DairyNZ Economics Group

Slides:



Advertisements
Similar presentations
Environmental Impacts of dairying in Canterbury Ross Redpath Royal society teacher fellow 2003.
Advertisements

The impact of projected climate change on Monaro farms. Doug Alcock Livestock Officer (Sheep and Wool) Climate Change Adaptation in Southern Australian.
The Impact of Achieving Targets set out in Food Harvest 2020 on Nitrogen and Phosphorus Usage Noel Culleton.
Nutrient Management Subtitle. Burning Issues Nutrient Management2.
Competitive Position of the Tasmanian Dairy Industry -Farmers Key to Success- David Beca – Red Sky Agricultural Pty Ltd.
Dairy Farming.
Irish Dairying – A Competitive Industry? Fiona Thorne & Billy Fingleton Teagasc Glanbia Regional Seminars 2006.
Evaluation of Economic, Land Use, and Land Use Emission Impacts of Substituting Non-GMO Crops for GMO in the US Farzad Taheripour Harry Mahaffey Wallace.
OVERSEER® Nutrient Management Tool: Present and future perspectives Waikato Regional Council Presentation 25 October 2012 Philip Mladenov Chief Executive.
2008 Tasmanian Dairy Conference Burnie, 8 th October 2008 South Island (NZ) Dairy Industry Development Richard Christie – Executive Director, South Island.
The NFU champions British farming and provides professional representation and services to its farmer and grower members Fair price for product Sian Davies.
-Advocates for continual growth of agriculture in New Zealand. -E.g. Andy West; double current milk solids(MS) production and $3 Billion more lamb production.
Rural Economy Research Centre AESI Student Day 05/11/2009 Examining the relationship between production costs and managerial ability P. Smyth 1, 2, L.
Reducing footprint while maintaining profit Pierre Beukes, Kevin Macdonald, Chris Glassey.
1 3. Cost effective feeding systems ANIM 3028 Tom Cowan Tropical Dairy Research Centre, UQ, Gatton.
Economic Impacts of GHG and Nutrient Reduction Policies in New Zealand Adam Daigneault Landcare Research Motu Climate Economics Research Workshop Wellington.
Salinity and Bulk Water Workshop 27 October 2010 Werribee Irrigation District.
Planning Certainty A challenge for Investment April 2014 Tom Chesson – CEO Australian national Irrigators Council Murray Smith – Principal Engineer, Agriculture.
A Spatial Analysis of the Beef Supply Response in Scotland Cesar Revoredo-Giha Montserrat Costa-Font Philip Leat SRUC-Food Marketing Research 150th EAAE.
Leading the way in Agriculture and Rural Research, Education and Consulting The impacts of CAP reform on Scottish farms Shailesh Shrestha, Bouda Vosough.
Dr Bill Cotching Tasmanian Institute of Agricultural Research Managing our Land and Water Resources A research perspective.
Whole farm systems analysis of greenhouse gas emission abatement strategies for dairy farms Richard Rawnsley, Karen Christie, and Rob Kildare.
Leading the way in Agriculture and Rural Research, Education and Consulting Environmental and Financial Implications of CAP 2015 reforms on Scottish Dairy.
Flux investigations for intensive dairy farming, Hamilton Basin, NZ Dave Campbell, Louis Schipper, Paul Mudge & Tehani Kuske Earth and Ocean Sciences University.
‘Reducing Barriers to Change’ Theresa Wilson DairyNZ Sustainability Team Leader.
Lessons learnt from the dairying Accounting for Nutrients project Warwick Dougherty.
2015 NSW Dairy Farm Monitor Project Camden, 2 nd Mar 2016 Kerry Kempton – Technical Specialist Dairy Peter Havrlant – Development Officer Dairy NSW DPI.
NZIF Conference –Exploring the changing regulatory and market environments. Taking opportunities in sensitive catchments Mike Barton Mike Barton 31st August.
Technical Alliance Technical Leaders Group and Technical Support Group
Summary of Pilot Study for Upper Waikato in the Joint Venture project
EGS-AGU-EUG Joint Assembly Nice, France, 10th April 2003
Biomes of the World.
Biomes of the World.
Agricultural Systems and Food Production
Biomes of the World.
Reducing sediment & nutrient losses from intensive agriculture Restoring eutrophic shallow lakes Pastoral agriculture is the dominant land use in New.
The cost of reducing nutrient loss from agriculture
Problems and solutions
Economic Joint Venture model: summary of progress
The Netherlands: manure policy and request for a derogation to the livestock manure limit of 170 kg N/ha per year for dr. ir. Cindy.
Sources of contaminants in the Waikato-Waipa catchment
Klamath ADR Hydrology Report
Environmental and Natural Resource Economics 3rd ed. Jonathan M
Prioritising soil conservation and water quality issues for the Waikato River and Waipā River Restoration Strategy, New Zealand. Reece Hill1,2, Dan Borman1,2.
The Influential Environment
N - Efficiency Results Katherine Cherry.
Interactions between the phosphorus content of animal manures
Economic model for the Healthy Rivers process
Dairy Farming in New Zealand
Global Livestock Development with Special Focus on Latin America
Greenhouse Gas Emissions Data
Biomes of the World.
Prioritising soil conservation and water quality issues for the Waikato River and Waipā River Restoration Strategy, New Zealand. Reece Hill1,2, Dan Borman1,2.
Backtrack Dairies.
Biomes of the World.
Biomes of the World.
Synergies between agricultural nitrogen and greenhouse gas regulation
Agricultural production in Finland up to 2020
Biomes of the World.
Sheep and Beef data Project Team Femi Olubode (WRC) Blair Keenan (WRC)
Biomes of the World.
Biomes of the World.
Chapter 21 Biomes of the World
Biomes of the World.
Biomes of the World.
What is a biome? A BIOME is the largest geographic biotic unit, a major community of plants and animals with similar life forms and environmental conditions.
Topic A: The use of stream/ground water for irrigation
Why do different organisms live in different places?
Biomes of the World.
Hamilton City – population 150,000
Presentation transcript:

DairyNZ Economics Group Farm level data DairyNZ Economics Group

Objective Determine the economic impact of reducing N loss on dairy farms in the Waikato River Catchment Create abatement cost curves – for the Waikato catchment model

Overview of methodology Collection of Baseline data Select farms for modelling - representation Identify mitigations and assumptions Farmax and Overseer modelling Checking and interpretation of results Write up

Waipa Franklin Sub Regions North of Hamilton and West of State Highway 1 has relatively higher rainfall than East of State Highway 1. Soils tend to be moderately well drained in this area with some poorly drained soils. Much of the moderately well drained soils are hilly and more likely to be occupied by sheep, beef or forestry. North of Te Kauwhata and East of State Highway 1 relatively lower average rainfall is found with a tendency towards summer dry periods. Soils are predominately poorly or less well-drained. Lower relative rainfall is found South of Te Kauwhata and East of Hamilton, however the soils become very poorly drained in parts (as distinct to sub catchment 2). The sub region between Hamilton to Cambridge has mostly well drained soils and relatively low rainfall persists (compared to West of Hamilton/State Highway 1). The largest sub region stretches from Cambridge in the North to the bottom of the catchment excluding the area around Pirongia, Ohaupo and Te Awamutu. This area is characterised by relatively higher rainfall, with a mixture of both well drained and poorly drained soils. The wettest sub region is found around Mt Pirongia, Ohaupo and Te Awamutu with a range of soil types and drainage in the area.

Upper Waikato Sub Regions This sub region includes an area with relatively low proportions of dairying land; it includes the township of Taupo and the area along the Napier Taupo Road that falls within the Upper Waikato River catchment. It has moderate rainfall and well drained soils. This sub region includes the area of lower rainfall that runs between Taupo and Reporoa along State Highway Five, it encompasses some well drained soils, but also some poorly drained soils around Reporoa. In the Upper Waikato area, this is the largest grouping of poorly drained soils. Farms around Reporoa are often smaller in size but slightly more intensively farmed than farms in sub catchments 1 or 4. This area encompasses the majority of the moderate to low nitrogen leaching vulnerability in the Upper Waikato area. Sub region 3 is the area in the North of the Upper Waikato catchment boundary. Please note that it does not include some of the area around Cambridge that was put into the Waipa Franklin study due to timing (see Section 1.1). This area has lower rainfall than sub catchment 4 and includes some less well drained soils; it therefore has a lower nitrogen leaching vulnerability than sub catchment 4. This sub region encompasses the majority of the Upper Waikato catchment both in total land area and dairy farm area. It has higher rainfall than the other three sub catchments and is dominated by very well drained pumice soils. It has a high nitrogen leaching vulnerability. It includes a range of dairy farm types from newer large scale, but lower intensity, forestry conversions, to older, smaller more intensive farms around Tokoroa.

Waipa-Franklin Farms Group Representation of sub-catchment Comments Percentage of sub region Hectares represented System 1 Farm 2 60% 17,175 Low Farm 2 well-draining soil. Farm 6 poor draining soil. Farm 6 40% 11,450 Medium 2 Farm 1 100% 21,116   High Farm on less well draining soil. Farm typical scale for area. 3 Farm 3 20% 7,786 Farm 3 is on well-drained soils which are less typical for the catchments. Farm 4 is on poorly drained soils. Farm 5 is on poor draining peat. Farm 4 30% 11,679 Farm 5 50% 19,465 4 Farm 9 19,966 Farms 4 and 20 balance each other in scale for the sub catchments. Farm 10 19,996 5 Farm 11 76,478 Range of soil types for the four farms. Farm 12 is weighted lower than the others due to higher stocking rate and irrigation (minority of farms irrigated). Farm 12 10% 25,493 Farm 13 Farm 14 6 Farm 7 70% 54,222 Farm 7 well-draining soil, Farm 8 poorly drained. Farm 8 23,238

Upper Waikato Farms Group Representation of sub-catchment Comments Percentage of sub region Hectares represented System 1 Farm 4 100% 3,364 Low Typical large scale farm for this area on well drained soils 2 Farm 10 30% 6,359 Medium Farm 10 is on well drained soils while farms 11 and 12 on less well drained soils. Farm 12 is higher input and more intensive than farm 11, who is typical for the area. Farm 11 40% 8,479 Farm 12 3 Farm 1 75% 9,636 Farm 1 is fairly typical of this small area. Farm 9 represents the small proportion of farms with some irrigation use. Farm 9 25% 3,212 4 Farm 5 20% 17,861 All farms are on similar pumice soils in this area. Farm 5 is a well run farm in the area but not the top producer. Farm 7 is typical of new conversions on more marginal land. Farm 6 has typical production for the smaller scale older farms around Tokoroa. Farm 3 is a larger scale farm with typical production. Farms 8 and 2 balance each other in terms of production and inputs. Farm 8 is lower input and production. Farm 7 High Farm 6 Farm 2 13% 11,163 Farm 3 Farm 8 15% 13,395

Representative farms Assign a weighting to each farm consultation with local Consulting Officers Upper Waikato Waipa-Franklin

Base N leaching Waipa-Franklin

Base N leaching Upper Waikato

N Mitigations Optimise feed pad / standoff pad N fertiliser – timing, applications, volume Reduce Imported supplements (up to 20%) Reduce stocking rate (up to 20%) Introduce standoff pad

Assumptions Milking platform only $6.50 milk price Standardised feed and fertiliser prices Labour fixed, unless 100+ cows removed Size of effluent area not increased Concrete standoff pad with bark - cows not fed on pad

Impacts – Waipa-Franklin

Impacts – Upper Waikato

Waipa-Franklin Composite Farm

Conclusion 26 farms modelled across 2 catchments Higher N leaching in Upper Waikato 10-20% reduction in N loss, smaller impact on profit 20%+ reduction in N loss - larger impacts on production and profit requiring more change on-farm with different management skill level