Mitigation strategies for greenhouse gas emissions from animal production systems: synergy between measuring and modelling at different scales

2008 ◽  
Vol 48 (2) ◽  
pp. 46 ◽  
Author(s):  
J. W. van Groenigen ◽  
R. L. M. Schils ◽  
G. L. Velthof ◽  
P. J. Kuikman ◽  
D. A. Oudendag ◽  
...  

Animal production systems are large and complex sources of greenhouse gases (GHG), especially nitrous oxide (N2O) and methane (CH4). Emissions from these systems are expected to rise over the coming decades due to the increasing global population and shifting diets, unless appropriate mitigation strategies are implemented. In this paper, we argue that the main constraints for such implementation are: (i) the complex and often poorly understood controls of GHG sources in animal production systems; (ii) the lack of knowledge on the economic and social costs involved in implementing mitigation strategies; and (iii) the strong political emphasis on mitigating nitrate leaching and ammonia volatilisation, rather than GHG emissions. We further argue that overcoming these three constraints can only be achieved by initiating integrated mitigation strategies, based on modelling and experimental work at three scales. At the ‘laboratory and field scale’, basic causal relationships with respect to processes of GHG formation and other detrimental fluxes need to be experimentally established and modelled. As management options are considered at the ‘farm scale’, this is the ideal scale to evaluate the cost-effectiveness, feasibility and possible pollution swapping effects of mitigation measures. Finally, at the ‘national and supra-national scales’, environmental legislation is implemented, effectiveness of environmental policies and emissions abatement measures are being monitored, and the social costs of various scenarios are being weighed. We illustrate the need for integral measures and working across different scales using our own work on the relationship between nitrogen surplus and fluxes to the environment. At the field scale, a clear positive relation between nitrogen surplus and N2O emission, NO3– leaching and NH3 volatilisation was experimentally established. At the farm scale, the model DAIRYWISE was used to evaluate effects of minimising nitrogen surplus on the nutrient flow and economic viability of an average Dutch dairy farm. Even after including trade-off effects of CH4 emissions from cattle and manure storage, there was still a clear positive relationship between farm gate nitrogen surplus and GHG emission. At this scale, the prime issue was balancing environmental gains with economic viability. Finally, at the ‘national and supra-national scale’ we developed the MITERRA-EUROPE model, and used it to quantify the effects on GHG emissions of environmental policies aimed at reducing NO3– leaching and NH3 volatilisation in the 27 Member States of the European Union (EU-27). This showed the intricate relationship between different environmental goals, with both positive feedback (balanced fertilisation reduced both NO3– leaching and N2O emission) and negative feedback (‘low-emission’ manure application reduced NH3 volatilisation but increased N2O emission) possible. At this scale, there is a clear need for an integral approach towards reducing environmental assessment to the environment. Our studies so far suggest that ‘balanced fertilisation’ is among the most promising mitigation measures for simultaneously lowering N2O emission, NO3– leaching and NH3 volatilisation, without pollution swapping to CH4 emission.

Animals ◽  
2017 ◽  
Vol 7 (12) ◽  
pp. 75 ◽  
Author(s):  
Maria Yunes ◽  
Marina von Keyserlingk ◽  
Maria Hötzel

2006 ◽  
Vol 63 (2) ◽  
pp. 194-209 ◽  
Author(s):  
Francirose Shigaki ◽  
Andrew Sharpley ◽  
Luís Ignácio Prochnow

Eutrophication has become a major threat to water quality in the U.S., Europe, and Australasia. In most cases, freshwater eutrophication is accelerated by increased inputs of phosphorus (P), of which agricultural runoff is now a major contributor, due to intensification of crop and animal production systems since the early 1990s'. Once little information is available on the impacts of Brazilian agriculture in water quality, recent changes in crop and animal production systems in Brazil were evaluated in the context of probable implications of the fate of P in agriculture. Between 1993 and 2003, there was 33% increase in the number of housed animals (i.e., beef, dairy cows, swine, and poultry), most in the South Region (i.e., Paraná, Rio Grande do Sul, and Santa Catarina States), where 43 and 49% of Brazil's swine and poultry production is located, respectively. Although grazing-based beef production is the major animal production system in Brazil, it is an extensive system, where manure is deposited over grazed pastures; confined swine and poultry are intensive systems, producing large amounts of manure in small areas, which can be considered a manageable resource. This discussion will focus on swine and poultry farming. Based on average swine (100 kg) and poultry weights (1.3 kg), daily manure production (4.90 and 0.055 kg per swine and poultry animal unit, respectively), and manure P content (40 and 24 g kg-1 for swine and poultry, respectively), an estimated 2.5 million tones of P in swine and poultry manure were produced in 2003. Mostly in the South and Southeast regions of Brazil (62%), which represent only 18% of the country's land area. In the context of crop P requirements, there was 2.6 times more P produced in manure (1.08 million tones) than applied as fertilizer (0.42 million tonnes) in South Brazil in 2003. If it is assumed that fertilizer P use represents P added to meet crop needs and accounts for P sorbed by soil in unavailable forms each year, if swine and poultry manure were to replace fertilizer, there would be an annual P surplus of 0.66 million tonnes in the South region alone. These approximations and estimates highlight that, similarly to other parts of the world, there is a potential for surplus P to quickly accumulate in certain regions of Brazil. Unless measures are developed and implemented to utilize manure P, repeated annual surpluses will create an increasingly difficult problem to solve. These measures can be grouped as source and transport management. Source management attempts to decrease dietary P, use feed additives, manure treatment and composting, as well as careful management of the rate, timing, and method of manure applications. Transport management attempts to control the loss of P in runoff from soil to sensitive waters via use of conservation tillage, buffer or riparian zones, cover crops, and trapping ponds or wetlands. These measures are discussed in the contest of Brazil's climate, topography, and land use, and how successful remediation programs may be implemented at farm and watershed level.


2009 ◽  
Vol 2009 ◽  
pp. 78-78
Author(s):  
T Yan ◽  
F J Young ◽  
D C Patterson ◽  
C S Mayne

The European Union Nitrates Directives set a limit on the amount (170 kg/ha) of manure nitrogen (N, = faecal N + urine N) that may be applied to land each year. This limit has very significant implications for stocking rates on intensive livestock farms. Consequently, there is increasing interest in developing mitigation strategies to reduce N output in faeces and urine in animal production systems. The objectives of the present study were to evaluate the effects of dietary crude protein (CP) concentration on the efficiency of N utilisation in lactating dairy cows.


1995 ◽  
Vol 61 (1) ◽  
pp. 1-8 ◽  
Author(s):  
C. R. W. Spedding

Abstract‘Sustainability” has been defined in so many different ways that it no longer has an accepted (or acceptable) meaning. Nevertheless, it is being used as a label to confer respectability on corporate plans and research proposals, practical projects, attitudes and intellectual positions. The weaknesses of current definitions are examined with a view to clarifying the physical, biological and socio-economic objectives, covered by the term ‘sustainable’.Since it is no longer feasible to abandon the term or to restrict its scope, it is worth considering what useful meaning can be attached to the concept. An attempt is made to spell out the tvays in which it could sensibly be used in relation to animal production systems. It is suggested that this would have to take the form of a package of expressions covering the essential attributes offuture animal production systems.


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