Tekran ® Automated Mercury Speciation F.H. Schaedlich 1, Robert K. Stevens 2, D.R. Schneeberger 2, Eric Prestbo 3, Steve Lindberg 4, Gerald Keeler 5 F.H.

Slides:



Advertisements
Similar presentations
Atmospheric Mercury in the Guadalupe Watershed Andy Lincoff Peter Husby Barbara Bates US EPA Region 9 Laboratory Richmond, CA Richmond, CA.
Advertisements

Modeling Atmospheric Mercury Deposition to the Sounds and Other Water Bodies O. Russell Bullock, Jr. NOAA Air Resources Laboratory (On assignment to the.
UPDATE ON DAQS AIR QUALITY MEASUREMENTS & MERCURY STUDIES NC DENR/DAQ Mercury/CO 2 Workshop Raleigh, NC April 19, 2004 Steve Schliesser Todd Crawford NC.
Modification and Validation of Diesel Particulate Matter Cassette for PM-1.0 Sampling at Different Flow Rates Saulius Trakumas and Peter Hall SKC Inc.,
1 Problem Resolution Model 1130 & Model 1135 Frank Schaedlich 330 Nantucket Blvd. Toronto, Canada M1P 2P4 Rev 1.12 Aug 2004.
Atmospheric Mercury in the Oil Sands Region Workshop at Earth Science Analysis and Application of Speciated Mercury Data July 30, 2014 Dan McLennan,
Inert Atmosphere Systems in OLED Research and Fabrication Copyright, 1996 © Dale Carnegie & Associates, Inc.
Air Pollution and Stratospheric Ozone Depletion
Control of Sulfur Oxides Dr. Wesam Al Madhoun
1 Source-attribution for atmospheric mercury deposition: Where does the mercury in mercury deposition come from? Dr. Mark Cohen NOAA Air Resources Laboratory.
Air Pollution Chapter 5.
Shannon Capps April 22, Mercury cycling From
SF Bay Region Atmospheric Mercury Monitoring Funded by: RMP, USEPA w/ services by: NADP/MDN, Contra Costa, San Francisco, San Jose.
An Investigation of Atmospheric Mercury Deposition to Bay Area Storm Runoff: a Pilot Study Sarah Rothenberg, Lester McKee, Don Yee, Alicia Gilbreath, Michelle.
The ProRak™ Advantage An introduction to Hg Process Monitoring and Feedback Control.
Section 1: What Causes Air Pollution?
Building a Global Modeling Capability for Mercury with GEOS-CHEM Noelle Eckley Selin GEOS-CHEM meeting 6 April 2005.
Eric Prestbo Ph.D. Analysis of Atmospheric Mercury Speciation at HEDO Station, Okinawa.
Global Transport of Mercury (Hg) Compounds Noelle Eckley EPS Second Year Symposium September 2003 Photo: AMAP & Geological Museum, Copenhagen.
Mercury in the Great Lakes Region Sponsored by the Commission for Environmental Cooperation’s Environment, Economy and Trade and Pollutants and Health.
Gas Analyzer Theory of Operation
Atmospheric Mercury Simulation with CMAQ Version Russ Bullock - NOAA Air Resources Laboratory* Kathy Brehme - Computer Sciences Corp. 5 th Annual.
Wet Deposition of Mercury In The U.S. Results from the NADP Mercury Deposition Network, David Gay Illinois State Water Survey, Champaign, IL,
LAB 8 – MERCURY IN FOREST SOILS RELATIONSHIP BETWEEN HG AND ORGANIC MATTER.
Mercury is cyanide soluble and therefore is removed from the ore and follows through the process solution. Mercury is adsorbed onto the activated.
D. Gay, Schmeltz, Sharac, Nat. Tribal Conf. for Env. Management, Billings, MT, June 26, 2008, Slide 1 Current Mercury Monitoring Approaches in Tribal Country.
Chapter 9: Air: Climate and Pollution
Trends of Mercury Flow over the US with Emphasis on Florida Progress Report by Janja Husar and Rudolf Husar Submitted to Thomas Atkeson, Florida DEP May.
Elemental Mercury Capture by Activated Carbon in a Flow Reactor Shannon D. Serre Brian K. Gullett U.S. Environmental Protection Agency National Risk Management.
1 Eric M. Prestbo, Ph.D. Air Mercury Speciation Accuracy and Calibration Presented at the SFO Air Mercury Speciation.
Continuous measurements of the atmospheric concentrations of Reactive Gaseous Mercury (RGM), Fine Particulate Mercury (FPM) and Gaseous Elemental Mercury.
2537A Tekran Mercury Analyzer
1 Session 2 – Analytical Issues Mercury Speciation Workshop 330 Nantucket Blvd. Toronto, Canada M1P 2P4 Rev 1.10 Nov 2003.
Unit 3: Chapter 12 notes AIR.
NOAA’s Atmospheric Mercury Monitoring in the Gulf of Mexico Region [April 2007 summary] This summary is updated periodically, and the current version is.
Trans-Pacific Chemical Transport of Mercury: Sensitivity Analysis on Asian Emission Contribution to Mercury Deposition in North America Using CMAQ-Hg C.-J.
Organization of Course INTRODUCTION 1.Course overview 2.Air Toxics overview 3.HYSPLIT overview HYSPLIT Theory and Practice 4.Meteorology 5.Back Trajectories.
Mercury Monitoring in Ambient Air F.H. Schaedlich
Field Methods of Monitoring Atmospheric Systems Measurement of Air Pollution Copyright © 2009 by DBS.
Global Modeling of Mercury in the Atmosphere using the GEOS-CHEM model Noelle Eckley, Rokjin Park, Daniel Jacob 30 January 2004.
Ultra-trace Mercury Monitoring in Air. Company History Founded in 1989 to develop custom instrumentation for environmental analysis Founded in 1989 to.
Investigation of air-snow exchanges of mercury: proof of concept for automated gradient sampling of interstitial air at the Summit FLUX facility Xavier.
Modeling the Atmospheric Deposition of Mercury to Lake Champlain (from Anthropogenic Sources in the U.S. and Canada) Dr. Mark Cohen NOAA Air Resources.
Air Pollution.
Mercury Dry Deposition
Detailed Operation: Model 1130 and Model 1135 Rev: 1.11 November 3, 2003.
Mercury Measurement Programs within NOAA/ARL Steve Brooks, Mark Cohen, Tilden Meyers, Paul Kelley, Winston Luke NOAA/Air Resources Laboratory NOAA/Air.
1 Modeling the Atmospheric Transport and Deposition of Mercury Dr. Mark Cohen NOAA Air Resources Laboratory Silver Spring, Maryland Mercury Workshop, Great.
D. Gay, Schmeltz, Sharac, Nat. Tribal Conf. for Env. Management, Billings, MT, June 26, 2008, Slide 1 Current Mercury Monitoring Approaches in Tribal Country.
1 Session 3 – Particulates & Data Handling Mercury Speciation Workshop 330 Nantucket Blvd. Toronto, Canada M1P 2P4 Rev Nov 2003.
Dr. Mark Cohen NOAA Air Resources Laboratory Silver Spring, Maryland
Objectives Name five primary air pollutants, and give sources for each. Name the two major sources of air pollution in urban areas. Describe the way in.
Air Pollution and Stratospheric Ozone Depletion
CHAPTER 12.1 ENVIRONMENTAL SCIENCE What Causes Air Pollution?
Material Flow Carol Timson 4/12/2004. Overview l Biogeochemical Systems Mass Balance l Ecosystem Closed Loop l Anthroposystem Open System l Material Flow.
Material Flow Carol Timson 4/12/2004. Overview l Biogeochemical Systems Mass Balance l Ecosystem Closed Loop l Anthroposystem Open System l Material Flow.
2002 U.S. data from USEPA National Emissions Inventory (NEI); 2002 Canadian data from Environment Canada; 1999 Mexican data from inventory prepared by.
NYS Department of Environmental Conservation ATMOSPHERIC MERCURY BEST PRACTICES AND SOP WORKSHOP Topics and questions for discussion that require consensus.
ANLEC R&D COMMUNICATION PACK ( ). Trace emissions from Oxy Combustions do not pose significantly higher health, environmental or operational.
Office of Research and Development National Risk Management Research Laboratory, Air Pollution Prevention and Control Division Photo image area measures.
ANLEC R&D COMMUNICATION PACK ( ). While mercury can be removed from Oxy-Fuel flue gas, further work is required to understand its form and removal.
NOAA’s Atmospheric Mercury Monitoring in the Gulf of Mexico Region January 17,
CONSTRAINTS FROM RGM MEASUREMENTS ON GLOBAL MERCURY CHEMISTRY Noelle Eckley Selin 1 Daniel J. Jacob 1, Rokjin J. Park 1, Robert M. Yantosca 1, Sarah Strode,
Microwave Soil Vapor Treatment
Pollution control methods of thermal power plants
Air Transport and Fate Research Partnership Meeting,
Control of Sulfur Oxides Dr. Wesam Al Madhoun
Dr. Tanveer Iqbal Associate Professor,
Biogeochemical Cycle of Mercury (Hg)
John Munthe and Ingvar Wängberg
Presentation transcript:

Tekran ® Automated Mercury Speciation F.H. Schaedlich 1, Robert K. Stevens 2, D.R. Schneeberger 2, Eric Prestbo 3, Steve Lindberg 4, Gerald Keeler 5 F.H. Schaedlich 1, Robert K. Stevens 2, D.R. Schneeberger 2, Eric Prestbo 3, Steve Lindberg 4, Gerald Keeler 5 1 Tekran Inc., Railside Rd. Toronto, Canada M3A 1A3, 2 Florida Dept. Environmental Protection at USEPA, Res Triangle Park, NC 27711, 3 Frontier Geosciences Inc., 414 Pontius Ave. N., Suite B, Seattle, WA Oak Ridge National Lab. PO Box 2008, Oak Ridge, TN University of Michigan, School of Public Health, 109 Observatory Street, MI

Tekran Automated Mercury Speciation Objectives Development of automated methods to measure and differentiate between: Development of automated methods to measure and differentiate between: Reactive Gaseous Mercury (RGM) in ambient air Reactive Gaseous Mercury (RGM) in ambient air Total Particulate Mercury (TPM) in ambient air Total Particulate Mercury (TPM) in ambient air Elemental mercury (Hg 0 ) in ambient air Elemental mercury (Hg 0 ) in ambient air

Tekran Automated Mercury Speciation Ambient Air Mercury Speciation Different forms of gaseous Hg have very different behaviors. Different forms of gaseous Hg have very different behaviors. Forms can interconvert in the atmosphere and in various reservoirs. Forms can interconvert in the atmosphere and in various reservoirs. Classes of mercury in ambient air: Classes of mercury in ambient air: Elemental mercury: Hg 0. Elemental mercury: Hg 0. Reactive mercury: Hg II, RGM, Hg 2+. Reactive mercury: Hg II, RGM, Hg 2+. Particulate mercury: Hg P, TPM. Particulate mercury: Hg P, TPM.

Tekran Automated Mercury Speciation Model 2537A Mercury Analyzer Provides continuous total gaseous (TGM) readings with update rate as low as 2.5 minutes. Provides continuous total gaseous (TGM) readings with update rate as low as 2.5 minutes. Detection limit < 0.1 ng/m 3 (5 min. samples). Detection limit < 0.1 ng/m 3 (5 min. samples). Automatic recalibration with internal Hg 0 permeation source. Automatic recalibration with internal Hg 0 permeation source. Capable of unattended operation for extended periods. Capable of unattended operation for extended periods.

Tekran Automated Mercury Speciation Model 2537A Analyzer

Tekran Automated Mercury Speciation Flow Diagram of Model 2537A Mercury Analyzer

Tekran Automated Mercury Speciation Elemental Mercury: Hg 0 Typically 90+% of atmospheric Hg loadings. Typically 90+% of atmospheric Hg loadings. Relatively inert. Long residence time. Relatively inert. Long residence time. Hg 0 sources impact large areas. Hg 0 sources impact large areas. Sources: chlor-alkali plants, gold and Hg mining, thermal power plants. Sources: chlor-alkali plants, gold and Hg mining, thermal power plants.

Part 1 Reactive Gaseous Mercury Monitoring

Tekran Automated Mercury Speciation Why Bother Measuring RGM ? RGM (as HgCl 2 ) is emitted from power plants and incinerators. RGM (as HgCl 2 ) is emitted from power plants and incinerators. RGM is removed rapidly via wet and dry deposition. RGM is removed rapidly via wet and dry deposition. Often responsible for contamination of sensitive nearby ecosystems. (Florida Everglades, Arctic). Often responsible for contamination of sensitive nearby ecosystems. (Florida Everglades, Arctic).

Tekran Automated Mercury Speciation Reactive Mercury: Hg(II) or RGM Consists of reactive, water soluble forms, primarily HgCl 2. Consists of reactive, water soluble forms, primarily HgCl 2. Usually only a few percent of total gaseous mercury present in the atmosphere. Usually only a few percent of total gaseous mercury present in the atmosphere. Short range: deposits relatively close to the source of emission. Short range: deposits relatively close to the source of emission. Primary sources: Coal burning power plants, waste incinerators. ( Chlor-alkali plants ?) Primary sources: Coal burning power plants, waste incinerators. ( Chlor-alkali plants ?)

Tekran Automated Mercury Speciation Difficulties Measuring RGM Method must be 1-2 orders of magnitude more sensitive than total mercury methods. Method must be 1-2 orders of magnitude more sensitive than total mercury methods. Reject much larger elemental component. Reject much larger elemental component. Exclude particulate bound mercury, however, particulate filters have problems passing RGM. Exclude particulate bound mercury, however, particulate filters have problems passing RGM. Apparatus must pass RGM to the collector quantitatively. Apparatus must pass RGM to the collector quantitatively.

Tekran Automated Mercury Speciation Model Principles of Operation Quartz, specially coated annular denuder is thermally desorbed and regenerated. Quartz, specially coated annular denuder is thermally desorbed and regenerated. Sampling Phase. Sampling Phase. Absorbs RGM while passing all elemental Hg. Absorbs RGM while passing all elemental Hg. Model 2537A reads Hg 0 during this phase. Model 2537A reads Hg 0 during this phase. Desorption/Analysis Phase. Desorption/Analysis Phase. Zero air used as carrier. Zero air used as carrier. RGM released as elemental mercury. RGM released as elemental mercury.

Tekran Automated Mercury Speciation RGM Sampling Phase Denuder is slightly warm. Denuder is slightly warm. Inlet slightly warm. Inlet slightly warm. Denuder captures all RGM while passing Hg 0. Denuder captures all RGM while passing Hg 0. Total sample flow is 10 lpm. Total sample flow is 10 lpm. Analyzer measures Hg 0 during this time. Analyzer measures Hg 0 during this time.

Tekran Automated Mercury Speciation Analysis Phase Denuder is heated to 500C. Denuder is heated to 500  C. Inlet heated to clean upstream glassware. Inlet heated to clean upstream glassware. Denuder releases captured RGM as Hg 0. Denuder releases captured RGM as Hg 0. Excess zero air flow cleans upstream components. Excess zero air flow cleans upstream components. Instrument measures accumulated RGM as Hg 0. Instrument measures accumulated RGM as Hg 0.

Tekran Automated Mercury Speciation Lab RGM Apparatus

Tekran Automated Mercury Speciation Quartz Denuder Assembly

Tekran Automated Mercury Speciation Model 1130 Denuder & Pump Module

Tekran Automated Mercury Speciation Preliminary Results - Toronto

Tekran Automated Mercury Speciation Preliminary Results - Toronto

Tekran Automated Mercury Speciation Lab Testing: Frontier Geosciences

Tekran Automated Mercury Speciation Seattle RGM Data Ambient Air - Downtown Seattle Courtesy: Frontier Geosciences

Tekran Automated Mercury Speciation Mercury Levels - Rural Michigan Courtesy: UMAQL

Tekran Automated Mercury Speciation Summary - RGM A quartz annular denuder coated with KCl quantitatively collects HgCl 2 but does not retain Hg 0. A quartz annular denuder coated with KCl quantitatively collects HgCl 2 but does not retain Hg 0. HgCl 2 collected on a denuder is thermally desorbed as Hg 0. HgCl 2 collected on a denuder is thermally desorbed as Hg 0. The automated instrument that uses this denuder technology measures RGM concentrations down to 1 pg/m 3. The automated instrument that uses this denuder technology measures RGM concentrations down to 1 pg/m 3. Denuder lasts weeks between recoatings. Denuder lasts weeks between recoatings.

Part 2: Particulate Mercury Monitoring

Tekran Automated Mercury Speciation Why Bother Measuring TPM ? Particulate bound mercury (TPM / Hg P ) is created directly by some industrial processes and also formed downwind of sources by the combination of mercury with existing particulates. Particulate bound mercury (TPM / Hg P ) is created directly by some industrial processes and also formed downwind of sources by the combination of mercury with existing particulates. TPM is removed rapidly via wet and dry deposition. TPM is removed rapidly via wet and dry deposition.

Tekran Automated Mercury Speciation Particulate Mercury: TPM Consists of various compounds of mercury bound onto particles. Consists of various compounds of mercury bound onto particles. Size range: Generally < 3 um. Size range: Generally < 3 um. Usually only a few percent of total mercury present in the atmosphere. Usually only a few percent of total mercury present in the atmosphere. Short range: deposits relatively close to the source of emission. Short range: deposits relatively close to the source of emission.

Tekran Automated Mercury Speciation Difficulties Measuring TPM Method must be 1-2 orders of magnitude more sensitive than total mercury methods. Method must be 1-2 orders of magnitude more sensitive than total mercury methods. Must reject much larger elemental component. Must reject much larger elemental component. Method must exclude reactive gaseous mercury, however, normal particulate filters have problems in that they retain RGM. Method must exclude reactive gaseous mercury, however, normal particulate filters have problems in that they retain RGM.

Tekran Automated Mercury Speciation Model Principles of Operation Sampling Phase Sampling Phase Quartz, regenerable particulate filter (RPF) captures fine fraction (< 2.5 um) particulates after air has passed through impactor and denuder Quartz, regenerable particulate filter (RPF) captures fine fraction (< 2.5 um) particulates after air has passed through impactor and denuder Desorption/Analysis Phase Desorption/Analysis Phase Zero air used as carrier Zero air used as carrier Downstream pyrolyser is activated first Downstream pyrolyser is activated first RPF is heated to desorb captured particulates RPF is heated to desorb captured particulates

Tekran Automated Mercury Speciation Model 1135 – Particulate Mercury Monitor Unit stacks on top of Model 1130 Unit stacks on top of Model 1130 Allows simultaneous deter- mination of Hg 0, RGM and HgP Allows simultaneous deter- mination of Hg 0, RGM and HgP Detection limit ~ 1 pg/m 3 Detection limit ~ 1 pg/m 3

Tekran Automated Mercury Speciation Model 1130 & Model 1135 Flow Path

Tekran Automated Mercury Speciation Ambient Air Speciation

Tekran Automated Mercury Speciation Conclusions - HgP A quartz RPF quantitatively collects particulate mercury but does not retain Hg 0 A quartz RPF quantitatively collects particulate mercury but does not retain Hg 0 HgP collected on a denuder is thermally desorbed and converted to Hg 0 in the pyrolyzer HgP collected on a denuder is thermally desorbed and converted to Hg 0 in the pyrolyzer Carbon based particulate matter on the filter is oxidized to CO 2 during desorption cycle Carbon based particulate matter on the filter is oxidized to CO 2 during desorption cycle Filter is usable for 1 – 2 weeks before requiring restuffing Filter is usable for 1 – 2 weeks before requiring restuffing