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Presentation to BOSC

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Potential for re-emission from coal combustion residues (fly ash and scrubber sludge) ... Burn different rank coals in the Multi-pollutant Combustion Research Facility ... – PowerPoint PPT presentation

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Title: Presentation to BOSC


1
ORD Mercury Combustion ProgramStatus and
Accomplishments
  • Presentation to BOSC
  • By
  • U.S. Environmental Protection Agency
  • Office of Research and Development
  • National Risk Management Research Laboratory
  • February 23, 2005

2
Overview of Todays Presentation
  • Highlight mercury combustion RD included within
    Long Term Goal 1 of the mercury MYP
  • To reduce and prevent release of mercury into the
    environment
  • Discuss what has been accomplished
  • Describe where we need to move in the future

3
ORD Hg Combustion - Background
  • Coal combustion is significant source of mercury
    domestically and internationally
  • Reducing mercury emissions is complex due to the
    variety of coal types and control technology
    configurations

4
ORD Hg Combustion - Program
  • ORD/NRMRL Mercury Combustion Program is
    Addressing
  • Approaches to optimize currently utilized SO2,
    NOX, and PM controls to get mercury co-benefit.
  • Mercury control via injection of sorbent
    (primarily activated carbon)
  • Measurement of mercury emissions from coal-fired
    power plants (e.g., CEMs)
  • Potential for re-emission from coal combustion
    residues (fly ash and scrubber sludge)

5
ORD Hg Combustion - Coordination
Collaborators
Primary Clients
  • Office of Air Radiation (OAQPS and OAP)
  • Office of Solid Waste (OSW)
  • EPA Regional Offices
  • DOE
  • EPRI, utilities, others
  • Overseas partners
  • Energy Research Centre of the Netherlands
  • European Union

Other Clients
  • Utilities
  • States and local regulatory agencies
  • DOT and DOI
  • Association of State and Territorial Solid Waste
    Management Officials
  • Industries using CCR for commercial applications
  • Foreign governments

6
Control TechnologybyRavi Srivastava
7
Power Plant Equipment and Mercury
Hg(0), Hg(II), Hgp - form important for capture1
Wet Scrubber
Stack
SCR
Flue Gas
ESP or FF
Coal Air
700 F
Hg0
Ammonia
gt2500 F
Ash
Residue
Limestone or lime slurry
  • Factors that influence mercury control
  • Coal type
  • Time/temperature profile
  • Flue gas composition (chlorine) and fly ash
    characteristics (carbon, calcium, iron, porosity)
  • Air pollution controls already in place

1 Hg(0) elemental Hg Hg(II) oxidized Hg Hgp
particulate Hg
8
Sorbent Injection
Option1
  • Sorbent is injected upstream of the PM control
    device (ESP or FF)
  • Collected fly ash and sorbent are mixed

Option 2 Electric Power Research Institutes
(EPRI) TOXECON System
  • Sorbent injection Compact Hybrid Particulate
    Collector (COHPACTM)
  • Potential solution to ash reuse problems

coal
  • The extent of capture depends on
  • Sorbent characteristics (particle size
    distribution, porosity, capacity at different
    gas temperatures)
  • Residence time in the flue gas
  • Type of PM control (FF vs. ESP)
  • Concentrations of SO3 and other contaminants

9
Continuation of TOXECONTM DOE Phase I Project
Gaston, Low-sulfur Bituminous Coal
Testing Between June-November, 2003 (Longest ACI
testing period thus far)
  • ACI operated nearly continuously between June
    26-November 25 rate lt 0.7 lb/MMacf
  • Weekly Hg removal between 80- 90, average 86
  • Less variability in emissions over longer
    averaging period
  • Need to change air-to-cloth ratio to get 90
    removal
  • TOXECON requires a FF after an ESP, a plant
    configuration limited to relatively few plants
    currently.

Source 2004 Mega Symposium
10
Performance of Halogenated PACs(B-PAC and E-3)
  • Performance of B-PAC and E-3 for Western coal
    (subbituminous, lignite) is similar to that of
    TOXECON (using conventional PAC) for Eastern
    bituminous coal

11
Optimization of Existing Controls Projects
  • Mercury Control in Wet Scrubbers (Project 1)
  • Key question
  • Can we increase net capture in wet scrubbers and
    stabilize mercury in scrubber effluent?
  • Findings
  • Absorbed Hg2 is not stable, a portion of Hg2
    can be reduced to Hg0 and reemitted
  • Sulfite/bisulfite and pH identified as reemission
    parameters
  • Additives used for waste water treatment may be
    able to stabilize Hg2
  • Future RD efforts
  • Additive evaluation
  • Sorbents for Hg0 absorption

12
Optimization of Existing Controls Projects, cont.
  • Enhanced Wet Scrubber Hg Control via SCR
    Oxidation (Project 2)
  • Key question
  • what is the science and can we control the extent
    of oxidation?
  • Findings
  • HCl is a key source of chlorine needed for Hg0
    oxidation
  • No apparent effect of catalyst aging
  • Effect of residence time on oxidation
  • No apparent effect of SO2 on oxidation
  • Future RD efforts
  • Fundamental research to identify and characterize
    the role of flue gas composition, fly ash
    properties, and SCR variables on Hg oxidation
  • Field tests focusing on SCR impact on Hg
    oxidation for units firing subbituminous coals
    and coal blends

13
Sorbent Injection Projects
  • Activated Carbon Injection (Project 3)
  • Key question
  • How effective are the new class of commercial
    halogenated carbon sorbents?
  • Future RD efforts
  • Burn different rank coals in the Multi-pollutant
    Combustion Research Facility (MPCRF) and assess
    sorbent removal efficiency
  • Test effect of carbon feed rate and sorbent type
    on Hg removal
  • Evaluate leaching and utilization properties of
    residues
  • Develop, evaluate, and characterize the potential
    of advanced sorbents for the removal of mercury
    and other pollutants
  • Hg Control with PM Collectors (Project 4)
  • Key question
  • Can we optimize Hg control with PM collectors
    (ESPs) and thereby greatly reduce the overall
    cost by reducing or eliminating the need for
    activated carbon injection?
  • Findings
  • Capture of Hg is very dependent upon flue gas
    composition
  • Competition between Hg, SO3 and H2O for active
    sorption sites
  • Future RD efforts
  • Bench-and pilot-scale experiments
  • Hg chemistry and kinetics for inclusion in
    predictive models

14
Contribution of EPA Science
  • Through mercury and multi-pollutant RD efforts,
    ORD has
  • Comprehensively assessed state of the art mercury
    mitigation technology
  • Characterized key parameters associated with
    SCR-enhanced mercury control
  • Identified parameters that impact mercury capture
    in wet scrubbers

15
Program Office Support
  • ORD has provided key support to OAR during
    development of mercury and multipollutant
    regulations
  • Utility Mercury Rule
  • Briefed the Administrator on the status of
    mercury controls
  • Developed and updated a mercury white paper that
    represents the Agencys technical judgment
    regarding the status of mercury controls, and the
    emission reduction levels potentially achievable
  • Developed comprehensive estimates of performance
    and costs of mercury and multipollutant controls
  • Clear Skies, Mercury Rulemaking and Interstate
    Air Quality
  • Developed estimates of performance and cost of
    mercury, NOX, and SO2 controls for electric
    utility boilers
  • Characterized engineering and economic factors
    that affect installations of mercury and
    multipollutant control technologies

16
Additional Activities
  • Regularly provide guidance on mercury control
    technologies to states, regions, and other
    organizations
  • Working with DOE and other interested parties to
    set up an international workshop on mercury
    control in China

17
Future Activities
  • In the future, combustion RD will
  • Inform compliance decisions (mercury/multipollutan
    ts)
  • Stimulate development of more cost-effective
    integrated control options
  • Assist other countries (e.g., India and China)
    understand how to cost-effectively mitigate their
    mercury emissions - UNEP

18
Continuous Emissions Monitors for Coal-Fired
Power PlantsbyJeff Ryan
19
Objectives and Approach
  • Quality Hg measurements are critical for
  • Regulatory application
  • Control technology RD
  • International emissions inventories
  • Hg measurements include
  • Manual methods (e.g., OH, M29, etc.)
  • Hg CEMs
  • Alternative monitors (e.g., sorbent media)
  • Hg measurements are complex
  • Source variation and characteristics and
    interferences
  • Pollution control device effects (inlet/outlet)
  • Total vs. speciated Hg
  • QA/QC tools (i.e., elemental oxidized Hg gas
    standards)
  • Systematic Research and Demonstration
  • Fundamental and Laboratory Research
  • Pilot-plant testing

20
Accomplishments and Impacts
  • Regulatory Applications
  • Hg monitoring critical component of trading rule
    and Clear Skies
  • NRMRL has conducted several Hg CEM pilot-plant
    and field studies that demonstrate current levels
    of performance and support regulatory application
  • Demonstrated use of critical elemental and
    oxidized Hg gas standards co-developed by NRMRL
  • Written comprehensive status report submitted to
    regulatory docket (FY03 APM)
  • Coauthored monitoring procedures in proposed MACT
    and cap and trade rules
  • NRMRL generated data to support OAR responses to
    comments

21
Accomplishments and Impacts (cont.)
  • Control Technology Research Applications
  • Reliable Hg CEMs for control technology
    application are critical for technology
    evaluation and process monitoring/control
  • Research and technology application are
    complicated by need to perform speciated
    measurements before/after pollution control
    devices
  • Numerous biases affect quantification and
    speciation
  • Pilot-plant and field proof-of-concept testing of
    device (inertial impactor) to minimize these
    effects have been successful

22
Much work still to be done
  • Regulatory Application
  • Demonstrate proposed/promulgated monitoring
    procedures prior to implementation
  • Develop/demonstrate Instrumental Reference Method
    critical for implementation
  • Conduct additional field testing to address
    implementation issues
  • Demonstrate application in likely post-regulation
    environments through additional field testing
    (PAC inj, SCR, scrubbers, etc)
  • Note FY06 APM deliverable on schedule

23
Much work still to be done (cont.)
  • Control Technology Application
  • Must identify, demonstrate and implement accurate
    and reliable process control Hg monitor suitable
    for performance testing
  • Additional pilot-plant and field testing critical

24
International Application
  • Cost-effective monitoring techniques /
    technologies are critical to establishing Asian
    Hg emissions inventory
  • Are Hg CEMs practical?
  • Costly
  • Complex
  • Monitoring with sorbent media and continuous
    sampling an option
  • Application must be validated (costly)
  • Training and Demonstration?

25
Summary Message
  • Were Not Done Yet
  • NRMRL research comprehensively addressing
    regulatory, control technology and international
    activity research needs
  • OAR relies heavily on ORD to support regulatory
    issues related to source measurement

26
Coal Combustion ResiduesbySusan Thorneloe
27
Coal Combustion Residue (CCR) Assessment
Characterization and Cross-Media Transfers
  • CCR Work in Support of Long Term Goal 1
  • Assess the effect of selected Hg-control
    technologies on the characteristics of CCRs and
    how selected utilization/disposal practices
    impact the fate of Hg and other metals (APM 2003)
  • Assess the effect of APC systems on the
    characteristics of Hg-enriched CCRs and increased
    environmental risk from CCR management (APM 2004)

28
Current Program Outputs
  • Completed
  • Review of available CCR characterization data and
    management practices (EPA-600/R-02-083, Dec 2002)
  • Major finding is that available data is of
    limited applicability
  • Data are not comparable due to range of leach
    tests in use
  • Limited quality assurance or documentation
  • Determination of appropriate leach test in
    consultation with OSW
  • Major effort to determine appropriate leach
    testing protocol that is applicable to CCR types
    and management practices adopted the Leaching
    Framework (Kosson et al., 2002)
  • Meeting with Science Advisory Board in 2003
  • supportive of technical approach and high level
    of QA incorporated into protocol

29
Current Program Outputs (cont.)
  • Completed
  • Evaluation of CCRs from 11 Facilities (14 units)
    for total and leachable content for mercury and
    other metals
  • A realistic approach was used for long-term metal
    release for a range of conditions typical of CCR
    disposal and utilization (2003-2005) - Draft
    interim report is undergoing review
  • Memo for OAR regulatory docket providing results
    from CCR evaluations conducted to date (prepared
    in consultation with OSW)

30
Current CCR Characteristics/Results
  • Based on four facilities where either ACI or
    brominated sorbents are in use, leaching of
    mercury from CCRs does not appear to be of
    concern for most disposal environments
  • Limited data for only two facilities with wet
    scrubbers suggests that leaching of Hg may be of
    concern and warrants further evaluation

Note Briefings providing CCR results were
conducted for OSW, OAQPS, OARs AA, and the
Administrator in 2004.
31
Current CCR Characteristics/Results (cont.)
  • There are some management practices that may
    aggravate leaching potential (e.g., co-disposal
    with high-sulfur coal rejects).
  • Leaching of As and Se is of concern in nearly all
    management scenarios whether or not Hg-control
    is in place
  • Advanced sorbent technologies can increase
    capture of Arsenic, selenium, and other metals
    resulting in higher potential environmental
    releases

32
In Progress
  • Leaching Studies (APM 2006)
  • Completing evaluation of CCRs that have been
    received
  • Obtaining additional CCRs to account for range of
    expected coal types and air pollution control
    configurations
  • Evaluation of potential release rates for use in
    fate and transport models
  • Thermal Stability Studies (APM 2008)
  • Completing life-cycle evaluation to determine
    environmental tradeoffs from production of wall
    board, asphalt, and cement clinker using CCR and
    non-CCR material
  • Examining formation/release of organo-Hg
    compounds for anaerobic decomposition of
    mercury-enriched land-disposed CCRs (APM 2007)
  • Capstone report on potential cross-media
    transfers from use of Hg-enriched CCRs in
    commercial applications (APM 2008)

33
Current and Future Impacts to Regulatory
Environment
  • Will enable EPA to ensure cross-media transfers
    are addressed. Inputs will be used in RCRA
    Subtitle D regulatory effort to evaluate
    potential environmental and health impacts.
  • Could result in increased costs for those
    facilities that may have to install engineering
    controls such as use of liners, leachate
    collection, and infiltration control
  • Have identified some management practices that
    will aggravate leaching potential.
  • Major interest in the U.S. and Europe to utilize
    ash and scrubber sludge. These results can help
    to ensure that scenarios that pose potential
    environmental and health concerns are avoided.
  • Results will make it easier to target future
    evaluations of specific CCRs.

34
Future Program Outputs
  • Current and future in-house CCR research will
  • Assist OSW with their health risk assessment and
    development of regulations that respond to
    changing characteristics of coal combustion
    wastes
  • Assist with analysis of the fate of Hg and other
    metals from land applied CCRs (APM 2006) Report
    to be produced
  • Allow federal/state/local regulators to determine
    beneficial reuse options that are protective of
    human health and the environment (APM 2008)
  • Report on formation of organo-Hg from anaerobic
    decomposition of CCRs (APM 2007)
  • Report on fate of toxic metals from management of
    CCRs (i.e., disposal and commercial usage) from
    plants equipped with multi-pollutant control
    technologies (APM 2008) will provide mass
    balance tracking fate of mercury and other
    metals.

35
Achieved Outcomes
  • Critical and comprehensive review of the status
    of mercury controls has significantly enhanced
    the ability of policy makers to make informed
    decisions
  • Advanced CEMs for regulatory and control
    technology applications
  • Developed/refined protocols to evaluate
    cross-media transfers are now in use allowing
    more informed decisions by stakeholders
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