World’s Soil Resources

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Research needs It will be evident from the discussion in this section that much remains to be learned. Amongst the priority research questions are the following: 1. Sustainable intensification – How can we get the benefits from intensification while minimizing the associated environmental and social costs? 2. Trade-offs between soils and efficiency – How can we manage for resilient soil and related ecosystem services while continuing to maximize efficiency? To what extent can we have both? 3. Soil degradation and intensification – What is the extent of degraded soils? There are currently no sound estimates. What portion of degraded soils can be attributed to un-sustainable intensification? 4. Options and trade-offs for improved soil management – What can we learn from management practices used in intensification areas to help restore degraded soils? Are there any options that can integrate best management practice for sustainable intensification? What are the short – and long-term tradeoffs of resource use and sustainability? What are the environmental and social costs and economic benefits of land use intensification? 5. Farming practices and soil health – How do changes in harvest frequency and crop rotation affect soil resilience? How much change is needed to restore degraded soils? Land intensification Sector Distribution Major environmental consequence Knowledge gap Cropping intensification Harvest frequency Globally Soil quality and resilience Ecosystem service Continuing monoculture Developing and transition countries Soil health, pesticide residue Biological resilience Nutrient intensification Over fertilization Developing countries Soil acidification, water pollution, N 2 O emission and nitrate accumulation Rate reducing versus balancing? Irrigation Submerged Rice Developing countries, Asia Water scarcity, methane emission Trade-offs C and water, Dry crops Arid/semi-arid regions Secondary salinization, water scarcity Competition for water Livestock intensification Over grazing Developing countries Soil degradation, water storage, C loss Forage versus feed crops? Industrial breeding Industrialized countries Waste, water pollution, residue of veterinary medicine and antibiotics Safe waste treatment and recycling Forest clearance, wetlands drainage Deforestation. wetland shrink Developing and transition countries Biodiversity, natural wealth, C loss Agro-benefit versus natural value Table 4.2 Threats to soil resource quality and functioning under agricultural intensification Status of the World’s Soil Resources | Main Report Soils and Humans 64
4.3.3 | Land use change resulting in irreversible soil change In this section we deal with soil sealing and mining, which have been identified as two important soil degradation processes occurring around the world. The current extent and rate of growth of soil sealing and mining are significant, and create considerable risks to essential ecosystem services. These changes in land use nearly always require a trade-off between various social, economic and environmental needs. Sealing and land take The ongoing urbanization and conversion of the landscape with settlements, infrastructure and services is occurring in many regions. Europe and Asia, in particular, are experiencing high rates of urban expansion and urban sprawl, and there are often insufficient incentives to re-use brownfield sites. These factors are causing an increase in land take and soil sealing. The drivers are essentially economic and demographic growth. In Europe, America and Oceania, at least 70 to 80 percent of the population currently lives in urban areas. The rate of urbanization is expected to continue to increase, particularly in Asia and Africa. The concept of land take covers all forms of conversion for the purpose of settlement, including: the development of scattered settlements in rural areas; the expansion of urban areas around an urban nucleus; the conversion of land within an urban area (densification); and the expansion of transport infrastructure such as roads, highways and railways. Broadly, this discussion considers as land take any conversion of agricultural, natural or semi-natural land cover to an ‘artificial’ (e.g. human-made) area. Artificial land cover classes are categorized in the Corine Land Cover system – see Table 4.3. A greater or smaller part of land take will result in soil sealing. Soil sealing means the permanent covering of an area of land and its soil by impermeable artificial material such as asphalt or concrete, for example through buildings and roads. As shown in Figure 4.6, the sealed area is only part of a settlement area. Gardens, urban parks, leisure areas and other green spaces within the boundaries of settlements are not covered by an impervious surface or are only partially covered. They thus form part of a land take but do not contribute to soil sealing (Prokop, Jobstmann and Schöbauer, 2011.) The ratio between sealed area and total area for a given land use class is measured by the soil sealing index. An example of this index, calculated for the Italian region of Emilia-Romagna, is shown in Table 4.4. Table 4.3 Artificial areas in Corine Land Cover Legend Status of the World’s Soil Resources | Main Report Soils and Humans 65
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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
Page 55 and 56: 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: Livestock density Livestock product
Page 109 and 110: Impact of land take Land take, by 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
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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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Page 475 and 476:
References Abahussain, A.A., Abdu,
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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
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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
Page 515 and 516:
Kurz, W.A., Dymond, C.C., White, T.
Page 517 and 518:
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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