Improving the economic and environmental performance of a New Zealand hill country pastoral catchment M.B. Dodd, M.E. Wedderburn, T.G. Parminter AgResearch,

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Presentation transcript:

Improving the economic and environmental performance of a New Zealand hill country pastoral catchment M.B. Dodd, M.E. Wedderburn, T.G. Parminter AgResearch, Ruakura Research Centre, Private Bag 3123, Hamilton, New Zealand B.S. Thorrold Dexcel, New Zealand J.M. Quinn National Institute of Water and Atmospheric Research, New Zealand mike.dodd@agresearch.co.nz Context hill country pastoralism Objective Low altitude steeplands Moist-temperate climate Moderately intensive pastoralism (sheep/beef) Landscape prone to erosion and weed reversion High density stream network Volatile commodity prices Environmental compliance pressure Declining rural labour force To conduct a multi-stakeholder, participatory action research project to achieve a “well managed rural hill land farm system” in the context of stakeholder-defined goals Viable businesses Ecosystem health Protected landscape values Active partnerships Demonstrable environmental performance Adequate rural services and infrastructure Stakeholder group Farmers Foresters Local government Regional government Agricultural scientists Environmental scientists Conservationists Maori Indicator data table Indicator Old System Benckmark value New system Soil fertility (Olsen phosphate) 17 25 23 Pasture production (t DM/ha/y) 9.5 12.1 10.0 Sediment export (t/ha/y) 2.86 0.44 0.69 Phosphorus export (kg/ha/y) 3.0 0.8 1.2 Indigenous plant diversity (# spp per plot) 20 34 28 Lambing (% weaned) 109 120 124 Cattle gross margin ($/stock unit) 46 58 82 Annual farm surplus ($/ha grazed) 181 253 285 Process three loops of the learning cycle Results from each phase Phase 1 The existing system was failing to meet stakeholder goals from both economic and environmental perspectives (see indicator data table) Why? A high proportion of erodible land with low pasture productivity, high maintenance costs (fertiliser, fencing, weed control), poor animal performance, low profitability, poor water quality, low diversity of aquatic faunal and terrestrial indigenous plant communities. Phase 2 Research models (agroforestry, farm systems, catchment flow) predicted improvements in most economic and environmental indicators resulting from a range of altered stock policy and tree-planting options. Phase 3 As a result of the land use and management changes, over 5 years there were improvements in a number of indicators: soil fertility, pasture production, animal performance, sediment loss, plant diversity, enterprise profitability (see indicator data table) Setting goals and indicators Assemble stakeholder group Awareness Phase 1 Collect indicator data on existing system and benchmarks Reflect on the status of the current system Apply research models Land use change implemented in phase 3 Identify management options Compile and align output data from several research models Forecasting Phase 2 Pinus radiata afforestation of pasture on steeper land Changes in stock policy to high fecundity ewe flock and bull beef system Riparian protection by fencing and/or tree planting Indigenous forest fragment restoration Spaced-planting poplars for erosion control in pasture Reflect on the potential for management change Apply land use change Design new land use plan Collect indicator data on outcomes Implementation Phase 3 Reflect on the outcomes relative to original goals Conclusions The participatory process achieved a facilitated consensus on appropriate goals, indicators and planning of land use change Land use change did improve economic and environmental indicators towards stakeholder goals Rates of change for some indicators were different from expectations Implementation costs were high relative to immediate returns We gratefully acknowledge these supporting agencies: