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AbstractThis study examines the profitability of phase farming with lucerne for a farming system on the South Coast of Western Australia. Consistent with previous studies, lucerne appears promising within niches in the farming system. However, further improvements in the production and / or utilisation of lucerne are likely to be required before widespread adoption is financially attractive. Several important conclusions emerge from this study:
IntroductionInclusion of lucerne in the farming system is seen by many as a means of addressing several important challenges facing agriculture on the South Coast of Western Australia. These challenges include:
Trial results and farmer experience suggest a promising future for lucerne on the South Coast (e.g. Latta 2002). Despite this, many lucerne stands in the region are still in their first rotation, and cropping after lucerne is a new experience for most farmers. Furthermore, stands of lucerne established in recent years have benefited from a period of favourable wool and sheep prices. Few farmers have yet tested the profitability of lucerne under less favourable market conditions, e.g. such as those endured during much of the 1990s. These and other issues related to lucerne on the South Coast were examined in detail by Bathgate and Pannell (2002). Their analyses indicated a profitable outcome for lucerne in certain niches in the farming system, and identified a range of important profit drivers including soil type mix, lucerne summer growth rates, and wool and sheep prices. This study builds on the work of Bathgate and Pannell (2002) by addressing the following questions …
In addressing these questions, the objective of this paper is to provide information that will assist in prioritising a) extension messages and b) future research needs. MethodsStudy areaThis study focuses on the 400 - 500 mm rainfall belt within the shire of Esperance on the South Coast of Western Australia. Sandy textured soils are dominant, and the area is generally referred to as the Esperance sandplain. Typical farm size is 2,000 - 3,000 ha. Most farms produce a mix of grain, wool and meat. Typically 50 - 60% of arable land is sown to crop with the balance being pasture. Sheep are the dominant livestock enterprise, although cattle are important on some individual farms. The traditional growing season for crops and pasture is May to October, with about two-thirds of annual rainfall falling over this period. A summer drought follows during which time the quality and quantity of feed available for livestock steadily declines, culminating in the "autumn feed gap". This feature of the farming system has important implications for the profitability of alternative feed sources (such as lucerne), in that the timing of feed supply can be just as important as the amount produced. Analytical techniqueThe analysis was conducted using the South Coast version of MIDAS. The acronym MIDAS stands for "Model of an Integrated Dryland Agricultural System". The MIDAS approach has been described in detail by several authors (e.g. Kingwell and Pannell 1987, Bathgate 1999). Briefly, MIDAS is a mathematical programming model that represents the technical, physical, biological and managerial aspects of broadacre livestock and crop production systems. Crops, crop stubbles, pastures, sheep, grain feeding, machinery and finance are all represented to a high level of detail. In addition, the model is strongly based on soil types and rotations, with different production figures for each rotation on each soil type. The South Coast MIDAS represents a farm of 2,500 hectares in the 400 - 500 mm rainfall zone of the South Coast. Several mixes of soil type are included in the model to allow for sub-regional differences. The soil mix used in this analysis represents a typical mix for the Esperance sandplain and is summarised in Table 1. Table 1. Summary of soil type mix assumed for the Esperance sandplain sub-region of the South Coast.
Representation of lucerne in MIDASLucerne is assumed to be sown in August and first grazed in November of the same year. From then on grazing is rotational with 6 week breaks, so as to ensure that overgrazing does not occur. The lucerne based pasture is assumed to be a mixed sward that includes a range of annual species (i.e. much the same mix of grasses and herbs as would be found in a sub-clover based pasture). Costs associated with lucerne are summarised in Table 2. Table 2. Costs of lucerne establishment, maintenance and removal
During the May - October growing season lucerne is assumed to grow at the same rate as annual pastures. From November to April there is no growth of annual pasture, although it remains available as a source of dry feed. By contrast, the lucerne continues to grow over the dry months, albeit at a reduced rate. Indicative annual pasture and lucerne growth rates are provided in Table 3 (note: actual growth rates represented in the model vary according to soil type and rotation). Table 3. Indicative growth rates for annual and lucerne based pastures (these figures are for the medium-depth duplex soil group).
Lucerne phases of two, three and four years are represented in the model. Lucerne is assumed to provide yield and nitrogen benefits to the first two years of crop coming out of the lucerne phase. Lucerne rotations included in the model are as follows:
These lucerne rotations are available on all soil groups except the saline soils. In addition the model includes continuous pasture, pasture - crop rotations, continuous crop rotations and green manure options. In total there are over 90 different rotational combinations available for each soil group. Lucerne is assumed to be removed in the spring of the year prior to cropping. Autumn removal just prior to crop seeding would be preferable from a grazing perspective, but is a risky strategy because of the difficulties of killing lucerne at a time when it is unlikely to be actively growing. Price assumptionsTable 4 lists the price assumptions for this analysis. These prices are based on a range of sources including ABARE, futures markets and forward contracts. They are intended to represent medium term estimates, and so may not directly correspond to prices received this year. Table 4. Price assumptions.
Results and discussionChanges in whole-farm strategy when lucerne is included in the systemPatterns of feed supply are altered markedly by the inclusion of lucerne in the farming system. This has important implications for the diet of livestock, particularly "out of season", i.e. November to April. Changes in the November - April diet composition selected by MIDAS are highlighted in Figure 1.
Figure 1. Impact of lucerne on diet composition over the November - April out of growing season period. By contrast, inclusion of lucerne in the system has minimal impact on the area of crop selected by MIDAS. However, important shifts in cropping rotation may be required to accommodate lucerne. These shifts can be summarised as follows:
An example of these changes in cropping rotation due to inclusion of lucerne is illustrated in Table 5. Lucerne has displaced crop on the medium-depth duplex and to compensate for this change there has been a shift in rotation on the deep sands, even though lucerne is not grown on this soil group. Table 5. Summary of enterprise mix by soil group with and without lucerne.
Impact of lucerne on whole-farm profitInclusion of lucerne in the farming system improved MIDAS whole farm profit, with the dollar value of lucerne being highly sensitive to several key assumptions. For example, under current wool and sheep prices the average value of each hectare of lucerne was approximately $30-40. Inclusion of prime lambs increased this figure by a further $10-20/ha, especially where lambs were carried over summer and sold in January. The majority of these benefits relate to savings on supplementary feed costs. This is because lucerne reduces the requirement for grain and hay feeding (see Figure 1). Importantly, gains from lucerne diminish as a greater area is sown. That is, each additional hectare sown is worth less than the previous hectare. Eventually a point will be reached where sowing additional lucerne actually reduces profit. This principal is demonstrated in Figure 2, where the marginal value of lucerne is graphed for scenarios with and without prime lamb production. The optimal area of lucerne is at the point where marginal value is $0, i.e. the point where there are no further gains to be had from increasing the area of lucerne.
Figure 2. Marginal value of lucerne with and without inclusion of prime lambs in the enterprise mix. In practice it is not so critical to precisely identify the "optimal" area of lucerne. However it is important to recognise that just because some lucerne is good, more will not necessarily be better. Reasons for the pattern of diminishing returns include:
Does lucerne improve the profitability of cropping?Cereals sown directly after a lucerne phase often show increases in yield and protein relative to cereals sown after annual pasture. For example, Latta et al. (2001) report trial results where wheat yield and protein after lucerne were 10% and 1% higher than wheat grown after annual pasture. Despite such impressive yield and protein benefits, results from this economic analysis suggest that the net impact of lucerne on the profitability of a farmer’s cropping programme will generally be small, sometimes nil, and occasionally negative. This is due to a combination of reasons. Firstly, the length of most lucerne rotations means that benefits to following crops can only be realised occasionally. For example, a one-off yield boost of 250 kg/ha (worth say $40) in an 8 year lucerne / crop rotation is actually only worth $5/ha when averaged out over the rotation. Secondly, the drying effect that lucerne has on the soil profile can actually cause yield decreases in following crops in situations where growing season rainfall is low (e.g. Latta and Devenish 2002). The reverse of this argument is that the drying effect of lucerne could be beneficial to following crops in very wet years due to reduced waterlogging, although realisation of this benefit would require that lucerne be sown into waterlogging prone areas. Finally, as shown in Table 5, the inclusion of lucerne will typically displace some crop, most probably on a soil type where crops grow particularly well. In order to compensate for this loss of crop area, more crop will be sown on soil types where crops may be less productive and less profitable. The relatively minor impact that cropping benefits have on the profitability of lucerne is emphasised in Figure 3. Even with a 25% yield boost in the first cereal after lucerne (relative to cereal after pasture), the average value of lucerne is only slightly increased. The change in optimal area of lucerne is likewise small.
Figure 3. Impact of yield boost to following cereal crops on the increase in profit from adopting lucerne. Lucerne, profit and groundwater rechargeOn any given farm the amount of recharge occurring across the landscape varies considerably according to soil type. The extent to which lucerne can be used to reduce recharge is therefore dependent on its profitability on high recharge soil types. Indicative recharge figures for the soil groups used in this analysis are also provided in Table 6. These recharge figures assume an average annual rainfall of 450 mm. Table 6. Indicative recharge figures under annual-based agriculture for each of the soil groups used in this analysis.
From Table 6 it is evident that for the Esperance sandplain recharge is quite high for all of the major soil groups. Therefore, in order for lucerne to have a significant impact on recharge it must compete profitably on each of these soil groups. This is a far more challenging proposition than farmers in many other regions will face; most other regions have a broader mix of soils and recharge rates across the landscape. Results from this analysis (see Table 5) suggest that lucerne is profitable to some extent on the medium depth duplex soil, but unlikely to compete on either the deep sand or waterlogging prone duplex. In the case of the deep sands, continuous cropping is more profitable than lucerne, while on the waterlogging prone duplex the growth of lucerne is insufficient to compete with annual pastures and cereals. Consequently, the prospects for reducing recharge on these parts of the landscape using lucerne are somewhat diminished. Improvements in the production and / or utilisation of lucerne on these soil groups will be needed before widespread adoption will be financially attractive to farmers. Sensitivity analysis provides clues as to the kinds of improvements that might make lucerne profitable across more of the landscape. Figure 4 presents results of sensitivity analysis examining the impact of flock type and lucerne growth rates on the extent to which lucerne can be used to profitably reduce recharge. The "improved lucerne" shown in Figure 4 represents a hypothetical case where lucerne is equally productive across all of the non-saline soil types, and so is better able to compete with current land uses on deep sands and waterlogging prone duplexes.
Figure 4. Trade-off between recharge reduction using lucerne and whole farm profit for a range of scenarios. The results in Figure 4 further highlight how inclusion of prime lambs in the farming system is likely to improve the profitability of lucerne, and enhance the prospects for reducing recharge. Additional improvements in profitability and recharge reduction will be realised through the development of lucerne varieties and / or management packages that are better able to compete with existing enterprises on the deep sands and waterlogging prone duplex soil groups. AcknowledgementsThe input of staff from the Esperance office of the Department of Agriculture is gratefully acknowledged, particularly Jeremy Lemon, Anita Lyons and David Hall. ReferencesBathgate, A.D., 1999, Whole farm model to optimise profit on South Coast farms, Final Report for the Grains Research & Development Corporation, Department of Agriculture, Western Australia. Bathgate, A. & Pannell, D.J., 2002, Economics of deep-rooted perennials in Western Australia, Agricultural Water Management, vol. 53, pp. 117-132. Kingwell, R.S. & Pannell, D.J. (eds), 1987, MIDAS - A bioeconomic model of a dryland farm system, Pudoc, Wageningen. Latta, R., Blacklow, L., Lyons, A., Matthews, C., Bailey, T. & Rose, I., 2001, Lucerne establishment and production package, In: Crop Updates 2001 - Farming Systems for Sustainability, Department of Agriculture, Western Australia, pp. 27-28. Latta, R., 2002, Sheep production on lucerne, Agribusiness Decision, vol. 32, no. 7, pp. 8-10. Latta, R. & Devenish, K., 2002, Perennial pastures in annual cropping systems: lucerne and beyond, In: Crop Updates 2002 - Farming Systems for Sustainability, Department of Agriculture, Western Australia, pp. 3-4. *** Citation: O'Connell, M. (2003). Economic evaluation of phase farming with lucerne on the Esperance sandplain. Paper presented at the 14th International Farm Management Congress, Perth, Western Australia, 10th to 15th August 2003. |
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© Copyright CRC for Plant-based Management of Dryland Salinity 2003 |
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