Sandplain soils on the south coast of Western Australia have multiple limitations to crop production that include water repellence, low water and nutrient retention, subsoil acidity, and high soil strength. Crops on sandplain soils achieve, on average, almost 85% of their rainfall-limited yield potential; however, where there are multiple limitations the corresponding value is often <50% in any given year. Previous research has shown the value of applying clay-rich subsoil ('claying') to ameliorate water repellent soils and improve nutrient retention. Other studies have shown that deep ripping is effective in reducing compaction in sandplain soils. This paper quantifies the effects of 5 subsoil clay rates (0, 50, 100, 200, and 300 t/ha), with and without deep ripping to 0.5m, on soil properties, crop growth, and profitability in a replicated field experiment.Crop yields were increased by 0.3-0.6 t/ha as result of added clay. The clay content of the surface soil required to alleviate water repellence and achieve the highest yield increases was 3-6% in soils with~1% organic carbon. Longer term effects of claying included increased soil organic carbon by 0.2%, pH by 0.6 units, potassium by 47 mg/kg, soil strength by 250 kPa, and cation exchange capacity by 1.3 cmol c /kg to a depth of 0.1 m. However, changes in plant-available water (mm/m) were inconsistent between the clay treatments. Deep ripping to 0.5 m increased crop yields by 0.1-0.5 t/ha. These crop yield responses were still evident 3 years after the ripping treatment had been applied. Soil strength measurements indicate that re-compaction of the ripped treatments had occurred to a depth of 0.2 m in the second year following ripping. Crop responses to claying and deep ripping were additive. Claying and deep ripping, while almost doubling yields, achieved only 50-70% of the rainfall-limited yield potential on these marginally fertile soils. The highest clay rates (>3-6%) had cumulative discounted cash returns $AU100-200/ha higher than the unclayed 'control' treatment and $300/ha higher than the lowest clay rates. For most of the clay treatments, deep ripping increased discounted returns between 2005 and 2007 by $80-120/ha.

Abstract. Mallee-based agroforestry has potential to provide farmers with new income sources derived from biofuels, biofeedstocks, and carbon sequestration. Although mallees are planted on >12 700 ha across the south-west of Western Australia, very little commercial harvesting of mallee has occurred to date. The development of biomass processing industries is constrained by lack of robust information regarding the productivity of integrated mallee and agricultural systems. This study addresses this constraint by quantifying the productivity and economics of agricultural crops and pastures growing in the competition zone adjacent to mallee belts at 15 sites across the Western Australian wheatbelt. The sites covered a range of climate and edaphic conditions, three mallee species (Eucalyptus polybractea R Baker, E. loxophleba ssp. lissophloia LAS Johnson and KD Hill, or E. kochii ssp. plenissima (CA Gardner) Brooker), various crop and pasture rotations, and various mallee harvest-management treatments.Mallee-crop competition was negatively correlated with rainfall and positively correlated with mallee age and size, and greater for crops than pasture. Consequently, extent and magnitude of competition were highly variable across sites and years. On average, mallee-crop competition extended 11.3 m from unharvested belts and reduced crop and pasture yields by 36% within 2-20 m of the mallee belts relative to open paddock yields. This is similar to what has been reported for taller tree species. Harvesting mallees reduced competition such that crop and pasture yield was reduced by 22 or 27% relative to open paddock yields for mallees harvested at 3-or 6+-year intervals, respectively.The economic cost of mallee-crop competition on agricultural enterprises was also highly variable between sites, and between years within individual sites. Averaged across all site-years, the opportunity cost of competition was equivalent to forgoing agricultural production for 14.4 m on each side of unharvested mallee belts, or 9-10 m on each side of harvested belts.Farmers with mallee agroforestry systems will need to manage the economic impacts of competition by reducing agricultural input costs in the competition zone, timing crop-grazing rotations with mallee harvests, ensuring that the width of alleys is at least 25 times the height of the mature trees, and possibly root-pruning mallees in unharvested or long harvest interval systems.This research has shown that mallee-crop competition presents a significant cost to farmers and must be considered when designing mallee agroforestry systems. The findings have relevance for the development of appropriate biomass and carbon sequestration pricing benchmarks for mallee plantings.

Windbreaks in the south-eastern coastal region of Western Australia are generally established to protect agricultural land against damage from wind erosion. However, to date there has been no detailed economic analysis of establishing windbreaks on farms in the region. Accordingly, a decision model was developed to estimate benefits and costs of windbreaks as determined by production inputs and outputs, windbreak system design, frequency and severity of wind damage, and commercial tree products from the windbreak. The model used crop yield responses to shelter at sites across the medium–low rainfall agricultural areas of southern Western Australia. The model lends itself to further development as a risk analysis tool incorporating probabilities and empirical measurements of wind damage. A benefit:cost analysis, using a partial budget approach, compared situations with and without windbreaks. The model showed that windbreaks improved profitability when they reduced the severity of wind damage to crops. Without wind erosion events, windbreaks had a negative impact on farm profit. Investment in windbreaks is therefore a form of insurance. The relative level of benefits is determined by the frequency of wind damage, severity of damage, distance between windbreaks, pruning of lateral tree roots and the possibility of using trees that can produce commercial timber products.

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