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Continuous Ammonia Monitoring

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Title: Continuous Ammonia Monitoring Author: Jim Schwab Last modified by: mfaye Created Date: 10/26/2006 12:50:28 PM Document presentation format – PowerPoint PPT presentation

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Title: Continuous Ammonia Monitoring


1
Continuous Ammonia Monitoring
  • Jim Schwab, ASRC, University at Albany, SUNY
  • With contributions from many others!

2
Additional Contributers
  • Eric Edgerton, ARA, Cary, NC
  • Minsuk Bae, Yongquan Li, Ken Demerjian, John
    Spicer ASRC
  • Sara Pryor Indiana University
  • Bjarne Jensen - Danish National Environmental
    Research Institute
  • Jian Hou, Xianliang Zhou University at Albany
    School of Public Health
  • Donna Kenski - LADCO

3
Continuous Methods
  • Potential Routine Methods
  • Chemiluminescence
  • SEARCH TRN
  • API Model 201E or Thermo Model 17C (1 ppb LDL)
  • Ion Mobility Spectrometer
  • Laser Acousto-Optical Detection
  • AiRRmonia ECN, Netherlands, Mechatronics
    Instruments, b.v.
  • Research Methods
  • Tunable Diode Laser TDLAS
  • Wet Effusive Diffusion Denuder (WEDD)
  • Wet Scrubbing Long Path Absorption Spectrometer
    WS-LOPAP
  • Wet Scrubbing IC analysis (URG AIM 9000)
  • MARGA Steam Jet Collection IC

4
SEARCH Continuous NH3 Method (TRN)
  • 2-channel oxidized AND reduced nitrogen
    chemiluminescence analyzer
  • Channel 1 samples ambient air through a sodium
    carbonate denuder (TN), then two heated
    converters
  • Channel 2 samples ambient air through dual sodium
    carbonate and citric acid denuders (TN ), then
    through a single moly converter
  • NH3 operationally defined as TN-TN

SEARCH
5
Total Reduced Nitrogen (TRN) Analyzer
Total Reactive Nitrogen after Na2CO3 denuder
Total Oxidized Nitrogen after Na2CO3 and citric
acid denuders
350º C Moly Converters
650º C Pt Converter
SEARCH
6
NH3 and NH4 during CFPP Plume Event
NH4 increases NH3 disappears NHx conserved
SEARCH
7
Method 2 - IMS
  • Candidate for routine monitoring
  • IMS Ion Mobility Spectrometer (AirSentry-IMS
    Ammonia Analyzer, Particle Measuring Systems,
    Boulder, CO)
  • Ionization based time-of-flight technique
    performed at atmospheric pressure
  • Instruments are targeted to a specific molecule
    in a specific concentration range
  • Range for this instrument 0300 ppb (Lab
    Intercomparison) 0-100 ppb (Field Deployment)
  • Cost (with OBC) 26 K

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9
Operational Details
  • Requires up to 5 li/min of clean, dry instrument
    air (dewpoint -40º C)
  • Internal sample pump option
  • Factory default Smoothing Factor (8) should be
    increased for minute (or longer) averaged data
  • Optional On Board Calibration - integral
    permeation oven set up (recommended)
  • Nickel 63 sealed radioactive source (less than
    .005 microcuries) ionization source

10
IMS Field Data
Preliminary data do not cite or quote!
11
Pranalytica Nitrolux NH3 Analyzer
Photoacoustic spectroscopy CO2 laser Low-noise
microphone In-line particle filter (40 µm) LDL
and cost depend on model Model 1000 LDL 1
ppb Cost 24K Model 200 LDL 0.2 ppb Cost
38K Model 100 LDL 0.1 ppb Cost 72K
Note Instrument used was one of the first sold
by Pranalytica and company claims to have made
significant improvements to later (i.e. current)
instruments
12
Laboratory Intercomparison
  • September 12-30, 2005 at ASRC
  • Six measurement Methods seven instruments in
    all (Chemiluminescence method not included
    because instrument was not configured properly
    my error)
  • Heated glass manifold for uniformity of sampling
    environment
  • Synthetic air and calibration system
  • Ambient sample for two extended periods

13
Method Characteristics Tested during
Intercomparison
  • Response to known NH3 accuracy and precision
    of calibration
  • Time Response to step changes and spikes
  • Comparability during ambient sampling
  • Potential interferences

14
Preliminary data do not cite or quote!
15
Preliminary data do not cite or quote!
16
Preliminary data do not cite or quote!
17
Sampling and response time
  • This is an important issue for gaseous ammonia
    measurement it clearly affects methods
    detecting gaseous ammonia directly and ammonium
    after scrubbing.
  • The TDL is the system of choice for quick and
    accurate response but it is not a routine
    method!

18
Spring 2006 Measurements Pinnacle State Park,
Addison, NY
  • NH3 measured with AirSentry IMS
  • HNO3 with denuder difference chemiluminescence
    method

NH3 HNO3
Mean 1.06 ppb 0.66 ppb
Standard Dev. 0.77 ppb 0.62 ppb
Median 0.87 ppb 0.48 ppb
Maximum 5.82 ppb 5.75 ppb
Est. MDL 0.3 ppb 0.2 ppb
Completeness 90.1 85.4
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22
Response Time Memory Effect
  • Note that on previous slide the HNO3 drops below
    1 ppb each night
  • However, NH3 does not drop very low between peaks
  • We believe this is due at least in part to
    changing uptake and release of NH3 on the sample
    inlet, the switching valves, and the sample
    handling lines in the instrument

23
Candidate Methods for Monitoring and their
Major Shortcoming(s)(Editorial Opinions!)
  • ARA TRN (chemiluminescence)
  • Not ammonia specific
  • Three heated converters difference method
  • AirSentry IMS (Particle Measuring)
  • Response Time Problem
  • Nitrolux 200 (or 100) (Pranalytica)
  • Response Time (worst of all tested instruments,
    but should be better in current versions)
  • Cost Highest of routine monitoring candidates
    (for sufficiently low LDL)
  • AIRRmonia, URG AIM, MARGA need liquid reagents

24
Recommendation
  • ARA TRN (chemiluminescence)
  • Custom implementation of proven analyzer
  • Response time issue minimized (eliminated?) since
    there is no handling of ammonia
  • EPRI is considering commercialization of
    converter technology

25
Acknowledgements
  • Funding from
  • EPA
  • NYSERDA
  • NYSDEC
  • Although the research described in this article
    has been funded in part by the U.S. Environmental
    Protection Agency, it has not been subjected to
    the Agencys required peer and policy review and
    therefore does not necessary reflect the views of
    the Agency and no official endorsement should be
    inferred should be inferred.

26
End of Presentation
27
Nitric Acid Measurement
  • Denuder difference in conjunction with NOy
  • TECO 42S low-level chemiluminescence analyzer
    operates with two measurement channels and one
    background (prereactor zero) channel
  • Both measurement channels preceded by external
    heated molybdenum converters
  • Base channel is NOy
  • Second channel uses a NaCl coated denuder as
    inlet this channel measures NOy HNO3
  • Difference of channels is HNO3

28
Schematic of HNO3 Method
OUTSIDE
INSIDE
Gas lines
BYPASS PUMP
SS NEMA box mounted outside (5 m agl)
Power and signal wires
Heated Mo converter
Heated Mo converter
Mode switching valves
Model 42S chemiluminescence analyzer
NaCl coated denuder
PFA Teflon Tube
29
1-minute NH3 and WD at Yorkville
Spikes between 90 and 180 degrees suggest
nearby NH3 sources.
SEARCH
30
Local Sources of NH3 at YRK
2.6 km
1.5 km
Poultry operations within several km line up
with NH3 spikes.
3.3 km
SEARCH
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