Denis Choinière, ing. M.Sc. Environmental Division Consumaj inc. Consumaj.

Slides:



Advertisements
Similar presentations
Direction générale de lAviation civile Ministère de l'Écologie, du Développement durable, des Transports et du Logement Direction des Services de la Navigation.
Advertisements

André Vézina, ITA campus La Pocatière Economic analysis of different models of shelterbelts used to protect hog barns André Vézina, forest engineer, M.
Benefits of Installing Shelterbelts April 2006
Task Force on National Greenhouse Gas Inventories Revisiting the Use of Managed Land as a Proxy for Estimating National Anthropogenic Emissions and Removals.
PROJECT CLIMEPORT Mediterranean Port’s Contribution to Climate Change Mitigation ANTONIO CEJALVO Director Agencia Valenciana de la Energía (AVEN) Projet.
Reduce soil erosion from wind Provide noise screens Protect plants from wind-related damage Provide visual screens Alter microenvironment for enhancing.
Introduction to Windbreaks This training was prepared by the U.S. Department of Agriculture (USDA) team of Otto Gonzalez-USDA Foreign Agricultural Service.
Odour emission from livestock housing Assoc Prof. PhD. BUI XUAN AN Mobil
Managing Ammonia in Agriculture USDA Research Efforts.
Dale T Littlejohn Senior Geologist. What is fate and transport in the vadose zone? Vadose Zone Hydrocarbon release from buried pipeline Aquifer Surface.
André Vézina, ITA, La Pocatière Campus Shelterbelt Efficiency Criteria April 2006.
Monitoring Air Quality: Emissions and Odor From A Swine Finishing Livestock Facility.
Environmetal problems related to manure management Greenhouse gas emission from manure stores.
Emissions from Animal Production Systems John W. Worley.
Logo Module 4: Air Quality Around Production Facilities and Land Application Sites By Jeff Lorimor and David Schmidt.
French cities’ urban freight surveys 1 st Scientific and Technical Workshop Bologna 05/11/2013 Presented by: Adrien Beziat, PhD, Paris, France.
The INTEGRATION Modeling Framework for Estimating Mobile Source Energy Consumption and Emission Levels Hesham Rakha and Kyoungho Ahn Virginia Tech Transportation.
Industrial Ventilation - A major control measure Dr. AA, UTM.
BRAVO - Results Big Bend Regional Aerosol & Visibility Observational Study Bret Schichtel National Park Service,
MS© The Financial Feasibility of Using Shelterbelts for Swine Odor Mitigation Photos: P. Schultz John Tyndall, Iowa State University Robert Grala, Mississippi.
L’information météorologique en lutte anti-acridienne Robert Stefanski Division de la météorologie agricole Organisation météorologique mondiale L’information.
Missouri Air Quality Issues Stephen Hall Air Quality Analysis Section Air Pollution Control Program Air Quality Applied Sciences Team (AQAST) 9 th Semi-Annual.
Company "ECO" Services (ТОВ “ЕКО”) Company "ECO" (ТОВ “ЕКО”)
André Vézina, ITA, La Pocatière Campus Planning a Shelterbelt April 2006.
An agroforestry practice This presentation was developed by the USDA National Agroforestry Center.
Snohomish County PUD Mr. Wiederspohn. Today we are going to: Think, talk and work like scientists 10 teams - do 10 different experiments at the same time.
Using Barriers with the Wind Erosion Prediction System
Clark County PM 10 Saturation Study Robert A. Baxter, CCM T&B Systems Clark County Air Quality Forum – 03/14/06.
Coastal Altimetry Workshop - February 5-7, 2008 CNES initiative for altimeter processing in coastal zone : PISTACH Juliette Lambin – Alix Lombard Nicolas.
Air-Surface Exchange of Persistent Substances by Michael McLachlan ITM, Stockholm University for the summer school The Advances.
Module 6: PINs M6. M6. PINs Contents: Project Identification Notes – how to structure them (including eligibility, baselines and additionality) Two projects.
Windy Cities
The Nature of Agriculture – Deficiencies in Food Production.
Ammonia Measurement Techniques Ji-Qin (Jee-Chin) Ni, Ph.D. Dept. of Agricultural and Biological Engineering Purdue University October 21, 2008 Albuquerque,
Centre technique de la Nutrition Animale Predict the enterobacteriaceae decontamination of feed by pelleting system F. Putier – Manager
4. Atmospheric chemical transport models 4.1 Introduction 4.2 Box model 4.3 Three dimensional atmospheric chemical transport model.
Detail-Preserving Fluid Control N. Th ű rey R. Keiser M. Pauly U. R ű de SCA 2006.
Power Plant Construction and QA/QC Section 1.8– Wind Energy
Comparison of extrapolation method and a method of dynamic dilutions with Nasal Ranger Field Olfactometer as two methods of odour concentration determination.
EPA/ELG/NODA—AIR QUALITY ISSUE 1. National Academy of Sciences Review  NAS review of state of the science regarding CAFOs and Air Quality Response: 
Snohomish County PUD Mr. Sparks. Does wind have power?
New Mexico Pilot Study: Salt Creek and White Mountain Wilderness areas Prepared by: Ilias Kavouras, Vic Etyemezian, Jin Xu, Dave DuBois, Marc Pitchford.
Mark J. Schultz, P.E. Chief, Environmental Assessment and Contaminant Control Branch Dust Division Mine Safety and Health Administration Pittsburgh Safety.
Ministère de l'Écologie, du Développement durable et de l’Énergie The French National Projet : Using WIM for direct enforcement.
Types of Models Marti Blad Northern Arizona University College of Engineering & Technology.
Nutrient content of dairy slurry Slurry nutrient variability and nutrient prices Slurry data from UW soils lab (Marshfield, WI) First year available 715.
SiSPAT-Isotope model Better estimates of E and T Jessie Cable Postdoc - IARC.
Understanding the Potential of IT
Some Observations from Using a Colloidal Borescope in Basalt Aquifers Gerry Winter.
Precision Management beyond Fertilizer Application Hailin Zhang.
1 Giovanni Langella PhD at ETH Zurich/ EMPA Presentation Urban Physics spring school 2016.
Mixing Length of Hydrogen in an Air Intake Greg Lilik EGEE 520.
SOIL AS AN ECOSYSTEM INTRODUCTION TO SOILS FIELD STUDY What do we know about soil now? What makes up soil? What lives there? Where does soil come from?
7. Air Quality Modeling Laboratory: individual processes Field: system observations Numerical Models: Enable description of complex, interacting, often.
IEC FDIS 2016 Consensus Analysis Project
CITYFIED PROJECT METHODOLOGY: AN INNOVATIVE, INTEGRATED AND OPEN METHODOLOGY FOR NEAR ZERO ENERGY RENOVATION OF EXISTING RESIDENTIAL DISTRICTS Cristina.
T. Higgs May 25, 2017 AESA Stack Testing Seminar
Melissa officinalis L. under cherry tree in Galicia, Spain
Introduction to Spatial Statistical Analysis
Presented by Harry C. Elinsky, Jr. Filtech, Inc.
Replication Strategies for improved Livestock Waste Management in China DONG Hongmin Prof. Chinese Academy of Agricultural Sciences Monitoring and.
Mentha x piperita L. under cherry tree in Galicia, Spain
Applying GIS to Santa Cruz Island:
Carl Bro a/s - Team Leader - IPPC-experts - Quality Assurance
Continuous measurement of airborne particles and gases
Territorial impact assessment
Agricultural and Biological Engineering Purdue University
min. of 100 ft. (varies by region)
UFP  PARTICLE NUMBER (ToN)
Victoria Schoenwald Undergraduate Program
Presentation transcript:

Denis Choinière, ing. M.Sc. Environmental Division Consumaj inc. Consumaj

IntroductionIntroduction  Livestock activity  Produces odor  Impact on the cohabitation with the neighborhood  Natural windbreaks were identified as a potential measure to reduce the present problem  The implantation of natural windbreaks around buildings is promoted by different organisations such as FPPQ, MAPAQ.  Method that is welcomed by producers and their neighborhood

Introduction… Odor Windbreaks Windbreaks may reduce odors in many ways  By facilitationg dust deposits  By physically intercepting dust  By diluting odorous gases with increased turbulence  By absorbing certain componants of the odor Phase 1 of the projetPhase 3 of the projet

ProblematicProblematic Many hypotheses  few are scientifically validated  Tyndall and Collecti (2000) propose the hypothesis that farms would almost become inodorous if all dust was removed.  It is demonstrated that windbreaks facilitate dust deposits (like they do for snow or sand)  So if dust contributes largely to odor transportation, windbreaks should reduce odors from livestock operations. This is a hypothesis which has not yet been validated scientifically with direct odor measurements.

The Project: « Influence of Windbreaks on Odors »  Initiated by Consumaj and their research team from Consumaj/ McGill University  Completed with the following teams l’UPA St-Jean Valleyfield ITA de la Pocatière  André Vézina  Financial Partners LEI (Livestock Environmental Initiative) CDAQ (Conseil pour le développement de l’agriculture du Québec) MAPAQ (Ministère de l’Agriculture et des pêcheries et de l’alimentation du Québec)

ObjectivesObjectives  Quantify the influence of natural windbreaks on odor dispersion/reduction  Evaluate the tree species influence on odor dispersion/reduction  Evaluate the influence of the distance between the windbreaks and the odor emission source  Quantify the impact of odor windbreaks on separating distances, that is, to estimate new seperating distances according to the odor windbreaks established.

The Phases  Phase 1  Validate the impact of dust on the sampling protocol and odor measurement  Phase 2  Develop a mobile odor generator  Phase 3  Experiment the influence of windbreaks on odor

Phase 1 - Dust  4 growing finishing piggeries  2 filtered samples and 2 non-filtered samples  Measure odor concentration Farm AFarm BFarm CFarm DAll Without Filter 261 ou/m³195 ou/m³272 ou/m³478 ou/m³306 ou/m³ With Filter180 ou/m³219 ou/m³368 ou/m³303 ou/m³274 ou/m³ Conclusion  Non-significant impact of dust on the sampling protocol

Phase 2- Odor Generator  Degasser principle, maximises the contact between manure and air  Uses fattening pigs’ manure  Built for a regular size truck box  Produces 500 to 1000 odor units/sec  Air flow of 3600 CFM  Odor production adjusted as needed

Phase 2- Odor Generator Manure tank Ventilator Variable speed Recirculation pump Dilution duct Air - manure contact 338 m²/m³ 8 degasser cubes

Phase 2- Odor Generator

Phase 3- Windbreaks  Do tests on existing mature windbreaks  Site with little interference with odors from animals  2 deciduous windbreaks  2 evergreen windbreaks  3 distances - odor source / windbreak (15m; 30m; 60m)  5 replicas (high density)  1 low density  1 high density  1 low density  1 high density

Site 1  Deciduous, low density

Site 2  Deciduous, high density

Site 3  Evergreens, low density

Site 4  Evergreens, high density

Phase 3- Windbreaks  Field Methodology

Phase 3- Windbreaks  Odor nuisance scale

Data Interpretation  Analyse odor generator samples with the dynamic olfactometer to measure the odor concentration and the odor nuisance.  Define the relation for each panellist Odor nuisance  Odor concentration  Transform the odor nuisance field data to an odor concentration for each position in the field

Data Interpretation  Combine those field odor concentrations with:  Odor source emission rate  Number of dilutions from source to field point  Wind direction  UTM coordinate  Absolute distance from source  Distance from source - parallel and perpendicular to wind direction  Make a large spreadsheet with all this information and use it for the analysis

Effect on Plume Length

Effect on Plume Area

Effect on Average Odor Dilution

 Windbreak performance to reduce odors is better when windbreak is at 15m from the source then at 30m or 60m  Windbreaks can reduce separation distance from livestock operations and neighbors by 19% to 25%  Windbreaks can reduce the area affected by the odor by 30% to 37%  Windbreaks can also reduce the odor concentration within the odor plume  Low porosity (below 30%) windbreak is needed to have a measurable effect on the odor ConclusionConclusion

AcknowledgementsAcknowledgements  CDAQ  IESE  MAPAQ  McGill University  UPA St-Jean Valleyfield  André Vézina  Site Owners

Question Period Thank-you for your attention!