World’s Soil Resources

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A) Typical structure of settlement B) Sealed areas about 70 percent (black color) Figure 4.6 Schematic diagram showing areas sealed (B) as a result of infrastructure development for a settlement (A). Source: European Union, 2012. Table 4.4 Artificial areas in Emilia Romagna according to the Corine Land Cover Legend and sealing index. Status of the World’s Soil Resources | Main Report Soils and Humans 66
Impact of land take Land take, by its definition, is the subtraction of an area from a previous agricultural, natural or semi-natural land use. According to this definition, the most obvious impact on the ecosystem services that can be provided by soil is on the production of biomass, and in particular of food. To clarify the concept, we may imagine that a city expands its urbanized area by a new allotment of 100 ha created at the expense of agricultural land. This area will be covered by buildings, private and public gardens, commercial centres, roads, etc. The entire area will clearly lose most of its capacity to produce food, with the possible minor exception of family horticulture in unsealed areas such as gardens or allotments. Had the entire area been previously cultivated with, say, winter wheat with an average yield of 5 tonnes ha -1 , the total loss in terms of food production potential will be equal to 500 tonnes of winter wheat per year. Other ecosystem services are at risk also. Water infiltration and purification and carbon storage are mainly reduced by the effective sealed area, and not by the entire land taken. Support to biodiversity is clearly affected, although the degree depends on the different groups of organisms and also on the design of the urbanized area. In this context, a positive mitigation role can be played by ‘Urban Green Infrastructure’ – the incorporation of a network of high-quality green spaces and other environmental features. Green Infrastructure can include natural areas as well as human-made rural and urban elements such as urban green spaces, reforestation zones, green bridges, green roofs, eco-ducts to allow crossing of linear barriers, corridors, parks, restored floodplains, biodiverse farmland. Regulation of land take and mitigation of its impacts Where policy aims to minimize land take, measures can be implemented to encourage re-use of existing urban areas such as derelict areas, brownfields and upgrading of degraded neighborhoods. Measures promoting densification of existing urban areas can also contribute to the reduction of land take. Fiscal measures can prevent speculative urban sprawl. A number of municipalities, and regional governments, especially in Europe, have already adopted policies designed to achieve zero net urban expansion. However, zero expansion becomes more problematic when there is significant demographic pressure and a high rate of rural to urban migration. Rational and efficient urban planning and intelligent building and infrastructure design can also help reduce land take. In the past, urban planners, architects and civil engineers too often considered soil as a raw material, abundantly available and of limited value. Examples of efficient consideration of the value of soil in urban development include: the construction of parking lots in the basement of buildings; and ‘green’ covering of areas that are only occasionally used, such as parking lots for exhibitions and fairs etc. Where expansion of urban and built-up areas is a policy and planning imperative, intelligent urban planning needs to take account of the soil dimension to mitigate the impact of land take. An education process is needed to make urban planners aware of the value of soil quality and land capability and of the options for mitigating negative impacts of land take. Impacts of soil sealing Sealing by its nature has a major effect on soil, diminishing many of its benefits. Normal construction practice is to remove the upper layer of topsoil, which delivers most of the soil-related ecosystem services, in order to be able to develop strong foundations in the subsoil or underlying rock to support the building or infrastructure. Where strong foundations are not required, only a thin layer of topsoil is generally excavated and the surfaces are simply covered by a layer of impervious material, such as asphalt or concrete. Both techniques impair or eliminate the soil’s capacity to deliver ecosystem services. Status of the World’s Soil Resources | Main Report Soils and Humans 67
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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
Page 57 and 58: 2.1.2 | Nature and formation of soi
Page 59 and 60: 2.1.4 | Factors influencing soil C
Page 61 and 62: In coming years, human population a
Page 63 and 64: Management practices need to be imp
Page 65 and 66: Another important role of soil wate
Page 67 and 68: The development of molecular techno
Page 69 and 70: Fierer, N., Ladau, J., Clemente, J.
Page 71 and 72: Sato, T., Qadir, M., Yamamoto, S.,
Page 73 and 74: 3 | Global Soil Resources 3.1 | The
Page 75 and 76: Fridland’s was the first attempt
Page 77 and 78: Soil management has a considerable
Page 79 and 80: Accumulation of water soluble salts
Page 81 and 82: and increases infiltration, which r
Page 83 and 84: Figure 3.7 Soil suitability for cro
Page 85 and 86: 3.7 | Global assessments of soil ch
Page 87 and 88: 3.7.2 | LADA-GLADIS: the ecosystem
Page 89 and 90: References AFES. 2008. Réferentiel
Page 91 and 92: Neustuev, S.S. 1931. Elements of So
Page 93 and 94: 75% crops Mixed >50% artificial 50-
Page 95 and 96: or increasing forest areas. Between
Page 97 and 98: Degrading land covers approximately
Page 99 and 100: 70 60 (A) soil carbon 50 Soil
Page 101 and 102: A meta-analysis of 57 publications
Page 103 and 104: the nutrient inputs remain in the c
Page 105 and 106: Livestock density Livestock product
Page 107: 4.3.3 | Land use change resulting i
Page 111 and 112: Photo by F. Macias Photo by J.C. Fe
Page 113 and 114: The formation of sulfidic material
Page 115 and 116: are however strongly dependent on t
Page 117 and 118: Figure 4.10 Global distribution of
Page 119 and 120: Bardgett, R.D. & van der Putten, W.
Page 121 and 122: Dentener, F., Drevet, J., Lamarque,
Page 123 and 124: Hettelingh, J.P., Sliggers, J., van
Page 125 and 126: Magnani, F., Mencuccini, M., Borghe
Page 127 and 128: Pugh, T.A.M., Arneth, A., Olin, S.,
Page 129 and 130: Van Aardenne, J.A., Dentener, F.J.,
Page 131 and 132: 5 | Drivers of global soil change D
Page 133 and 134: 5.1.2 | Urbanization In tandem with
Page 135 and 136: Large areas of arable land have bee
Page 137 and 138: most affected zone with 15 million
Page 139 and 140: (Brito et al., 2005). This has impl
Page 141 and 142: MA. 2005. Ecosystems and Human Well
Page 143 and 144: 6.1.2 | Status of Soil Erosion Over
Page 145 and 146: Figure 6.2 Location of active and f
Page 147 and 148: High soil erosion rates will also h
Page 149 and 150: Near-surface soil water content has
Page 151 and 152: 6.2 | Global soil organic carbon st
Page 153 and 154: where the drainage in the 1960’s
Page 155 and 156: 6.2.4 | Spatial distribution of car
Page 157 and 158: 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
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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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