielle Bruulsma, Tom Bunn
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Leys, John Lobb, David Ma, Lin Maci
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Urquiaga Caballero, Segundo Urquiza
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