Profit and risk in dryland cropping: seasonal forecasts and fertiliser management Peter C. McIntosh1, Senthold Asseng2, Enli Wang3 CSIRO Oceans & Atmosphere Flagship, GPO Box 1538, Hobart TAS 7001, Australia, [email protected] Department of Agricultural & Biological Engineering, University of Florida, Gainesville, FL 32611, USA, [email protected] 3 CSIRO Agriculture Flagship, GPO Box 1666, Canberra ACT 2601, Australia, [email protected] 1 2 Abstract Fertiliser management in dryland cropping involves a trade-off between risk and return. Increasing the fertiliser application rate can increase profit in good years, but may lead to a loss in bad years. Farmers try to avoid the potentially serious consequences of consecutive loss years by adopting a conservative strategy, typically applying $1 of fertiliser only when the long-term net return would be $2. A forecast of seasonal rainfall can help inform fertiliser management decisions; application rates can be increased in forecast good years and decreased in forecast bad years. The value of a seasonal forecast of above/below median rainfall was determined at a variety of sites in the Australian wheat belt. The long-term value of the forecast varied from $16/ha to $80/ha, compared to a realistic conservative strategy without a forecast. This value was achieved with little increased risk. The same value could be obtained by increasing fertiliser rates in every year, but the risk was higher. Seasonal forecasts give probabilistic information about the seasonal bias and are therefore valuable in the long-run rather than in any given year. At the sites studied, and at an 80% level of surety, seasonal forecast information was of value over time periods ranging from three to eight years. Key words Risk-averse nitrogen management, variable climate Introduction The application of nitrogen fertiliser in dryland cropping requires a balance between risk and return. The optimum fertiliser rate will vary from year to year depending on seasonal rainfall. Too much fertiliser in a dry year can lose money, while too little fertiliser in a wet year is a lost opportunity. Forecasts of seasonal rainfall are now sufficiently skilful that they can be of considerable value when benefits are averaged over a number of years. In the southern part of the Western Australian wheat belt, it has been shown that even moderately skilful seasonal forecasts of rainfall can have a value exceeding A$50 /ha when averaged over 27 years (Asseng et al., 2012). This value exceeds that of previous studies (e.g. Ash et al., 2007; McIntosh et al., 2007; Moeller et al., 2008; Wang et al., 2008) because of the use of a realistic and conservative baseline management strategy in the absence of a forecast. Seasonal forecasts are, by necessity, probabilistic rather than deterministic, regardless of the method used. It is not possible to give definitive predictions at seasonal timescales because of the chaotic behavior of the climate system. However, it is possible to make probabilistic statements about the chances of rainfall in the coming season. The simplest format is to specify whether the rainfall is likely to be above or below the long-term median value. The use of probabilistic information is not familiar to many people, and there can be a tendency to reject a forecast system if the most likely outcome does not eventuate when it is first used. However, the value of a probabilistic forecast system lies in the longer term, and it is important to communicate this fact clearly. This work had two goals. The first was to demonstrate that the excellent results achieved by Asseng et al. (2012) in Western Australia are likely to be achievable in the eastern wheat-belt of Australia as well. The second goal was to start to explore the number of years a forecast should be used in order to be reasonably certain (at some level of probability) that it adds value. Methods The methods used here closely follow those used by Asseng et al. (2012) in Western Australia. The experiments were designed to explore the value of climate forecasts in the absence of other factors, such © 2015 “Building Productive, Diverse and Sustainable Landscapes “ Proceedings of the 17th ASA Conference, 20 – 24 September 2015, Hobart, Australia. Web site www.agronomy2015.com.au as carryover from year-to-year of nitrogen and stored soil water, disease, pest, frost, heat stress and crop rotation. It will be desirable in future studies to extend the realism of the simulation and explore non-linear interactions by incorporating some or all of these additional factors. There were four study sites in New South Wales (NSW) spanning low to moderate rainfall regimes for the May-Nov growing season: Griffith (245 mm), Ardlethan (292 mm), Temora (329 mm) and Young (421 mm). A continuous wheat system on red Chromosol soil was simulated using APSIM Wheat version 7.5 (Holzworth et al., 2014). cultivar was sown according tomoderate a variablerainfall sowing rule: when There were four study sitesThe in New South“Scout” Wales (NSW) spanning low to regimes for the30 mm total rain fell in 10 consecutive days between 15 April and 10 July, or on 10 July if there was insufficient May-Nov growing season: Griffith (245 mm), Ardlethan (292 mm), Temora (329 mm) and Young (421 rain. Soil water was resetsystem to the on lower and nitrogen to 50 using kg N/ha on 15Wheat April.version 7.5 mm). A continuous wheat red limit Chromosol soil wasreset simulated APSIM (Holzworth et al., 2014). The cultivar “Scout” was sown according to a variable sowing rule: when 30 mm total rain fell in 10 consecutive 15 April by anda10 July,oforprofit on 10ratios July iffrom there$0was Nitrogen fertiliser was applieddays at abetween rate determined range to insufficient $3 per $1 of rain. Soil water was reset to the lower limit and nitrogen reset to 50 kg N/ha on 15 April. fertiliser applied. A profit ratio of $0 means that the fertiliser rate is determined from the maximum of the gross margin (GM) versus N curve from past years. A profit ratio of $3 is determined from where the GM Nitrogen fertiliser was applied at a rate determined by a range of profit ratios from $0 to $3 per $1 of versus N curve has a slope of 3:1, and will generally result in a much smaller application of N. Farmers in fertiliser applied. A profit ratio of $0 means that the fertiliser rate is determined from the maximum of the Western Australia that they a profit of $2-3 (Asseng et al., gross margin (GM) indicated versus N curve fromgenerally past years.operated A profitatratio of $3ratio is determined from where the2012) GM so as to reduce the risk of losing money in a dry year. versus N curve has a slope of 3:1, and will generally result in a much smaller application of N. Farmers in Western Australia indicated that they generally operated at a profit ratio of $2-3 (Asseng et al., 2012) so as to reduce the risk of losing money inrainfall a dry year. Forecasts of May to November made on 1 May were obtained from the Australian Bureau of Meteorology’s Predictive Ocean-Atmosphere Model for Australia (POAMA). This model is a dynamical Forecasts of Mayocean-atmosphere-land to November rainfall made on 1 May wereinitialized obtained from theforecast Australian Bureau of a vast global coupled computer model at each start time from Meteorology’s Predictive Ocean-Atmosphere Model for Australia (POAMA). This model is a dynamical network of atmosphere and ocean observations (e.g. Hudson et al., 2013; Zhao et al., 2014). The model global coupled ocean-atmosphere-land computer model initialized at each forecast start time from a vast provides retrospective forecasts extending back to 1981. While POAMA provides multiple forecasts to network of atmosphere and ocean observations (e.g. Hudson et al., 2013; Zhao et al., 2014). The model explore the spread of forecasts possible extending outcomes,back we simply thePOAMA mean rainfall at each site forecasts and compared this to provides retrospective to 1981.used While provides multiple to the model’s long-term mean rainfall there. At the four sites in NSW, POAMA correctly predicted whether explore the spread of possible outcomes, we simply used the mean rainfall at each site and compared this to rainfall would be above or rainfall below the median 74% and 81% of thecorrectly time. predicted whether the model’s long-term mean there. At thebetween four sites in NSW, POAMA rainfall would be above or below the median between 74% and 81% of the time. If the forecast in a particular year was for above median rainfall, then the GM versus N curve from which Ifthe thefertiliser forecastrate in a was particular year was forconstructed above median rainfall, then theyears GM versus curve fromwas which the determined was from all historical whereNthe rainfall observed fertiliser rate was determined was constructed from all historical years where the rainfall was observed to be to be above the median. The below median case was treated similarly. In experiments where no forecast was above the median. The below median case was treated similarly. In experiments where no forecast was required, all historical years back to 1981 were used. Example curves for Nyabing are shown in Figure 1; the required, all historical years back to 1981 were used. Example curves for Nyabing are shown in Figure 1; the othersites sitesare arequalitatively qualitativelysimilar. similar. See Asseng et al. (2012) further details about the method. other See Asseng et al. (2012) for for further details about the method. Figure 1. application forfor all all years (black), above median rainfall yearsyears (blue)(blue) Figure 1. Gross Grossmargin marginversus versusNNfertiliser fertiliser application years (black), above median rainfall and years (red) at at Nyabing, WA. TheThe N rate appropriate to a to profit ratioratio of $2of for$2each andbelow belowmedian medianrainfall rainfall years (red) Nyabing, WA. N rate appropriate a profit for $1 each $1 applied N is indicated by the green arrows. The other sites are qualitatively similar. applied N is indicated by the green arrows. The other sites are qualitatively similar. The “break-even time” is the number of years a farmer would need to grow a crop in order to be, say, 95% © 2015 “Building Productive, Sustainable “ time can then be compared between experiments sure that the farm is not Diverse losing and money. The Landscapes break-even Proceedings of the 17th ASA Conference, 20 – 24 September 2015, Hobart, Australia. Web site www.agronomy2015.com.au using different profit ratios, or between experiments with and without a forecast. Figure 2 shows the 5th and © 2015 "Building Productive, Diverse and Sustainable Landscapes " 2 The “break-even time” is the number of years a farmer would need to grow a crop in order to be, say, 95% sure that the farm is not losing money. The break-even time can then be compared between experiments using different profit ratios, or between experiments with and without a forecast. Figure 2 shows the 5th th 95 percentiles of gross margin for all combinations of modelled years taken n at a time, where n is the th and 95 percentiles margin for all combinations modelled taken n atmodelled, a time, where is the number of years along of thegross x-axis. For example, at Nyabing,of where there years were 27 years therenare number of yearsofalong the10x-axis. Nyabing, where 27 yearsmeans modelled, therethe are many subsamples length years.For Theexample, statisticalatdistribution of thethere set ofwere subsample provides many subsamples of length 10 years. The statistical distribution of the set of subsample means provides the percentiles when n=10. percentiles when n=10. Figure 2. Gross margin 5th and 95th percentiles over varying numbers of years (subsample sizes) for a profit th Figure margin and ratio 95th percentiles over results varyingare numbers of years (subsample sizes) for a profit ratio 2. of Gross $2 (green) and5profit $0 (red). These for Nyabing, WA. The break-even time is indicated ratio of $2the (green) and profit ratio $0positive. (red). These results are for Nyabing, WA. The break-even time is indicated where 5th percentile becomes where the 5th percentile becomes positive. Results We compared the original Western Australian site (Nyabing) with preliminary modeling at the four eastern Results Australian sites. Further refinement of starting soil moisture and the sowing rule will be necessary to fully Weaccount compared the differences original Western Australian sitein(Nyabing) withwest. preliminary modeling at the four easternhave for the between conditions the east and However, these initial experiments Australian sites. Further refinement of starting soil moisture and the sowing rule will be necessary to fully shown encouraging gains from a seasonal forecast. At a $2 profit ratio, using a forecast increased the longaccount for the differences between conditions in the east and west. However, these initial experiments have term profit at all sites between $16 /ha (Griffith) and $80 /ha (Ardlethan). The original value at Nyabing (on a shown encouraging gains from a seasonal forecast. At a $2 profit ratio, using a forecast increased the longclay soil)atwas It is clear the good results obtained in WA byThe Asseng et al.value (2012) will be feasible term profit all $65 sitesha. between $16 that /ha (Griffith) and $80 /ha (Ardlethan). original at Nyabing (on in eastern Australia. a clay soil) was $65 ha. It is clear that the good results obtained in WA by Asseng et al. (2012) will be feasible in eastern Australia. There are various possible risk metrics for dryland cropping, such as the percentage of loss years, the mean long-term loss, possible the chance ofmetrics two lossforyears in a cropping, row, and the number years to break a There are various risk dryland such as the of percentage of losseven. years,Using the mean forecast increased all these risks at Nyabing, and increased the mean loss at Temora. All other risks remained long-term loss, the chance of two loss years in a row, and the number of years to break even. Using a the same or decreased. must be compared with the alternative strategy for obtaining therisks sameremained profit; forecast increased all theseThis risks at Nyabing, and increased the mean loss at Temora. All other decreasing the profit ratio and effectively applying more N in each year regardless of the forecast. This the same or decreased. This must be compared with the alternative strategy for obtaining the same profit; amounts the to moving the green arrow to the right along in Figure 1ofuntil profit This equals decreasing profit ratio and effectively applying more the N inblack eachcurve year regardless the the forecast. that obtained using forecast. In this case, outalong of thethefour risks mentioned and1 over sites, the that risk amounts to moving thea green arrow to the right black curve in Figure until the the five profit equals obtained using a forecast. In this of the four risks amentioned andotherwise over the five sites, the increased in 15 out of these 20case, casesout compared to using forecast, and remained therisk same. increased in 15 out of these 20 cases compared to using a forecast, and otherwise remained the same. A forecast adds value when the 5th percentile using a forecast exceeds the 5th percentile when a forecast is not used. It may take a number of years for this to occur. This is a generalisation of comparing break-even times. The number of years taken for a forecast to be of value (at the 80% level) was estimated this way at each site. © 2015 “Building Productive, Diverse and Sustainable Landscapes “ Proceedings ofProductive, the 17th ASA Conference, 20 – 24 September 2015, © 2015 "Building Diverse and Sustainable Landscapes " Hobart, Australia. Web site www.agronomy2015.com.au Proceedings of the 17th ASA Conference, 20 – 24 September 2015, Hobart, Australia. Web site www.agronomy2015.com.au 3 Future calculations will use a more robust bootstrapping method. A forecast was found to be of value after between three and eight years at all sites. This calculation assumes the climate in each year is uncorrelated with neighbouring years. If correlation between years is allowed for, the calculation is only approximate due to the short time sequence available, but the indication is that this time increases by one to three years. Conclusions There is a trade-off between risk and return in dryland cropping because of Australia’s variable climate. Applying more fertiliser each year increased the long-term return, but at an increased risk. By comparison, strategic application of more fertiliser based on a seasonal climate forecast increased the return at reduced risk. A seasonal forecast was found to be of value after three to eight years at the sites studied, and the return was between $16 /ha and $80 /ha, indicating the great potential value of seasonal forecasts. Extension of this work in future studies might take a whole-of-system approach and incorporate additional factors such as knowledge of stored soil moisture at planting. Acknowledgement This work was funded in part by the Managing Climate Variability Program of the Grains Research and Development Corporation. References Ash, A., McIntosh, P., Cullen, B., Carberry, P. and Smith, M.S., 2007. Constraints and opportunities in applying seasonal climate forecasts in agriculture. Crop and Pasture Science, 58(10): 952-965. Asseng, S., McIntosh, P.C., Wang, G. and Khimashia, N., 2012. Optimal N fertiliser management based on a seasonal forecast. European Journal of Agronomy, 38: 66-73. Holzworth, D.P. et al., 2014. APSIM–evolution towards a new generation of agricultural systems simulation. Environmental Modelling & Software, 62: 327-350. Hudson, D., Marshall, A.G., Yin, Y., Alves, O. and Hendon, H.H., 2013. Improving intraseasonal prediction with a new ensemble generation strategy. Monthly Weather Review, 141(12): 4429-4449. McIntosh, P.C., Pook, M.J., Risbey, J.S., Lisson, S.N. and Rebbeck, M., 2007. Seasonal climate forecasts for agriculture: Towards better understanding and value. Field Crops Research, 104(0378-4290, 0378-4290): 130-138. Moeller, C., Smith, I., Asseng, S., Ludwig, F. and Telcik, N., 2008. The potential value of seasonal forecasts of rainfall categories—Case studies from the wheatbelt in Western Australia’s Mediterranean region. Agricultural and Forest Meteorology, 148(4): 606-618. Wang, E., Xu, J.H. and Smith, C.J., 2008. Value of historical climate knowledge, SOI-based seasonal climate forecasting and stored soil moisture at sowing in crop nitrogen management in south eastern Australia. Agricultural and forest meteorology, 148(11): 1743-1753. Zhao, M., Hendon, H.H., Alves, O. and Yin, Y., 2014. Impact of improved assimilation of temperature and salinity for coupled model seasonal forecasts. Climate Dynamics, 42(9-10): 2565-2583. © 2015 “Building Productive, Diverse and Sustainable Landscapes “ Proceedings of the 17th ASA Conference, 20 – 24 September 2015, Hobart, Australia. Web site www.agronomy2015.com.au
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