-  r
                   United States
                   Environmental Protection
                   Agency 	
Environmental Monitoring
Systems Laboratory
Research Triangle Park, NC 27711
                   Research and Development
EPA/600/S4-88/020 August 1988
&EPA         Project  Summary

                   Fourier  Transform  Infrared
                   Spectrometry  of  Ambient
                   Aerosols
                   Martin Pollard and Joseph Jaklevic
                      Fourier transform infrared (FTIR)
                  spectrometry has been evaluated as
                  a method for determining the con-
                  centration of selected species pres-
                  ent in ambient aerosols collected on
                  Teflon* filters. The filters are analyzed
                  by transmission measurements after
                  collection of the fine fraction (<  2.5
                  urn diameter)  of  the  ambient
                  particles on 2 pm  pore size Teflon
                  filters. The spectra of the blank filters
                  are subtracted from  the spectra of
                  the loaded filters and the area of the
                  specific  absorbance  bands for am-
                  monium,  nitrate,  and  sulfate are
                  measured and compared to  calibra-
                  tion curves. The  filter orientation
                  must be maintained for all  measured
                  infrared spectra.
                      Calibration curves were  devel-
                  oped  for sulfate  and  ammonium
                  nitrate from measurements  of lab-
                  oratory-generated  particles. The
                  lower limit  of detection  (LLD)  for
                  laboratory-generated sulfate, cal-
                  culated from measurements  of the
                  620 cm'1 absorption band,  is  1.7
                  ng/cm2 (3o). The LLD for the  sulfate
                  band  at 1117 crrr1  is  0.2 ng/cm2;
                  however, this band cannot be used in
                  the analysis  of  ambient aerosol
                  samples because  of spectral inter-
                  ferences. The LLD  for laboratory-
                  generated ammonium nitrate  is 1.32
                  ng/cm2.  Multicomponent analysis
                  methods were developed to  analyze
                  ammonium nitrate  in the presence of
                  ammonium sulfate.
                   'Mention of product trademark or company
                   names does not constitute an endorsement or
                   recommendation for use
    Ambient aerosols were collected
during the Carbonaceous Methods
Species Methods Intercomparison
(GARB) study.  The filters  were
analyzed for sulfate by both FTIR and
Ion Chromatography (1C). There  is
good agreement between sulfate
analysis by 1C and analysis of the
FTIR transmission spectra of the air
filters. The LLD for ambient sulfate
was measured to be  5.8 ng/cm2. if
filter  orientation  is maintained the
LLD is estimated to be 1  - 2 ng/cm2.
    The CARB  study samples  were
also analyzed for elemental carbon
using FTIR. Intercomparisons  were
made with results obtained from the
analysis of co-collected  quartz  filter
samples using a thermal combustion
method of analysis. Good correlation
was found between the infrared
absorbance in the 650  - 666  cm*1
region of particles  collected on
Teflon filters  and the  elemental
carbon determined from analysis  of
the quartz filters. Attempts to develop
a direct elemental carbon calibration
standard on  Teflon filters  were
unsuccessful.  It was concluded that
calibrations must be made with co-
collected air samples on quartz filters
analyzed by thermal methods.
    The chemical interactions on the
filter between ammonium nitrate and
ammonium sulfate were  studied. It
was determined  that  both com-
pounds can interact to form the
nonvolatile  mixed salts 2NH4N03*
(NH4)2S04 and 3NH4N03.(NH4)2S04.
NH4NO3 was found to react on the
filter with NaCI to form  NaNO3 and
volatile NH4CI. A procedure based on

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this  reaction  is  proposed  as  a
method to retain nitrate ion on Teflon
filters.
    In  order  to  analyze  large
numbers  of  filter samples,  the FTIR
spectrometer was  modified by  the
addition  of  an  automatic sample
changer.  The sample changer com-
partment  accepts the filter  carousel
from  a Sierra/Anderson  model 245*
automated dichotomous  sampler.
The motion of the sample changer is
completely controlled by the  FTIR
computer.
    This  Project  Summary  was
developed by EPA's  Environmental
Monitoring   Systems Laboratory,
Research  Triangle  Park,  NC,  to  an-
nounce key findings  of the  research
project that is fully documented in  a
separate report of the same  title (see
Project Report ordering information at
back).

Introduction
    The collection  and  analysis of
ambient aerosols is an important means
of  studying   the chemistry  of  the
troposphere. The major  constituents of
the fine fraction (< 2.5 \vm diameter) of
the particulate matter in the atmosphere
are ammonium  sulfate,  ammonium
nitrate, and  elemental and organic
carbonaceous  particles.  Knowledge of
the origins, interaction,  and  deposition of
these  compounds is important  in the
study  of visibility   degradation,
atmospheric chemistry, acid deposition,
and the effects  of these  particles on
human health  and terrestrial ecology.
    Ambient   aerosols  are  typically
collected with  dichotomous air samplers
which collect particles in  two  size
fractions. The  fine fraction  particles are
<  2.5 nm in  diameter and the coarse
fraction particles are in the 2.5-15 urn
diameter size  range. The size fractions
correspond to the bimodal distribution of
particles sizes found in the atmosphere.
The particles  are collected on  various
filter  media  including  Teflon,  Nylon,
quartz, and paper filters. The  choice of
filter  media   depends, among other
things,  upon  the compounds  to be
measured, on  the analysis technique to
be used, and the cost of the filters.
    There  are  a number  of  chemical
analysis techniques available to measure
the concentrations  of  elements  and
compounds  collected  on air  filters.
Sulfate and nitrate ions collected on the
filters are  typically measured  using ion
chromatography. Ion chromatography  is
a very sensitive but destructive analytical
technique  for  the determination of sul-
fate, nitrate, and a number of other ions.
The  method requires  liquid  extraction,
followed by separate analysis of cations
and  anions, and provides  no  direct
information concerning compound
speciation of the ions. In addition, the
extraction  procedure can  alter  the
species found on the filter.
    Another method  for determining
sulfate collected on filters is x-ray
fluorescence  (XRF) analysis.  This
nondestructive  method of analysis  has
been  used  in an automated  system  to
determine elemental  sulfur, as well as
other elements, deposited  on  Teflon
filters. Sulfate  concentrations can  be
inferred by assuming that all of the sulfur
is  in  the form  of sulfate. Ion  chrom-
atography analysis for sulfate has been
compared to XRF analysis for sulfur on
Teflon air filters and  the two methods
have  been shown to  provide equivalent
results for sulfate. X-ray fluorescence
provides no  information concerning
nitrate deposition due  to  the  low energy
of the characteristic nitrogen x-ray
emission.
    X-ray diffraction  is a  nondestructive
technique that can provide for compound
identification. It is  difficult  to  obtain
quantitative  results   using  x-ray  dif-
fraction  for  two  reasons: (1)  The
sensitivity of this technique is relatively
low. Consequently, high particle loadings
are  required  to obtain  adequate
measurements  for accurate  compound
identification.  High  particle loadings
introduce the  possibility  of  chemical
reactions between particles concentrated
on the filter. (2) Water  in the sampled air
can promote recrystallization  of particles
on the filter. This introduces a preferred
orientation  in  the sample which  will
change the peak ratios in the diffraction
signals causing difficulties in calibration.
    Recently, another method for particle
analysis  on Teflon  filters  has been
reported  by other researchers who have
shown that ammonium and sulfate can
be  measured directly on Teflon filters
using  FTIR transmission  spectrometry.
Their results showed  the  equivalence  of
XRF  and FTIR  spectroscopy for the
quantitative  determination  of sulfate.
They also  reported   quantitative
measurements of the ammonium  cation.
In addition  to  the discrete  absorption
bands associated with  the  vibrational
modes of specific molecular species, the
mid-infrared spectrum of  these ambient
aerosols  shows  continuous  absorption
across the entire spectrum which  is
characteristic of  carbonaceous particles.
To the extent that a relationship between
this absorption and the elemental carbon
content can be established, a method fc
nondestructive  automated  analysis  c
carbon   particle   concentratio
simultaneously with that for sulfate, arr
monium, and nitrate  particles coul
result. Finally, this technique is appealin
because it makes use of a common filte
media, Teflon, is nondestructive, require
no sample  preparation,  is amenable  t
automation,  and can  provide  simul
taneous analysis of compounds  tha
typically require different  types  c
analysis on  different filter media.
    This   report   describes   a
experimental  program  intended  to buili
on  previous  work  reported  in tfv
literature, where a number of suggestion
are proposed to improve lower  limits c
detection  for  sulfate.  This  study fia
implemented  and tested  those  sugges
tions. Experiments  to  test  analytice
methods to quantitatively determine sul
fate, nitrate, ammonium,  and elemente
carbon  on  laboratory-generated  sam
pies and  ambient  samples are  alsi
described.
    An FTIR  spectrometer was modifie<
with the addition of an automatic sampli
changing compartment.  The  FTIR in
strument and sample changing  com
partment will  be  described;  however,  ,
detailed description of the FTIR systen
can be  found in the  operating manus
accompanying the instrument.

Conclusions
    Automated  FTIR analysis of aerosc
samples using  a Nicolet model 5DXB
Fourier transform infrared spectromete
has been  realized with  the design an<
construction  of  a specialized  sampli
handling system. The  sample  com
partment directly accepts  the sample
carousel from a commercial  air sample
produced  by   Sierra/Andersen  Inc
thereby minimizing  sample  handling
Software was developed and added  t(
the existing data collection and analysii
programs in  the  Nicolet FTIR to allov
complete control  of the position of am
filter. Software  was  also  written  t<
analyze ambient  air  samples  by auto
matically   providing  an   optima
background subtraction  and integration o
absorption  bands of  interest  of  th<
collected particles. This instrument pro
vides automated  nondestructive sulfat*
analysis of  up to 40 Teflon air filters witt
minimal sample handling and operate
intervention.
    Quantitative  spectral  analysis meth
ods were developed to  analyze sulfate it
aerosols collected on Teflon  filters
Laboratory experiments showed tha
detection limits are eight times lower fo

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analysis  using the sulfate  absorption
band at 1117 cm-1 than  for the band at
620  cm'1.  However,  spectral  inter-
ferences  found in ambient  samples pre-
vented use of this  former  band  for
routine sulfate analysis.  Analysis of air
samples  collected in Los Angeles during
the California Air Resources Board GARB
study showed good  correlation of  the
FTIR method of analysis for sulfate with
ion chromatography (1C) analysis of the
same sample filters.
    Small improvements in the detection
limit for sulfate using the 620 cnrr1 band
were realized by  using 2 pm pore size
Teflon filters, saving reference spectra of
each blank filter prior to  air sampling for
use during background subtraction, and
maintaining  the physical orientation  of
the filters  during  infrared spectral
measurements. All of  these practices
contribute to more accurate background
subtraction which  leads  to a  more
accurate  measurement  for sulfate.  The
lower  limit of  detection for  sulfate  in
ambient  aerosols using the  620  cnrr1
absorption band was measured to be 5.8
Vig/cm2 during the GARB study in which
the filter  orientation was not maintained
throughout the analysis. If  filter  orien-
tation is maintained, then the  lower limit
of detection is estimated to  be  1 - 2
pg/cm2 for ambient sulfate.
    Spectral analysis  methods  were
developed to  quantitatively measure
ammonium  nitrate in the  presence  of
interferences due to ammonium sulfate.
Ammonium  nitrate measurements  were
accurate  to within 3  -  5%  after  am-
monium  sulfate  spectral interferences
were removed on laboratory-prepared
aerosol  samples.  The  lower limit  of
detection for the  measurement  of  am-
monium  nitrate was found  to be  1.32
ng/cm2 for  laboratory-generated  sam-
ples.
   A high  degree  of  correlation  was
found between elemental carbon  mea-
surements on infrared spectra of ambient
samples  collected on Teflon filters and
elemental carbon  measured by thermal
methods  on  samples collected on quartz
filters. However,  attempts to develop a
direct  elemental  carbon  calibration
standard  on Teflon  filters using  lab-
oratory generated soot particles  was
unsuccessful.  It   was concluded  that
calibrations  must  be made  with co-
collected  air samples  on quartz  filters
analyzed  by  thermal methods.
   The sensitivity of infrared analysis to
specific compounds represents a unique
advantage  for performing  quantitative
chemical measurements  of ambient
aerosols.  The 2:1  and 3:1 mixed salts of
ammonium nitrate and ammonium sulfate
were identified  on ambient  filters
collected during the GARB  study. The
Fourier  transform infrared spectrometer
also  provides an   ideal  means  for
studying the  dynamics  of chemical
reactions  occurring  on   the  filter.
Laboratory experiments showed  that
nitrate ion could be  trapped  on the filter
by  reactions of ammonium  nitrate with
NaCI, but  experiments  with  ambient
samples were inconclusive.

Recommendations
    It is recommended  that this tech-
nique and  instrument be incorporated
into an air sampling and analysis network
in  order to develop  an  intercomparison
database  to  further  evaluate  this
instrument  relative  to other  methods of
analysis. This  instrument can easily be
incorporated into an existing air sampling
network  because it uses  a common filter
medium, Teflon, performs nondestructive
analysis, and is designed to handle large
numbers of samples in an  automated
system.  Additional ambient  samples are
required to:
1.   Determine  collection parameters,
    such as  sampling  time and  flow
    rates, to provide adequate samples
    for analysis within the constraints of
    the   sensitivity  of  the analytical
    method.
2.   Determine the  type  of  spectral
    interferences  that  will occur  in
    various sampling environments.
3.   Confirm the correlation  for  sulfate
    measured  by  Fourier  transform
    infrared   analysis   and  ion
    chromatography.
4.   Collect carbon  samples on  quartz
    filters in  parallel with Teflon filter
    samples to develop  a calibration for
    elemental carbon.
5.   Collect a  sufficient  number  of
    samples containing  ammonium ni-
    trate and  carbon  to develop an
    empirical method to determine  the
    baseline underneath the ammonium
    nitrate absorption band.

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  Martin Pollard and Joseph Jaklevic are with  Lawrence  Berkeley Laboratory,
        University of California, Berkeley, CA 94720.
  William A. McClenny is the EPA Project Officer (see below).
  The  complete report, entitled "Fourier Transform Infrared Spectrometry  of
        Ambient Aerosols," (Order No. PB 88-213 236/AS; Cost: $14.95, subject
        to change) will be available only from:
           National Technical Information Service
           5285 Port Royal Road
           Springfield, VA 22161
           Telephone: 703-487-4650
  The EPA Project Officer can be contacted at:
           Environmental Monitoring Systems Laboratory
           U.S. Environmental Protection Agency
           Research Triangle Park, NC 27711
United States
Environmental Protection
Agency
                  Center for Environmental Research
                  Information
                  Cincinnati OH 45268
Official Business
Penalty for Private Use $300

EPA/600/S4-88/020
0000329

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