World’s Soil Resources

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Figure 15.2 Change in the percentage area of all land prepared for crops and pastures under different tillage practices in Australia, 1996-2010 Source: SOE, 2011. Land management practices have improved significantly during the past few decades, due to better grazing practices, adoption of conservation tillage, enforcement of forestry codes and soil conservation measures in engineering (e.g. relating to road construction and urban development). Ground-based monitoring of management practices and land cover along with data on land-management practices (SOE, 2011) reveal a pattern of: • more careful grazing and maintenance of effective land cover at critical times of the year • improved adoption of conservation practices, especially across the cropping lands of southern Australia • an associated large decline in the amount of tillage in farming systems (Figure 15.2) New Zealand Soil loss by erosion is a major problem in many areas of New Zealand due to a combination of factors including soil type, topography and climate, as well as the type and associated intensity of land use (especially pastoral agriculture). Eyles (1983) provided the first systematic inventory of soil erosion in New Zealand and made the following observations and estimates. Surface erosion occurs mainly on the South Island. In 1983 sheet erosion affected 10 million ha of the country, while wind erosion affected 3 million ha (the total area of New Zealand is approximately 27 million ha). Mass movement occurred mainly on the North Island and slip erosion was estimated to affect 7 million ha. Fluvial erosion also occurred mainly in the North Island with rill and gully erosion estimated to affect 2 million ha. The study concluded that a total of 9 million ha of farmed land in New Zealand was at risk of significant erosion, although the level of risk was variable. The large scale afforestation of hill country and steep-land pasture since 1983 (see case study below) will have substantially reduced rates of soil erosion (especially sheet and slip erosion). However, forest harvesting results in significant soil disturbance and this will increase the risk of erosion when the first rotation forest is harvested and the second rotation established. Dymond (2010) analysed erosion rates in order to refine the national carbon budget because soil erosion in New Zealand results in the large export of sediment and particulate organic carbon (POC) directly to the sea. The North Island of New Zealand was estimated to export 1.9 (−0.5/+1.0) million tonnes of POC per year to the sea, and to sequester 1.25 (−0.3 /+0.6) million tonnes of carbon per year from the atmosphere through Status of the World’s Soil Resources | Main Report Regional Assessment of Soil Changes 486 in the Southwest Pacific
egenerating soils. The South Island was estimated to export 2.9 (−0.7/+1.5) million tonnes of POC per year, and to sequester approximately the same amount. Dymond (2010) assumed that exported carbon is buried at sea with an efficiency of 80 percent. This gives New Zealand a net carbon sink of 3.1 (−2.0/+2.5) million tonnes per year (equivalent to about 45 percent of New Zealand’s fossil fuel carbon emissions in 1990). There is essentially a ’conveyor-belt’ transfer of carbon from the atmosphere to soils regenerating from erosion and to the sea floor where carbon is permanently buried. The large magnitude of the net sink is primarily due to tectonically driven uplift and erosion combined with high biological productivity. The degree to which other elevated and humid islands in the Pacific can operate as a net sink has not been determined. Pacific Islands The high rainfall and steep lands in many of the larger Pacific Island countries make them vulnerable to soil erosion. Understanding the significance of this erosion requires information on both rates of soil formation and the baseline rates of sediment movement in different landscapes. The latter can be much larger than in temperate regions and relatively fast rates of erosion around 50 tonnes ha -1 yr -1 have been recorded in heavily forested landscapes in Fiji (Glatthaar, 1988; Liedtke, 1989) and Samoa (Terry, Garimella and Kostaschuk, 2002; Terry, Kostaschuk and Garimella, 2006). Tropical cyclones, intense rainstorms, steep slopes and landslides are key factors. The desire for economic development has led to increasing areas of good quality soil being used for cash crops such as coffee and cocoa and for cattle production. These factors in conjunction with population pressures are forcing small-scale agriculture onto steeper less suitable lands. Logging, whether managed or illegal, increases the pressure even further. Condron and Di (2002) indicate that rates of soil loss by erosion in these areas are typically between 10 to 90 tonnes ha -1 yr -1 (see also Asquith, Kooge and Morrison, 1994; Liedtke, 1989). Accelerated soil erosion has also been associated with plantations, particularly on marginal sloping land. Although most atolls are away from the cyclone belt in the Southwest Pacific, a few have been severely eroded by large storms. The impacts are devastating as much of the limited soil resource is washed away, and also what is left becomes highly salinized and of limited productive capacity. This was particularly noted on Funafuti, Tuvalu following cyclone Bebe in 1972 (Maragos, Baines and Beveridge, 1973). Sub-Antarctic Islands Several sub-Antarctic islands in the Southwest Pacific region continue to have high rates of soil erosion. Macquarie Island, for example, is an isolated island in the Southern Ocean that provides a critical habitat for migratory species. Macquarie Island has been severely eroded and approximately AUD $25 million has been spent in recent years on habitat restoration programmes, mainly for the eradication of rabbits. 15.5.2 | Soil organic carbon change Most of the region experienced large losses of soil carbon when land was first cleared for agriculture. The major phases of clearing in each country were noted above. In some countries clearing associated with uncontrolled logging continues today, for example in Papua New Guinea and the Solomon Islands (Moorehead, 2011). The initial disruption to soil caused by clearing usually results in a significant loss of nutrients. Organic matter is oxidised and the removal of surface cover (litter and protective vegetation) makes the soil more prone to erosion. Stores and cycles of nutrients adjust under the new land use, but in most cases the net loss of nutrients and leakage are greater than under natural conditions. Most studies indicate that across the region soil carbon typically reduces to 20–70 percent of the pre-clearing amount (e.g. Sanderman and Baldock, 2010). Opportunities for restoring some of this very large stock of carbon have been a focus of soil research in Australia and New Zealand during the last decade. Status of the World’s Soil Resources | Main Report Regional Assessment of Soil Changes 487 in the Southwest Pacific
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Status of the World’s Main Report
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Dick, Warren Dos Santos Baptista, I
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Table of contents Disclaimer and co
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4.1 | Current land cover and land u
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6.5.5 | Responses | 126 6.6 | Soil
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7.7.3 | Soil and drought hazard | 1
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9.5.2 | South Africa | 266 9.6 | Su
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12.3.8 | Soil acidification | 373 1
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14.5.4 | Nutrient imbalance | 464 1
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Foreword This document presents the
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Preface | Scope of The State of the
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Acknowledgments The Status of the W
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CACILM CAMRE CAZRI CBD CBM-CFS CCAF
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FDNPS FFS FIA FSI FSR GAP GDP GEF G
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LU MA MADRPM MAF MAFF MDBA MDGS MEN
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SKM SLAM SLC SLM SMAP SMOS SOC SOE
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List of tables Table 1.1 | Chronolo
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List of figures Figure 2.1 | Overvi
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Figure 6.15 | Factors controlling s
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Figure 11.4 | Soil map and soil deg
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colored diaper associated with micr
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Preface The main objectives of The
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Global soil resources Coordinating
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The balance between the supporting
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1.2 | Basic concepts Prior to the 2
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Soil functions and ecosystem servic
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Climate regulation ∑ Regulation o
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2 | The role of soils in ecosystem
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2.1.2 | Nature and formation of soi
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2.1.4 | Factors influencing soil C
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In coming years, human population a
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Management practices need to be imp
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Another important role of soil wate
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The development of molecular techno
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Fierer, N., Ladau, J., Clemente, J.
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Sato, T., Qadir, M., Yamamoto, S.,
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3 | Global Soil Resources 3.1 | The
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Fridland’s was the first attempt
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Soil management has a considerable
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Accumulation of water soluble salts
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and increases infiltration, which r
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Figure 3.7 Soil suitability for cro
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3.7 | Global assessments of soil ch
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3.7.2 | LADA-GLADIS: the ecosystem
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References AFES. 2008. Réferentiel
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Neustuev, S.S. 1931. Elements of So
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75% crops Mixed >50% artificial 50-
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or increasing forest areas. Between
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Degrading land covers approximately
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70 60 (A) soil carbon 50 Soil
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A meta-analysis of 57 publications
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the nutrient inputs remain in the c
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Livestock density Livestock product
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4.3.3 | Land use change resulting i
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Impact of land take Land take, by i
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Photo by F. Macias Photo by J.C. Fe
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The formation of sulfidic material
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are however strongly dependent on t
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Figure 4.10 Global distribution of
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Bardgett, R.D. & van der Putten, W.
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Dentener, F., Drevet, J., Lamarque,
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Hettelingh, J.P., Sliggers, J., van
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Magnani, F., Mencuccini, M., Borghe
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Pugh, T.A.M., Arneth, A., Olin, S.,
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Van Aardenne, J.A., Dentener, F.J.,
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5 | Drivers of global soil change D
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5.1.2 | Urbanization In tandem with
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Large areas of arable land have bee
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most affected zone with 15 million
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(Brito et al., 2005). This has impl
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MA. 2005. Ecosystems and Human Well
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6.1.2 | Status of Soil Erosion Over
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Figure 6.2 Location of active and f
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High soil erosion rates will also h
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Near-surface soil water content has
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6.2 | Global soil organic carbon st
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where the drainage in the 1960’s
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6.2.4 | Spatial distribution of car
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Vegetation Classes Topsoil Subsoil
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Soil Order Historic Area 10 6 ha Pr
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6.3 | Soil contamination status and
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and Uruguay. The number of exposed
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products increase soil acidity (Bar
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availability and inhibit plant grow
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In several Asian countries, a blend
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underlines the need for global-scal
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Figure 6.10 Urbanisation of the bes
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Figure 6.11 Major components of the
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Within the same continent, large va
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Box 6.2 | Nutrient balances in urba
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is among the top options in the por
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The quality of the soil’s water i
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At continental scales, the only pra
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Figure 6.16 (a) Global distribution
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Engineering in Japan, 5: 157-174. A
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Chadwick, D., Sommer, S., Thorman,
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Drechsel, Pay, Giordano, Mark, Gyie
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Gardner, T., Acosta-Martinez, V., C
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Hue, N.V. & Licudine, D.L. 1999. Am
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Liski, J., Ilvesniemi, H., Mäkelä
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Ng, H. 2010. Regional Assessment: S
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Reheis, M. 1997. Dust deposition do
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Smith, K.A., McTaggart, I.P. & Tsur
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United Nations. 2008. World Urbaniz
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Wood, M.K. & Blackburn, W.H. 1984.
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7 | The impact of soil change on ec
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Rockström et al. (2009) suggest we
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0.0 Response 1.0 Water quality Soil
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One approach to maintaining soil he
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Author Database Used Extent Estimat
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salinization. Safe design and opera
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The second limitation to prediction
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Figure 7.6 Some soil-related feedba
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soils occurs on largely unmanaged a
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extremes several weeks in advance (
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The direct effect of aerosols on th
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capacity declines as N loads increa
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The concept of the critical load of
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as it indicates that management and
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10-year frequency Ten-year frequenc
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phenomena such as the onset of mass
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Although poorly explored, diversity
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affect the health of humans and ani
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Bever, J.D., Westover, K.M. & Anton
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Damoah, R., Spichtinger, N., Servra
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Fenn, M.E., Poth, M.A., Aber, J.D.,
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Heimann, M. & Reichstein, M. 2008.
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Koster, R.D., Dirmeyer, P.A., Guo,
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Naeem, S., Bunker, D.E., Hector, A.
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Raufman, Y.J. & Fraser, R.S. 1997.
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Sheffield, J. & Wood, E.F. 2007. Pr
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UNEP. 2012. Policy Implications of
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8 | Governance and policy responses
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contemporary challenge for policy m
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Year 1982 FAO World Soil Charter 19
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Ensure integrated management of pes
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8.4 | Regional soil policies 8.4.1
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while in areas with fertile soils t
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In New Zealand, there are few regul
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The SEEA Central Framework identifi
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EC. 2013. Decision No 1386/2013/EU
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World Bank. 2011. Rising Global Int
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9.1 | Introduction Land degradation
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Figure 9.1 Agro-ecological zones in
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The soils are strongly weathered an
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It exposes the soil to the erosive
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In many African cultures, harvestin
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Maputo accounts for 83 percent of t
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Poverty: General poverty of the far
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Considering that over 80 percent of
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Extent of SOM decline in the region
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Many farmers do not follow recommen
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9.5 | Case studies 9.5.1 | Senegal
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Figure 9.7 Extent of dominant degra
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management, it is important to note
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From 2006, several further national
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Figure 9.12 Actual water erosion pr
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Figure 9.13 Topsoil pH derived from
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Figure 9.14 Change in land-cover be
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Waterlogging Compaction Soil sealin
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Birru, T.C. 2002. Organic matter re
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Hein, L. & De Ridder, N. 2006. Dese
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Meyer, J.H., Harding, R., Rampersad
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Smith P. 2008. Soil organic carbon
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10 | Regional Assessment of Soil Ch
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Figure 10.1 Length of the available
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Figure 10.2 Threats to soils in the
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10.3.4 | Soil acidification There i
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In paddy rice cultivation and uplan
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10.3.10 | Sealing and capping Seali
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practices. On low slopes, agronomic
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(Valentin et al., 2008). For peatla
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in Laos (59 kg N ha -1 ). On the ot
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Sub-Regions. Inceptisols are the do
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10.5.2 | Case study for Indonesia T
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Peat fire is another important proc
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An agricultural soil monitoring pro
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The Basic Soil-Environmental Monito
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Figure 10.8 Estimate CH 4 emission
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Threat to soil function Soil erosio
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References Aggarwal, G.C., Sidhu, A
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FAO. 2012. FAOSTAT. Rome, FAO. (Als
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Kukal, S.S. & Aggarwal, G.C. 2003.
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Piao, S., Fang, J., Ciais, P., Peyl
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Taniyama, I. 2003. Study of soil fa
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Zhao, Y., Duan, L., Xing, J., Larss
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11.1 | Introduction The majority of
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The internal stratification within
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Mediterranean zone This zone by def
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(5) Salinization and sodification I
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The real extent of diffuse soil con
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While there is no harmonised exhaus
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Prepared by I. Alyabina Figure 11.2
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This is due to the country’s geo-
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Future changes in climate and land
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Considering an increase of industri
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Comparison of cultivated soils with
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Figure 11.3 Some types and extent o
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The plains in the basins of Amu Dar
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Threat to soil function Soil sealin
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References Acosta, J.A., Faz, A., J
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Inisheva, L.I. (ed.). 2005. Concept
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van Lynden, G.W.J. 1997. Guidelines
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12.1 | Introduction This chapter di
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Figure 12.1 Biomes in Latin America
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Temperate Grasslands, Savannahs and
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humid. The most common soil groups
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12.3.6 | Compaction In LAC there ar
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New regional information has been g
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Primary forests have higher carbon
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Prepared by C. Cruz-Gaistardo Figur
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The salinity of soils on the cultiv
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Figure 12.6 Expansion of the agricu
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Figure 12.7 Percentage of areas aff
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Figure 12.8 Predominant types of la
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Boddey, R.M., Alves, B.J.R, Jantali
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Gardi, C., Angelini, M., Barceló,
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Nogueira, M.A., Albino, U.B., Brand
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Spavorek, G., Bemdes, G., Barreto,
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13 | Regional Assessment of Soil Ch
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The Arab Centre for the Study of Ar
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Poverty within this system is exten
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Wind erosion A review conducted by
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13.3.5 | Soil salinization/sodifica
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13.3.9 | Compaction Soil compaction
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13.4 | Major soil threats in the re
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In Sudan, studies showed that in ar
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2002). There are few studies on the
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Consequences of salinization Salini
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Rates of C change are influenced no
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Figure 13.3 Layout of the project s
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13.5 | Case studies 13.5.1 | Case s
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Studies show that both climatic and
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2 - Land degradation assessment map
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Figure 13.9 Type of ecosystem servi
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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 and 502: 14.4.4 | Soil biodiversity Soil bio
Page 503 and 504: Figure 14.5 Risk of water erosion i
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: 15.5 | Threats to soils in the regi
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
Page 553 and 554: Bui, E.N., Hancock, G.J. & Wilkinso
Page 555 and 556: Hartemink, A.E. 1998b. Acidificatio
Page 557 and 558: Moorehead, A. (ed.). 2011. Forests
Page 559 and 560: Robertson, M.J., George, R.J., O’
Page 561 and 562: Wilson, B.R. & Lonergan, V.E. 2013.
Page 563 and 564: 16.1 | Antarctic soils and environm
Page 565 and 566: 16.3 | Response All activities in A
Page 567 and 568: IAATO. 2014. Tourism statistics. In
Page 569 and 570: Annex | Soil groups, characteristic
Page 571 and 572: a Photo by C. Tarnocai b Photo by S
Page 573 and 574: Figure A 2 (a) An Anthrosol (Plagge
Page 575 and 576: a Photo by P. Charzyński Figure A
Page 577 and 578: a Photo by A. Filaretova b Photo by
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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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