Department of Agroecology Danish Institute of Agricultural Sciences Dynamic NH 3 model EMEP atmospheric dispersion model. Deposition estimates used in.

Slides:

Advertisements

Similar presentations

Project and Workshop on inventories and projections of GHG and NH 3 emissions from agriculture in Central and Eastern Europe Ispra, Juni 2005 National.

Advertisements

MITERRA-EUROPE Assessment of nitrogen flows in agriculture of EU-27

JRC-AL – Expert Meeting on Cat.4D reporting – 21/ Nitrogen Balance in the IPCC guidelines and Good Practice Guidance and in European National.

JRC – Brussels on Workshop in GHG and NH3 emission inventories and projections Inventories - recommendations.

Daily Manure Production Per Animal We have estimates of manure production –4.5 kg/day/hd for swine (liquid manure) –45-50 kg/day/hd for dairy cow (liquid)

A. What is it? B. Why is it important? C. How is it done?

Managing Ammonia in Agriculture USDA Research Efforts.

Ammonia Volatilization from Wet Animal Manures C.W. Wood, J.J. Meisinger, P.A. Moore, Jr., and R.B. Thompson Auburn University, USDA-ARS, Beltsville, MD.

Monitoring Air Quality: Emissions and Odor From A Swine Finishing Livestock Facility.

Environmetal problems related to manure management Greenhouse gas emission from manure stores.

INVENTORIES OF CH 4, N 2 O and NH 3 FROM UK AGRICULTURE Tom Misselbrook, Lorna Brown IGER, North Wyke.

Setting Acceptable Odor Criteria Using Steady-state and Variable Weather Data Z. Yu 1, H. Guo 2, C. Lague 3 1.Division of Environmental Engineering, University.

Greenhouse gas emission scenarios for agriculture in Finland UNFCCC Workshop on Emissions Projections from Annex I Parties, , Wissenschaftszentrum,

Danish GHG and ammonia emissions

The Agriculture and Nature Panel Report Ispra 3 1 Ulrich Dämmgen and Nick Hutchings UN ECE Task Force on Emission Inventories and Projections, Agriculture.

Integrated Assessment Modeling, cost-effectiveness, and agricultural projections in the RAINS model Zbigniew Klimont International Institute for Applied.

Department of Agroecology Danish Institute of Agricultural Sciences Emission measurement database.

Section 4 - Manure Production Colorado CNMP Workshop Manure & Wastewater Production Prepared by J.E. Andrews, PE, NRCS - Lakewood, CO.

Ministry of Food Agriculture and Fisheries Danish Institute of Agricultural Sciences Options for reducing the greenhouse gas emissions from agriculture.

AGRICULTURE and POLLUTION. Nitrogen and Agriculture The nitrogen cycle: Atmospheric deposition, Biological fixation, Fertilisers, Animal manures Nitrogen.

1 Introduction, reporting requirements, workshop objectives Workshop on greenhouse gas and ammonia emission inventories and projections from agriculture.

Environmental Systems Analysis National Inventories of Methane and Nitrous Oxide Emissions from Agriculture in the Netherlands Carolien Kroeze, André van.

Box 1 CO 2 mitigation potential of managed grassland: An example Franzluebbers et al. (2000; Soil Biol. Biochem. 32: ) quantified C sequestration.

Update of COGAP and adoption by signatory states J Webb.

Nutrient Budgets For CNMPs Nutrient Management Planners Training March 31, 2009 Bobby Smith County Extension Coordinator UGA Cooperative Extension Morgan.

N-flow in Danish agriculture And FarmAC in Amazonas Ib Sillebak Kristensen & Nick Hutchings Aarhus University Dept. of Agroecology Foulum. Denmark 10.

Ammonia emissions from UK agriculture – the NARSES model TFEIP Workshop, Thessaloniki, Greece, October 2006 Tom Misselbrook IGER, North Wyke, UK.

Building A Better Ammonia Inventory Mark Janssen – LADCO/Midwest RPO.

Emissions of CH4 and N2O from Agriculture in Ireland Michael McGettigan, Environmental Protection Agency.

AARHUS UNIVERSITY Agriculture and Nature Expert Panel Report to plenum Nick Hutchings 1 Milan, 11 May 2015.

TATION AARHUS UNIVERSITY Agriculture and Nature Panel Stockholm 2011 Nick Hutchings, Barbara Amon and Rainer Steinbrecher 1.

Malé Declaration 1 ST emissions inventory workshop AIT, Bangkok, 3rd – 5th July 2006 Part 6 – Compilation of emissions from Agriculture (Sector 8) Harry.

Agricultural BMPs to Reduce N Emissions Jessica G. Davis Colorado State University.

Modeling experience of non- point pollution: CREAMS (R. Tumas) EPIC (A. Povilaitis and R.Tumas SWRRBWQ (A. Dumbrauskas and R. Tumas) AGNPS (Sileika and.

University of Natural Resources and Applied Life Sciences, Vienna Department of Sustainable Agricultural Systems I Division of Agricultural Engineering.

Ministry of Food, Agriculture and Fisheries Danish Institute of Agricultural Sciences Environmental aspects of using animal manure as an energy source.

BROUGHT TO YOU BY: BUILDING ENVIRONMENTAL LEADERS IN ANIMAL AGRICULTURE WELCOME TO MANURE MANAGEMENT JEOPARDY! Sections 2 and 3 Nutrient Management Regulations.

TATION AARHUS UNIVERSITY Agriculture and Nature Panel Istanbul 2013 Nick Hutchings, Barbara Amon and Rainer Steinbrecher 1.

Gaseous Emissions from Irish Agriculture Trevor Donnellan FAPRI-Ireland Partnership Teagasc Dublin.

AMMONIA EMISSION PREDICTIONS AND ABATEMENT – ISSUES FOR POLAND Tadeusz Kuczynski 1, Barbara Gworek 2, Andrzej Myczko 3 1-University of Zielona Gora, 2-

Sustainable Air Quality ME 449 Jan 14, 16; The Earth System Atmosphere –Conveyer of mass, moves mass source to receptor –Small storage capacity.

Ongoing improvements in the modelling of agricultural emissions Zbigniew Klimont, Willem Asman International Institute for Applied Systems Analysis (IIASA)

Air Quality Governance in the ENPI East Countries Training on emission inventories The EMEP/EEA Guidebook Agriculture December, 2013, Tbilisi, Georgia.

Updating Chapter of the Atmospheric Emission Inventory Guidebook Ulrich Dämmgen 1 and Nicholas John Hutchings 2 UN ECE Task Force on Emission Inventories.

N.Kozlova, N. Maximov North-West Research Institute of Agricultural Engineering and Electrification (SZNIIMESH) Saint-Petersburg, Russia PRAGUE 26 … 28.

Ministry of Food, Agriculture and Fisheris Danish Institute of Agricultural Sciences Simulation of nitrate leaching from an organic dairy crop rotation.

DIAS INFORMATION DAY GLOBAL WATER RESOURCES AND ENVIRONMENTAL CHANGE Date: 09/07/2004 Research ideas by The Danish Institute of Agricultural Sciences (DIAS)

Nutrient Management Planning CNMP Core Curriculum Section 4 – Nutrient Management.

Waste Characteristics and Volumes CNMP Core Curriculum Section 3 – Manure and Wastewater Storage and Handling.

Manure Storage Systems and Structures Determining environmental impacts of manure storage and storage systems on the farmstead. Joesph Kelpinski, MAEAP.

Marginal costs of reducing nitrogen losses to water and air in Denmark Senior Researcher Brian H. Jacobsen Institute of Food and Resource Economics University.

Eurostat activities concerning regional nutrient balances.

Reducing Ammonia Emissions in Europe – with focus on Denmark Senior Researcher Brian H. Jacobsen Institute of Food and Resource Economics University of.

Workshop on the Criteria to establish projections scenarios Sectoral projection guidance: Agriculture Mario Contaldi, TASK-GHG Ankara, March 2016.

Phosphorus Management for Sustainable Dairy Production International Conference: Steps to Sustainable Livestock John Bailey Sustainable Agri-Food Sciences.

Norwegian Meteorological Institute

Harmonisation with IPCC

Overview of existing excretion factors

Excretion – Anne Miek Kremer

Methodological studies in the field of Agro-Environmental Indicators

Nutrient balance for nitrogen TAPAS action – Statistics Belgium in collaboration with the Institute for Agriculture and Fisheries Research 11 June 2009.

Ammonia emissions from manure management

Workshop 28th March 2014, EUROSTAT, Luxembourg

Nitrogen and phosphorus excretion factors for livestock

N and P balances in Denmark on national and regional scale

Task 4 Hans Kros Alterra Workshop ‘Excretion factors’

Excretion factors Task 2: In-depth analysis of methodologies for calculation and presentation Léon Šebek, 28 March 2014.

The Agriculture and Nature Panel Report

Screens: 35% of mass transferred to solid phase 35% P and 30% N in solid phase Simple screens and filter-bands produce a solid phase with a very high.

Other Topics – Anne Miek Kremer

Presentation transcript:

Department of Agroecology Danish Institute of Agricultural Sciences Dynamic NH 3 model EMEP atmospheric dispersion model. Deposition estimates used in policymaking Needs emission estimates –Europe-wide (50 x 50 km grid). –High temporal resolution (3 hours). Work in progress.

Department of Agroecology Danish Institute of Agricultural Sciences Sources: –Housing. –Storage. –Field. The model Storage Field Animal housing Animal Mass flow model: –Ammoniacal N. –Organic N. –Dry matter. –Water. Hourly timestep

Department of Agroecology Danish Institute of Agricultural Sciences NH 4 + Organic-NH2OH2O NH 3 H2OH2O Manure Animal housing Manure storage

Department of Agroecology Danish Institute of Agricultural Sciences NH 4 + Organic-NH2OH2O NH 3 NH 4 + H2OH2O H2OH2O Manure Soil Field application

Department of Agroecology Danish Institute of Agricultural Sciences NH 3 emission Area of manure * Amount of NH 4 + * Henry-factor Amount of water * Transport resistance

Department of Agroecology Danish Institute of Agricultural Sciences Animal house emission Area of manure * Amount of NH 4 + * Henry-factor. Amount of water * Transport resistance Number of animals Floor area per animal Number of animals Urea-N per animal Temperature Manure pH Number of animals Volume per animal Ventilation rate Housing factor

Department of Agroecology Danish Institute of Agricultural Sciences Animal house emission Area of manure * Amount of NH 4 + * Henry-factor. Amount of water * Transport resistance Number of animals Floor area per animal Number of animals Urea-N per animal Temperature Manure pH Number of animals Volume per animal Ventilation rate Housing factor = parameter

Department of Agroecology Danish Institute of Agricultural Sciences Lots of data. Parameterisation & testing Lots of time. (see presentation on later today). Temporary parameterisation using Dk emissions. Synthetic weather data.

Department of Agroecology Danish Institute of Agricultural Sciences finishing pigs per 50 x 50km Ammonia emission (kg/day)

Department of Agroecology Danish Institute of Agricultural Sciences Meteorological e.g. –Daily temperature, rainfall, wind speed etc. Structural (vary with location) e.g. –Number of animals. –Type of animal housing. Operational (vary with time & location) e.g. –Housing dates and ventilation rates. –Manure application dates. Inputs  

Department of Agroecology Danish Institute of Agricultural Sciences Structural input examples For each animal type: –Animal numbers. –Ammoniacal-N and organic N excreted per animal. –Housing/storage type. Dairy cattle.

Department of Agroecology Danish Institute of Agricultural Sciences Animal numbers EUROSTAT Farm Structural Survey: –Animal numbers by type. –Regularly updated. Some data missing. NitroEurope project

Department of Agroecology Danish Institute of Agricultural Sciences Dairy cattle

Department of Agroecology Danish Institute of Agricultural Sciences Nitrogen excretion Use IPCC methodology: Feed intake, faecal dry matter production. Data: Milk production per cow (FSS). Assumptions: Diet quality, growth, weight.

Department of Agroecology Danish Institute of Agricultural Sciences

Department of Agroecology Danish Institute of Agricultural Sciences

Department of Agroecology Danish Institute of Agricultural Sciences Manure type Housing type depends on farm size? Small volumes – solid manure cheapest. Large volumes – slurry cheapest. Relate probability of slurry to farm size. Use farm size (FSS) to estimate slurry/solid. Example from Denmark

Department of Agroecology Danish Institute of Agricultural Sciences

Department of Agroecology Danish Institute of Agricultural Sciences Simple dynamic model. Estimate livestock heat production. –CIGAR (2002) Calculate ventilation necessary to maintain: –A target inside temperature (forced ventilation). Maximum and minimum ventilation rates. Heating. –Inside temperature 4C above ambient (free). Operational example - ventilation

Department of Agroecology Danish Institute of Agricultural Sciences Forced ventilation

Department of Agroecology Danish Institute of Agricultural Sciences Lack harmonised data at European scale. –But may be available at country scale. Operational management affected by legislation. Modelling –How accurate? –Useful for scenarios. Conclusions (1)

Department of Agroecology Danish Institute of Agricultural Sciences Data required for many purposes. –Ammonia, Greenhouse gasses, Nitrate leaching, Erosion. –Secondary PM formation. EU project. –Data collection. –Modelling. Conclusions (2)

Department of Agroecology Danish Institute of Agricultural Sciences

Department of Agroecology Danish Institute of Agricultural Sciences Depth of storage. Parameters - storage Manure pH and temperature. Organic N degradation coefficient. Transport resistance.

Department of Agroecology Danish Institute of Agricultural Sciences Start/stop date for applications Parameters - field Maximum application capacity. Application rate. Transport resistance constant. Infiltration rate. Duration of emission.

Department of Agroecology Danish Institute of Agricultural Sciences

Department of Agroecology Danish Institute of Agricultural Sciences Dirty floor area per animal. Animal housing Manure pH and temperature. Transport resistance.