drainage of organic soils for cultivation are responsible for about 10-12 per cent of all greenhouse gas emissions (Smith et al. 2007), while agricultural activities contribute, both directly and indirectly, account for about 30 per cent of total anthropogenic emissions (IPCC 2014d). Nevertheless, predictions are that this share could increase drastically.
EU soils contain more than 70 billion tonnes of organic carbon (Lugato et al. 2014), which is equivalent to almost 50 times the EU’s annual greenhouse gas emissions. In 2009,
European cropland emitted an average of 0.45 tonnes of CO2 per hectare (much of which resulted from land conversion). The conversion of peatlands and their use is of particular concern. For instance, although only 8 per cent of farmland in Germany is on peatland, this area is responsible for about 30 per cent of total greenhouse gas emissions for the entire farming sector (De Vos et al. 2015). However, with appropriate management practices, soil organic matter can be maintained and even increased. Apart from peatlands, particular attention should be paid to the preservation of permanent pastures and the management of forests soils. Keeping carbon stocks is thus essential for the fulfilment of present and future emission reduction commitments deriving from the implementation of the Soil Thematic Strategy (EC 2012c). The Life and Soil Protection report (DG Environment 2014) from the EU LIFE Environment programme identifies building soil organic matter as one of four headline priority issues, along with reducing soil erosion, the remediation of contaminated land and promoting targets for soil protection.
127:
Socio-economic factors of land abandonment in Eastern Europe and Central Asia
The breakup of the former USSR and the Council for Mutual Economic Assistance (COMECON) in 1991 began a period of transition from state-controlled to market-driven economies across Eastern Europe and Central Asia that resulted in a fundamental transformation of their agricultural systems and land-use. These transitional economies went through a stage of decline from 1991 to 2000. This economic and social crisis was particularly hard in rural regions, where state support of agriculture ended and rural development ceased almost entirely; where average life expectancy declined from 69 to 65
years, and male life expectancy in rural areas of the Russian Federation declined from 61 to 53 years (Prishchepov et al. 2013). As farming subsidies declined, the high cost of imported herbicides, fungicides and insecticides caused farmers to cut back on their use. Fertilizer use fell by 85 per cent in the Russian Federation and Ukraine and by almost 90 per cent in Kazakhstan between 1990 and 2000. Total grain production fell by more than 50 per cent during the same period (FAO 2013e). Between 1990 and 2000, investments in the Russian Federation agricultural sector declined from $39 billion to $2 billion (Prishchepov et al. 2013).
This free-fall in agricultural production in the Russian Federation, Ukraine and Kazakhstan slowed by 2000 and signs of recovery have been observed in all three countries since 2002-2005, clearly coinciding with the broader economic recovery of the entire region. Due to recovery of some agricultural subsidies and at least the partial success of reforms, fertilizer and machinery use has increased during the past few years. The use of mineral fertilizer has tripled since 1999 in Kazakhstan and doubled in the Russian Federation and Ukraine, but current application rates represent only a fraction of the amounts applied in the late 1980s (Lioubimtseva and Henebry 2012). A return to the 1980s application rates is unlikely and unnecessary, as they were frequently excessive. Between 1996–2000 and 2001–2008, overall yields had grown from 1.3 t/ha to 1.83 t/ha (FAO 2013e). Although weather remains a very important determinant for grain yield, improvements in crop management practices, fueled by growing state subsidies since 2005, have contributed to the recent increase and stabilization of crop yields (Liefert et al. 2013). However, this did not reduce the scale of land abandonment as marginal arable lands grew unprofitable and were gradually abandoned even under high grain demand. In addition, the area under cereals has continued shrinking from 50 million hectares in 1996–2000 to 45 million hectare in 2001– 2008 (FAO 2013e).
The share of harvested land under various major crops has changed in a different way (Figure-L2 46). Wheat has been the primary cereal crop in terms of area harvested and shows a slight increase in harvested area after the half- century of decline that followed the Virgin Lands expansion
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