The Extent to which Potential Benefits to EU Farmers of Adopting Transgenic Crops are Reduced by Cost of Compliance with Coexistence Regulations
Ian McFarlane and Julian Park
University of Reading, UK
MODUL University Vienna
This article forecasts the extent to which the potential benefits of adopting transgenic crops may be reduced by costs of compliance with coexistence regulations applicable in various member states of the EU. A dynamic economic model is described and used to calculate the potential yield and gross margin of a set of crops grown in a selection of typical rotation scenarios. The model simulates varying levels of pest, weed, and drought pressures, with associated management strategies regarding pesticide and herbicide application, and irrigation. We report on the initial use of the model to calculate the net reduction in gross margin attributable to coexistence costs for insect-resistant (IR) and herbicide-tolerant (HT) maize grown continuously or in a rotation, HT soya grown in a rotation, HT oilseed rape grown in a rotation, and HT sugarbeet grown in a rotation. Conclusions are drawn about conditions favoring inclusion of a transgenic crop in a crop rotation, having regard to farmers’ attitude toward risk.
Key words: biotechnology, coexistence, crop rotation, economic, modelling, risk, transgenic.Introduction
Since the first wide-scale planting of transgenic crops, the area grown globally has expanded rapidly with about 170 million ha grown in 2012—principally maize, cotton, soya, and canola. There were five countries (United States, Brazil, Argentina, Canada, and India) in which transgenic crops were grown on more than 10M ha (James, 2013). Of the established transgenic crops, only insect-resistant (IR) maize is approved for cultivation in the European Union (EU), and that crop is grown mainly in Spain and Portugal. Some of the other established transgenic crops could potentially be profitable for farmers to adopt in some parts of Europe (Park, McFarlane, Phipps, & Ceddia, 2011), but it is likely that the improvement in gross margin relative to a conventional crop would be offset by the cost to the farmer of compliance with coexistence regulations.
Many previous studies have been published concerning the economic impact of transgenic crops, and a few of these economic studies have been based on the formal representation of economic models. Some examples include the following.
In this article we report preliminary results obtained from the model for IR and herbicide-tolerant (HT) maize grown in a rotation, HT soya grown continuously or in a rotation, HT oilseed rape grown in a rotation, and HT sugarbeet grown in a rotation. These scenarios have been selected based on crop rotation researches (Benjamin, Milne, Parsons, Cussans, & Lutman, 2009; Castellazi et al., 2008; Colbach, Granger, & Meziere, 2013) that suggest that these events are both potentially available and could have benefits if grown with the EU. The article concludes by discussing briefly the likely take-up rate given farmers’ attitudes to risk.
Description of the Model
The model of economic consequences of transgenic crops in the EU (METE) dynamic simulation model has been constructed to provide individual crop or rotational gross-margin output. The model has been constructed in Microsoft Visual Basic.
Time period: Crop rotations typically extend over two to seven years; the model accommodates scenarios of crop sequences adopted over any period within this range. This enables the effects of crop and crop management choices on subsequent crops to be modelled.
Time step: As the model is an economic model as opposed to a model of crop development, we considered that one-month time steps are sufficient to model the management decisions that may be made during a crop cycle.
Area to be modelled: Coexistence costs are largely set by the need to provide separation from conventional crops on adjacent land, so the cost will vary with the area occupied by a transgenic crop. The model allows for simulations with a range of field sizes; for instance, the user can specify average field sizes between 5 and 80 ha.
Five regions: The AMIGA field research is based on five biogeographic regions: Atlantic (Ireland, UK, Denmark, Netherlands, Belgium, Portugal, Luxembourg), Boreal (Finland, Sweden, Estonia, Latvia, Lithuania), Continental (Austria, Germany, Slovakia, Hungary, Czech Republic, Poland, Slovenia), Mediterranean (France, Italy, Spain, Cyprus, Greece, Malta), and Balkans (Bulgaria, Romania). The model has been designed to distinguish between these regions.
Choice of sets of crops: The model allows the selection of conventional crops and crop sequences that are common in a given biogeographic region. Where theoretically appropriate, the GM alternative can be selected.
Physical and economic parameters: A table of typical yield per hectare of the selected crops, together with seed costs and ex-farm value per tonne at harvest was compiled using published data from Brookes (2012). Further costs taken into account are the costs of tillage, pesticides, and herbicides, together with, for some regions and crops, the cost of irrigation. This data was derived from Lang (2011) and Nix (2013).
Model calculations are initiated from a user form (Figure 1) after specifying
Figure 1. Form for selecting simulation details.
The model computes the predicted variations in yield of each crop in a cycle of continuous growth or crop rotation. Many possible crop sequences can be assessed for an arable farm of a specific size in any one of the five regions of the EU identified in the AMIGA project. Simulation proceeds in monthly steps, with crop potential yield re-estimated each month that the crop is in the soil, in response to simulated levels of pressure associated with pests, weeds, and drought and the management decisions associated with these pressures. Potential yield variation in response to the various pressures is calculated using coefficients obtained from published data (i.e., Brookes, 2005; Fulton & Keyowski, 1999; Gómez-Barbero, Berbel, & Rodríguez-Cerezo, 2008; Otiman, Badea, & Buzdugan, 2008).
The yield of each crop in a sequence is initially assumed to be as in published data for that crop for typical farms in that region. Then the potential yield is recalculated as an empirical function of
Impairment of potential yield due to multiple simultaneous pressures is assumed to be less than would have been imposed by the sum of those pressures acting separately (i.e., a crop already affected by a strong pressure is only partially further impaired by other unrelated pressures).
Model validation has been undertaken; this shows that the outcomes are consistent with ex-post published data of reports of the performance of IR and HT crops, particularly reports of the Bt maize grown in Spain (Gómez-Barbero et al., 2008). Ex-post data on the performance of Bt maize in the Czech Republic (Kocourek & Stara, 2012) confirmed yield losses of 10% to 15% of conventional maize under pressure from the European corn borer (ECB) in 50% of fields, with Bt maize being 100% effective in preventing loss of yield.
Bt maize MON810 is the only transgenic cereal crop approved for cultivation in the EU. In Figure 2, the gross margin per hectare is predicted for a maize crop affected by pest pressure. The model outcomes are consistent with the evidence from Spain, and indicate that for a large field, i.e. 40 ha, the cost of Bt technology and the cost of compliance with coexistence regulations reduce the gross margin when pest pressure is absent, but the protection of crop yield provided by the technology has a positive impact on gross margin at most levels of pest pressure experienced in the maize-growing regions of Spain in which ECB is present. However, the cost of compliance with coexistence regulations is greater when maize is grown in small fields or blocks because the buffer zone forms a proportionately greater part of the field space. For a field or block of only 5 ha, the model predicts that coexistence costs reduce gross margin further by €60/ha, and the technology is then only beneficial in conditions of severe pest pressure. This is consistent with the incentive for ‘clustering’ of fields for transgenic crop cultivation assessed by Demont and Devos (2008), who noted their expectation that clustering will precede any implementation of costly coexistence measures. The findings of Ceddia, Bartlett, and Peddings (2009) concerning field size and clustering in their modelling of the effect of buffer zones, crop areas, and spatial aggregation with reference to HT oilseed rape confirm that increasing spatial aggregation reduces coexistence costs.
Figure 2. Model outcomes for conventional and Bt maize.
There are various parameters that can be tested for sensitivity. For brevity, the sensitivity analysis illustrated here relates to the amount and timing of pesticide applied by farms growing continuous maize that may choose to adopt IR maize—the aim being to show how a farmer’s perception of risk can influence model performance and predicted profitability. The first farm is the ‘baseline,’ where pesticide is used in recommended quantities, and the manager only applies additional pesticide when moderate pest damage is apparent. The second farm is a ‘risk-taker’ where the manager hopes to escape pest damage without the full recommended pesticide application, and delays further applications later than the ‘baseline’ manager. The third farm is ‘risk-averse’ and initially applies more than the recommended pesticide application and continues to spray even at moderate signs of pest damage.
Figure 3 shows the predicted outcomes for the three cases; the insurance cost to the ‘risk-averse’ farm tends to depress the gross margin achieved with conventional maize in a region where pest pressure is a known hazard.
Figure 3. Effect of varying extent of managerial risk-taking with conventional maize.
Figure 4 shows the equivalent outcomes after adoption of IR maize; the inherent protection against pests provided by the IR trait provides all managements with confidence that pests will cause only minor damage, and attitudes to risk only become relevant at extreme levels of risk of pest damage. This reduces the sensitivity of gross margin to managerial decision making, as demonstrated in Figure 4.
Figure 4. Effect of varying extent of managerial risk-taking with IR maize.
The model is readily adaptable for simulation of the economic performance of a wide range of crops grown continuously or in rotations, subject to a wide range of pressures and treatments. Here, the effects on gross margin for a selection of typical cultivation sequences in selected regions of the EU are reported. Typical gross margins for other crops grown in EU member states were taken from Brookes (2012) and from EU cereal farms report 2012 (European Commission, Directorate General for Agriculture and Rural Development, 2013).
Besides maize, the only other European transgenic crop for which data was available was the HT soyabean grown in Romania prior to accession into the EU. Using ex-post surveys of farmers who were early adopters in Romania, Brookes (2005) suggested gross margin improvements derived from improved yields and improved quality of seed, coupled with lower costs of production, but comparison was being made with low level of previous performance.
HT soyabean is the most widely grown of all GM crops, grown on 80M ha in 2012, and representing 81% of world production of soyabeans (James, 2013). However, only a few regions of Europe are suitable for soyabean cultivation. We have used data from the successful cultivation of HT soyabeans in Romania up to cessation (as a condition of accession to the EU; Brookes, 2005; Otiman et al., 2008) and cultivation elsewhere (Brookes & Barfoot, 2009) to predict the gross margin for HT compared with conventional soyabeans. Simulations presented in Figure 5 suggest that there is likely to be little advantage in adopting HT soyabeans for small-scale cultivation when weed pressures are low; but, on a larger scale, the transgenic crop provides insurance against weed pressure. The simulation includes the assumption of 25% technology premium for HT soyabean seed, and if the supplier is able to offer a reduction in that premium, adoption of HT soyabean is correspondingly more likely to be profitable.
Figure 5. Model outcomes for conventional and HT soyabean.
Soyabeans are frequently grown in rotation with maize, and Figure 6 shows the predicted combined effect of cultivation of Bt maize and HT soyabeans in place of conventional maize and soya in rotation involving both crops. The severe effect of pest damage on conventional maize tends to dominate over the minor advantage of adopting HT soya in a rotation of mainly conventional maize, but if IR maize is then adopted in place of conventional maize, gross margin is protected against both forms of pressure.
Figure 6. Soyabean in rotation with maize (Region 1).
Figure 7 shows model output for HT rape (canola) grown in place of conventional oilseed rape in rotation with milling wheat. The canola crop leaves the soil free from weed pressure—to the advantage of the subsequent wheat crop—to the extent that Canadian farmers are able to adopt a ‘no-till’ practice. In the simulation, there is an assumption that there is a small improvement in yield in the following wheat crop, but the model does not at this stage include a ‘no-till’ scenario.
Figure 7. OSR in rotation with wheat (Region 3).
Figure 8 shows the predicted benefit of substituting HT sugarbeet in rotation between winter milling wheat and spring wheat (data from Dillen, Demont, Tillie, & Rodríguez-Cerezo, 2013). Under relatively low weed pressure, the conventional sugarbeet is predicted to offer a higher gross margin, but sugarbeet is known to be vulnerable to weed pressure.
Figure 8. Sugarbeet in rotation with wheat (Region 4).
A common feature of all model results is that the direct cost of compliance with coexistence regulations is higher for farms that grow the crops on large contiguous areas or those that have near neighbors who grow conventional crops, because the cost of maintaining a buffer zone falls on the farm growing the transgenic crop. Indeed in the few instances where neighboring farms agree that they will all adopt a transgenic crop, the cost of coexistence can be vanishingly small (Skevas, Fevereiro, & Wesseler, 2010).
Other simulation runs demonstrate the use of the METE model to predict the performance of HT soyabean, oilseed rape, and sugarbeet if EU authorities permit cultivation of these HT crops in place of conventional crops.
Initial simulation runs of the METE model suggest it can provide a useful tool to outline some of the gross margin implications of introducing GM crops into existing crops, or growing crops continuously (as with maize in some areas). Further work is needed to calibrate weed, pest, and drought pressure against empirical yield data so that the model can more accurately predict the point at which the use of GM varieties is likely to become profitable to the farmer. This “tipping” point is also dependent on the coexistence measures required in a particular growing region.
Nonetheless, the way in which the cost of compliance with regulations for coexistence of transgenic crops with conventional crops in EU arable farming falls entirely on the adopter of the transgenic crop presents a significant economic disincentive for transgenic crop adoption. Overall, the preliminary outcomes from our model suggest that there are numerous crop rotation scenarios where weed and pest pressures are high, in which the aggregate economic outcome could potentially lead to greater profit for the farmer if established transgenic crop varieties replaced conventional equivalent crops.
Anderson, D., & Cavendish, W. (2001). Dynamic simulation and environmental policy analysis: Beyond comparative statics and the environmental Kuznets curve. Oxford Economic Papers, 53, 721-746.
Benjamin, L.R., Milne, A.E., Parsons, D.J., Cussans, J., & Lutman, P.J.W. (2009). Using stochastic dynamic programming to support weed management decisions over a rotation. Weed Research, 49(2), 207-216.
Bohanec, M., Mess&ecute;an, A., Scatasta, S., Angevin, F., Griffiths, B., Krogh, P.H., et al. (2008). A qualitative multi-attribute model for economic and ecological assessment of genetically modified crops. Ecological Modelling, 215, 247-261.
Brookes, G. (2005). The farm-level impact of herbicide-tolerant soybeans in Romania. AgBioForum, 8(4), 235-241. Available on the World Wide Web: http://www.agbioforum.org.
Brookes, G. (2012). European arable crop profit margins 2010/2011. Gloucester, UK: GBC Ltd.
Brookes, G., & Barfoot, P. (2009). Global impact of biotech crops: Income and production effects, 1996-2007. AgBioForum, 12(2), 184-208. Available on the World Wide Web: http://www.agbioforum.org.
Castellazi M.S., Wood, G.A., Burgess, P.J., Morris, J., Conrad, K.F., & Perry, J.N. (2008). A systematic representation of crop rotations. Agricultural Systems, 97(1-2), 26-33.
Ceddia, M.G., Bartlett, M., & Perrings, C. (2009). Quantifying the effect of buffer zones, crop areas and spatial aggregation on the externalities of genetically modified crops at landscape level. Agriculture, Ecosystems and Environment, 129(2009), 65-72.
Colbach, N., Granger, S., & Meziere, D. (2013). Using a sensitivity analysis of a weed dynamics model to develop sustainable cropping systems. II. Long-term effect of past crops and management techniques on weed infestation. Journal of Agricultural Sciences, 151, 247-267.
Demont, M., & Devos, Y. (2008). Regulating coexistence of GM and non-GM crops without jeopardizing economic incentives. Trends in Biotech, 26(7), 353-358.
Dewar, A.M., Haylock, L.A., Bean, K.M, & May, M.J. (2000). Delayed control of weeds in glyphosate-tolerant sugar beet and the consequences on aphid infestation and yield. Pest Management Science, 56(4), 345-350.
Dillen, K., Demont, M., Tillie, P., & Rodríguez-Cerezo, E. (2013). Bred for Europe but grown in America: The case of GM sugar beet. New Biotechnology, 30(2), 131-135.
European Commission, Directorate General for Agriculture and Rural Development. (2013, March). EU cereal farms report 2012 based on FADN data. Brussels: Author. Available on the World Wide Web: http://ec.europa.eu/agriculture/rica/pdf/cereal_report_2012.pdf.
Fulton, M., & Keyowski, L. (1999). Producer benefits of herbicide-resistant canola. AgBioForum, 2(2), 85-93. Avaialble on the World Wide Web: http://www.agbioforum.org.
Gómez-Barbero, M., & Rodríguez-Cerezo E. (2006). Economic impact of dominant GM crops worldwide: A review (JRC report EUR 22547 EN). Seville, Spain: European Commission, Joint Research Centre (JRC), Institute for Prospective Technological Studies (IPTS).
Gómez-Barbero, M., Berbel, J., & Rodríguez-Cerezo, E. (2008). Adoption and performance of the first GM crop introduced in EU agriculture: Bt maize in Spain (JRC report EUR 22778EN). Seville, Spain: European Commission, JRC, IPTS.
James, C. (2013). Global status of commercialized biotech/GM crops: 2012 (ISAAA Brief No. 44). Ithaca, NY: International Service for the Acquisition of Agri-biotech Applications (ISAAA).
Kocourek, F., & Stara, J. (2012). Efficacy of Bt maize against European corn borer in Central Europe. Plant Protection Science, 48(Special Issue), S25-S35.
Munro, A. (2008). The spatial impact of genetically modified crops. Ecological Economics, 67(4), 658-666.
Lang, B. (2011). Farm business survey 2009/2010 crop production in England. Cambridge, UK: Rural Business Research.
Nix, J. (2013). Farm management pocketbook (43rd Edition). Melton Mowbray, UK: Agro Business Consultants Ltd.
Otiman, I.P., Badea, E.M., & Buzdugan, L. (2008). Roundup Ready soybean, a Romanian story. Bulletin UASVM Animal Science and Biotechnologies, 65(1-2), 352-357.
Park, J., McFarlane, I., Phipps, R., & Ceddia, G. (2011). The impact of the EU regulatory constraint of transgenic crops on farm income. New Biotechnology, 28(4), 396-406.
Skevas, T., Fevereiro, P., & Wesseler, J. (2010). Coexistence regulations and agriculture production: A case study of five Bt maize producers in Portugal. Ecological Economics, 69, 2402-2408.
van Ittersum, M., Ewert, F., Heckelei, T., Wery, J., Olsson, J.A., Andersen, E., et al. (2008). Integrated assessment of agricultural systems—A component-based framework for the European Union (SEAMLESS). Agricultural Systems, 96(2008), 150-165.
Suggested citation: McFarlane, I., Park, J., & Ceddia, G. (2014). The extent to which potential benefits to EU farmers of adopting transgenic crops are reduced by cost of compliance with coexistence regulations. AgBioForum, 17(1), 37-43. Available on the World Wide Web: http://www.agbioforum.org.
|© 2014 AgBioForum | Design and support provided by Express Academic Services | Contact ABF: firstname.lastname@example.org|