2010 VOC Workshop Session 1D: Fugitive emissions – definitions, measurement and verification David Knight Belgium - Flemish Government Environment, Nature.

Slides:



Advertisements
Similar presentations
Afdeling Algemeen Milieu- en Natuurbeleid - sectie Lucht Koning Albert II-laan 19, 9e verdiep., B-1210 Brussel Tel Fax NEC-programme.
Advertisements

TUR Planner Course Session 1 Introduction to Toxics Use Reduction and the Toxics Use Reduction Act.
Alabaster Corp. Tank Cleaning and Degassing General Process Overview.
1 EGTEI – 22 November 2011 Nadine ALLEMAND – EGTEI secretariat VOC monitoring issues in the Gothenburg Annex.
Slides 3 – Material flow analysis MATERIAL FLOW ANALYSIS.
Insert Filepath here International Symposium on Environmental Issues Industrial Pollution Control and Risk Management September 28 & Jack O’Keeffe.
EMS Model Policy Planning Implementation Checking Corrective Action Management Review.
Design for the Environment Felicia Kaminsky ESM 595F 2 November 2000.
19 June 2006 Environmental Protection Agency City of Copenhagen Solvent Emission Directive Frank Sorensen Environmental Protection Agency.
UF Lead Policy Review. The Basics Lead is a poison Blood Neurological effects Systemic effects Death More severe effects on kids Increased effects on.
Institute for Resource Efficient and Sustainable Systems Graz University of Technology The Concept of Cleaner Production June 30, 2006 „The Concept of.
Cleaner Production Assessment (Chapter 4)
Development of Policy Instruments: Environmental Health Indicators Veerle Arren Human Ecology Department Vrije Universiteit Brussel International Symposium.
Life Cycle Analysis and Resource Management Dr. Forbes McDougall Procter & Gamble UK.
Waste management.
Tour Stop 1: Outside The Building. Community Connectivity Encourages A Walkable Neighborhood At least 10 community services, and high density residential.
Solvent Emissions From the Organic Coating Process Jim Rowbotham Pexa Ltd. © Pexa 2009.
TRI MARTIANA.  A good and effective ventilation system is necessary in a workplace which have processes that emit air contaminants such as dust, fumes,
Air Emissions from Stationary Fuel Combustion Training Workshop Moldova, Chisinau, Sept
ENVIRONMENTAL MONITORING AND REPORTING BY ENTERPRISES FEASIBILITY OF DEVELOPING MONITORING GUIDELINES FOR CHEMICAL INDUSTRY IN EASTERN EUROPE, CAUCASUS.
Life Cycle Analysis. What is a Life Cycle Analysis? A method in which the energy and raw material consumption, different types of emissions and other.
By: Oscar Cardenas. Why Recycle? Saves natural resources- By making products from recycled materials instead of virgin materials, we conserve land and.
Harmonization process between inventory and Model projections of Air Pollution Emissions in Italy October, TFEIP Workshop on Emission Projections.
Workshop, 12/3/2004 Banska Bystrica – SLOVAC REPUBLIC “INTEGRATED LICENCE PROCEDURE (Greek case)” Katerina Iakovidou-Anastasiadou Hellenic Ministry for.
Site visit COVEX Site visit Visit to COVEX, S.A Comunidad de Madrid CONSEJERIA DE MEDIO AMBIENTE, VIVIENDA Y ORDENACIÓN DEL TERRITORIO.
APPLICATION FOR THE EU ECO- LABEL IN PRACTICE- CASE STUDY PROF.DR.WERNER SOBOTKA.
Atmosphere and Local Environment Experiences of implementation in ‘older’ Member States.
Ben Larson 1 November th Avenue NE, Seattle, WA (206)
PRINTING.
EPA Overreach WATERS OF THE U S METHANE REDUCTION PLAN LEGISLATIVE /REGULATORY FORUM SEPTEMBER 16, 2015.
Bavarian State Ministry of the Environment and Public Health 17./ Dr. Heinz Baumgarten, Dr. Richard Schlachta Ministry of Urban Development and.
Ministry of Waters and Environmental Protection, ROMANIA 1 BERCEN 1 st Exchange program – November 2002 Croatia PROBLEMS AND SOLUTIONS IN COOPERATION.
The Renson Headquarters Renovation issue Renovation issue Major findings Major findings The RENSON- The RENSON- Headquarters More information... More information...
EDF R&D Energetic aspects of urban waste treatments Claire Lecointe, Charlotte Barbut 2 nd AWAST Workshop November th, 2001, Rennes.
Exchange of practical experience with the implementation of the VOCs Solvents Directive 1999/13/CE: Technical instruction for how to demonstrate equivalent.
IPPC Amcor Flexibles Reflex - Facility B. IPPC – AFR_B The Facility was qualified as an installation for surface treatment of products using organic solvents,
VOC Directive 1999/13/EC: The German Approach to Simplification of the Reduction Scheme: Simplified Verification of Compliance Contents: Simplified Verification.
Dr. Richard Schlachta Bavarian Agency for Environment Salzburg, 21. – IMPEL Workshop on VOC: German point of view to the case study “coating.
Life Cycle Assessment of Waste Conversion Technologies April 15, 2004.
Practical experience with the implementation of the Solvents Directive in the Czech republic VOC Workshop, June 2010 Lucie Krejčí Air Protection Department.
1 Review of the Integrated Pollution Prevention and Control (IPPC) and National Emission Ceilings (NEC) Directives Marianne Wenning DG ENV, Head of Unit,
FEAD ANNUAL CONFERENCE 2008 Future Challenges for the Waste Management Industry Paris, 19 September 2008.
BARRIERS TO THE USE OF REDUCTION SCHEME
Assessment of options to streamline legislation on industrial emissions IPPC Review Stakeholder Hearing 4 May 2007 Caspar Corden Entec UK Limited.
EGTEI – Expert Group on Techno-economic Issues Methodology for data collection Presented by Nadine Allemand EGTEI secretariat Workshop to promote ratification.
12 May Cologne-CL 1 EU – ETS CO 2 Monitoring Stakeholders day MONITORING AND REPORTING GUIDELINES By Ir. Claude Loréa, CEMBUREAU Technical Director.
BERCEN plenary meeting Sofia, March 18, 2005 Agenda item 8 Draft Scope and Proposed Location of BERCEN Training 2005 BERCEN Secretariat.
AWAST final meeting - Brussels december 2003 Aid in the management and European comparison of Municipal Solid WASte Treatment methods for a global.
BALANCE OF MATERIAL. Practical Advices During the generation of the Material Balance phase.
Integrated and Planned Enforcement of Environmental Law Phare Twinning Project CZ03/IB/EN/01 MONITORING Mr. Jan Prášek IPPC Agency.
Air pollution policy: Institutional and administrative set-up Bob Nieuwejaers Head of Divison Division Air, Nuisance, Risk management, Environment and.
Better Regulation Dr. Jens Peter Mortensen Environmental Regulation of Industry Danmarks Naturfredningsforening EEB Representative in TWG of WI, WT & FDM.
The current legal situation
How Cells are Affected by and Interact with Their External Environment.
Solvent Management Plan (SMP) Template in Slovenia Workshop on the exchange of practical experience with the implementation of the VOC Solvent Emissions.
1 Review of the IPPC Directive and related legislation Second Meeting Of Working Group E On Priority Substances 17 October 2007 Filip FRANCOIS – DG ENV.
2010 VOC WORKSHOP Session 2 E Simplification options for the dry cleaning sector and for applying the reduction scheme in general David Knight Belgium.
Main flexibility tools for the adoption of high emission standards for LCPs set in the new Industrial Emissions Directive Gerard Lipinski Coordinator of.
13 juni 2016 © 2008, VITO NV – alle rechten voorbehouden Assessment of use of general binding rules for implementation of IPPC Directive General binding.
LCPs – Large Combustions Plants – what ist a large combustion plant?  > 50 MW rated thermal input  Irrespective of type of fuel, age and branch  Heat.
Ministry for Ecology, Energy, Sustainable Development and Sea in charge of Green Technologies and Climate Negotiations
VENTILATION AND AIR CONDITIONING Under the Subject Industrial Safety and Environment || ||
MONITORING Mr. Jan Prášek IPPC Agency.
Tony Kloss, Tyson Ford, Marisa Miller, Michael Pupillo
Nadine ALLEMAND Objectives of the presentation
IPPC Review Stakeholder Hearing
EPV as a communication and marketing tool: of course but…
Data specifications for IED Annex II Module 4
Industrial Emissions Directive Targeted stakeholder survey
Presentation transcript:

2010 VOC Workshop Session 1D: Fugitive emissions – definitions, measurement and verification David Knight Belgium - Flemish Government Environment, Nature and Energy department Air, Nuisance, Risk Management, Environment and Health Division Koning Albert II-laan 20, bus 8, 1000 Brussel Tel – Fax

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Mass balance of solvent based printing with incineration I = Input Solvent consuming Installation OUTPUT O1 = waste gases (stack) O2 = solvents in waste water O3 = residual solvent in product O4 = fugitive emissions O5 = destroyed/captured O6 = solvent in waste O7 = solvent in products (e.g. paints) O8 = recovered solvents for reuse O9 = other Simplified example Solvent based printing: O4 = fugitive emissions O5 = destroyed/captured O1, O2, O3, O6, O7, O8 = marginal Fugitive emission = O4 = I – O5 ELV and BATAEL  ELV: 100 mg C / Nm 3 20% of solvent input  Reduction scheme: 25% * (4*solids)  BREF: 7,5 – 12,5 % * (4*solids)

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Solvent based printing: flexography, rotogravure, laminating, varnishing (> 200 ton/year) I = 100% O4 = 10% O5 = 90 %  BREF BATAEL: 7,5 - 12,5 %  In IPPC permits: 10% of reference emission  Solvent based printing => incinerator  Floor extraction + cleaning machines => incinerator Solvent based flexography, rotogravure, laminating, varnishing

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 [O4 = I – O5] in practice UnitValueDevia tion Min.Max. Flowratem 3 /h Concentrationg/m 3 5 OperationHours3400 O5Ton/year85010% InputTon/year1000 O4Ton/year O4% of solvent input 1523,56,5 POSSIBLE SOLUTION = MEASURE O4 INSTEAD OF O5

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 [O4 = I – O5] in practice Possibility 1 Printing room with negative pressure due to extraction, all extraction to incinerator Possibility 3 Printing room under pressure / no pressure NO PROBLEM Can be tested with e.g. smoke PROBLEMATIC Emissions through doors, windows Possibility 2 Printing room with negative pressure due to extraction, not all extraction to incinerotor Emission through ventitlation shafts Can be tested with e.g. smoke Ventilation shafts can be measured

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Possibility 3: several methods tested during 1 production day (VITO  Method 1: input + passive sampling  Method 2: input + portable FID  Method 3: FID for O5 and passive sampling for O4  Method 4: FID for O5 and portable FID for O4  Method 5: portable FID for O4 and O5  Method 6: theoretical estimation based on specifics of printing machines and used solvents

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 1: solvent input + passive sampling I O4 Solvent based flexography, rotogravure, laminating, varnishing O5  Solvent input measured  O4 measured with passive sampling  O4 = 11% of solvent input

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 1: solvent input + passive sampling

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 5: Portable FID Input O4 Solvent based flexography, rotogravure, laminating, varnishing O5  O4 and O5 with portable FID  2 measurements for each source  O4 + O5 = 100%  O4 = 14,9 %

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 6: Theoretical estimation  Theoretical percentages based on the following assumptions:  Completely covered ink fountain = 0%  Adequate coverage of ink fountains = 2,5%  Chamber doctor blades = 2,5%  Open ink fountain = 5%  Disfunctioning of incinerator = 0,29%  Cleaning machine not connected = 5%  Residual solvent in products = 2,5%  ect.  Estimation of solvent use for every machine  Combination of this information leads to emission estimate of 9,6 %

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 2: solvent input + FID I O4 Solvent based flexography, rotogravure, laminating, varnishing O5  solvent input measured  O4 measured with portable FID

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 3: Passive sampling + FID I O4 Solvent based flexography, rotogravure, laminating, varnishing O5  O4 with passive sampling  O5 with FID continuous measurement  Solvent input = O4 + O5

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method 4: FID + portable FID I O4 Solvent based flexography, rotogravure, laminating, varnishing O5  O4 with portable FID: 4 measurements  O5 with FID: continuous measurement  Solvent input = O4 + O5

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Method%95% confidence % Cost 1 input + passive input + port FID3110Not representative for entire period passive + FID9260Not useful FID + port FID20107Not useful+++ 5 port FID theoretical10-+

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Conclusions solvent based printing  O4 = I – O5 does not always work in practice  Measuring O4 is in some cases a robust and feasible solution  Measuring O4 can however be expensive and labour intensive  For extrapolation from 1 day measurement to an entire year stable ventilation and printing specifics are needed  Measuring does not reduce emissions  Alternative approach: estimation based on reduction measures applied?

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Mass balance of paint/ink production with incineration I = Input Solvent consuming installation OUTPUT O1 = waste gases (stack) O2 = solvents in waste water O3 = residual solvent in product O4 = fugitive emissions O5 = destroyed/captured O6 = solvent in waste O7 = solvent in products (e.g. paints) O8 = recovered solvents for reuse O9 = other Simplified example Paint/ink production : 01 = waste gases O4 = fugitive emissions O5 = destroyed/captured O7 = solvent in product O2, O3, O6, O8, O9 = marginal Emission = O1 + O4 = I – O5 – O7 ELV  150 mg C / Nm 3 AND 3% of solvent input  3% of solvent input

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 O1 + O4 = I – O5 – O7 UnitValueDeviat ion Min.Max. I = INPUTTon/year % O7 = PRODUCTTon/year9.7001% O5 = INCINERATORTon/year10010%90110 O1 + O4Ton/year200>100%40723 O1 + O4% of input4%0% POSSIBLE SOLUTION = MEASURE O4 INSTEAD OF O1 AND O7

2010 VOC WORKSHOP: SESSION 1D17-18/06/2010 Paint and ink production: estimation of emissions at 3 plants in Belgium  Plant 1  O1 + O4 = I – O5 – O7  Plant 2  Uses results of monitoring of working environment  Twice a year employees wear passive sampling badges  For every production area, the ventilation frequency is known (e.g. air is refreshed 6 times per hour)  Concentration and ventilation combined give an estimate of mass flux for every area  Plant 3  All emissions are lead through ventilation shafts  All emissions are measured at least once a year  Continuous paint production  Difference between mass balance and measurement = 85%