3.6.2 Summary of the Second Assessment Report
Little has changed in the industrialized agricultural sector during the past
few years apart from the continuing trends towards genetically modified crops
and animals, and reduced chemical input production methods (Section
3.6.4.2). Farming systems remain a major contributor of anthropogenic emissions,
not just from energy inputs but mainly from methane from ruminants (cattle,
goats and sheep), livestock wastes, rice paddy fields, and nitrous oxide from
the application of nitrogenous fertilizers, and circulation of N within crop
and livestock production. Land use change activities, such as the clearance
of forests by burning and cultivation to provide more land for agricultural
production with subsequent soil degradation, are also major contributors (Chapter
4). Carbon sequestration by soils continues to be quantified and estimates
refined further, including the effects from reducing organic matter losses by
changing to minimum tillage techniques. Improved farm management can result
in lower emissions of CH4 and N2O and increased soil carbon
uptake.
New energy saving technologies, such as ice bank refrigeration for milk cooling
(CAE, 1996), continue to be developed, but need to be widely implemented if
they are going to have any significant effects on global greenhouse gas emissions.
Methods to reduce emissions by the agricultural sector are outlined in Section
3.6.4. Energy crop production continues to provide a possible alternative land
use where suitable land is available and markets exist for the products.
3.6.3 Historic and Future Trends
Although on-farm energy intensity (GJ/ha) continues to increase, energy inputs
per unit of production (GJ/t) have tended to decline in modern intensive industrialized
agricultural systems, mainly caused by increasing crop yields (IPCC, 1996).
The current trend in OECD countries is towards less intensive farming systems
because of public concerns for animal welfare, reduced chemical inputs, and
increasing demand for organically grown food. If this demand continues it could
lead to reduced GJ/ha and also to lower GJ/t if yields can be maintained, (though
this is generally not the case for low input farming). Conversely, in developing
countries energy use (both GJ/ha and GJ/t) is increasing in attempts to increase
yields (t/ha) by substituting machinery for manual labour, developing irrigation
schemes, and improving crop storage systems to reduce losses. For example, Indian
agricultural production has increased threefold since 1970 to 200Mt of food
in 1998, whilst during this period animal energy/ha declined 35%, and diesel
and electricity inputs increased by over 15 times (Prasad, 1999).
The development and introduction of biotechnology and gene technology could
offer new chances to accelerate and support the traditional plant and animal
breeding procedures. However, the conflict between food security and environmental
risks is yet to be resolved. In developing countries uptake of transgenic technologies
would require support of the farmers in adopting non-traditional techniques.
If, following a comprehensive risk assessment, public confidence in producing
genetically modified organisms is obtained, it could ultimately result in:
- yield increases per hectare of food and fibre crops;
- improved performance efficiency of livestock animals;
- reduced inputs of agrio-chemicals and fertilizers because of new resistant
cultivars; and
- development of low input cultivars with improved nutrient and water use
efficiency.
Energy inputs per unit of product could be reduced by around 10%-20% as a result,
and methane and nitrous oxide emissions also lowered. For energy crops, improvements
through traditional plant breeding techniques have barely begun. Opportunities
for developing high yielding crops more suitable for energy purposes (such as
high erucic acid oilseed rape) using genetic engineering techniques by transferring
genes through recombinant DNA technology also have potential (Luhs and Friedt,
1998).
More difficult to predict are changes in diet and food consumption based on
availability, quality, health, and environmental decisions. New protein sources
will also impact on land use as will the growing of new crops to provide biomaterials
specifically for manufactured products.
Social problems in rural areas continue to occur as does urban drift, particularly
in developing countries, resulting from unemployment caused by substitution
of manual labour by fossil fuel powered tractors and machinery. Rural economies
are also struggling financially (even in developed countries where farm subsidies
are available) because of current surpluses of many food and fibre commodities
leading to low prices. Therefore, limited funds are available for investment
in more modern, less energy intensive equipment. Further evaluation of combining
traditional manual techniques with modern crops and scientific knowledge to
improve sustainability is required. Possible removal of agricultural subsidies
in Europe and the USA is a further threat to the future profitability of these
rural regions (which may then need to be stimulated through a government development
plan), but could have beneficial effects in terms of reducing greenhouse gas
emissions (Storey, 1997). However, it will also be an opportunity for unsubsidized
energy crops to compete more successfully with the more traditional uses of
the land.
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