SERA
                                 United States
                                 Environmental Protection
                                 Agency
                                 •Industrial Environmental Research
                                 Laboratory
                                 Research Triangle Park NC 27711
                                 Research and Development
                                  EPA-600/S2-81-110  Sept. 1981
Project Summary
                                 Response  of  Portable VOC
                                 Analyzers  to  Chemical
                                 Mixtures


                                 D. A. DuBose, G. E. Brown, and G. E. Harris
                                   The report gives the responses of
                                  two types of portable VOC analyzers
                                  (Century Systems  OVA-108 and
                                  Bacharach TLV Sniffer), calibrated
                                  with methane and used to measure a
                                  variety of chemical vapor mixtures.
                                  Instrument  response  data for both
                                  binary and ternary mixtures of selected
                                  chemicals are presented. Various
                                  empirical models were evaluated to
                                  determine an appropriate method of
                                  estimating  mixture concentration
                                  based on instrument response. The
                                  evaluation concluded that the instru-
                                  ment response for a mixture falls
                                  between the responses expected for
                                  the pure compounds in the mixture.
                                  Thus, an interpolation or weighted
                                  average model can be used to predict
                                  the response for mixtures based on
                                  known responses for individual chem-
                                  icals. Both  linear and  logarithmic
                                  weighted average models are applied
                                  to the data and presented  with esti-
                                  mates of accuracy. In general, these
                                  models predicted the  instrument
                                  response to within 30 percent of the
                                  observed value.
                                   This Project Summary was developed
                                  by  EPA's Industrial Environmental
                                  Research Laboratory, Research Tri-
                                  angle Park, NC. to announce 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
                                   Portable VOC (Volatile Organic Com-
                                  pound) analyzers have been widely used
                                  in the identification of fugitive emission
                                  sources, a process  commonly called
                                  "screening." Screening is important
                                  both in research to  develop emission
                                  factors and in proposed regulatory
                                  monitoring of fugitive emissions. While
                                  these VOC analyzers will respond to
                                  mo.st organic vapors,  they respond with
                                  varying sensitivity to different chemical
                                  species.
                                   Previous to the present study. Radian
                                  Corporation performed a laboratory
                                  evaluation of the response character-
                                  istics of two common VOC analyzers
                                  (the Century Systems OVA-108 and the
                                  J.W. Bacharach TLV  Sniffer) to a large
                                  variety of individual organic compounds
                                  in air. The results of this previous EPA-
                                  funded study are  available in  two
                                  reports EPA-600/2-81-002 (NTIS PB81
                                  136194) and EPA-600/2-81 -051.
                                   This summary presents the results of
                                  testing in the area of chemical mixtures.
                                  The data base reported here includes
                                  response data on nine binary chemical
                                  combinations of acetic acid, acetone,
                                  chloroform, cyclohexane,  benzene,
                                  methanol, and methyl ethyl ketone plus
                                  one ternary combination.
                                   The results of these analyses show
                                  that the response to  a binary chemical
                                  mixture falls between the responses of

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the two individual chemicals at the total
concentration  of the  mixture.  This
indicates that synergistic  effects are
weak and suggests that some form of
interpolation or weighted average can
be used to predict the response of the
mixtures based on individual chemical
response characteristics.


Computation Methods
  This section describes and discusses
methods for estimating concentrations
when VOC instrument responses are
known. The fractional  composition of
the  detected vapors  must also be
known. Computed and graphical esti-
mates are discussed.
  In general, the VOC instrument
response to a mixture of compounds is
intermediate to the individual responses
to each one of them  at the same total
concentration.  This effect may be
approximated by a weighted average of
the responses (or linear interpolation in
the case of two chemicals). An estimate
of the weighted average response is:
                P,aiCTbie1/2Si
(1)
where
  RA = the estimated weighted average
      response,

  P, = the fraction of the mixture total
      concentration accounted  for by
      compound i (P, = Ci/CT),

  a, = exp(A) with "A" from Brown, et
      al. (1980)* for component i,

  b, = coefficient "B"from Brown, etal.
      (1980) for component i,

  s, = parameters "SE" from Brown
      et al. (1980) for component i,

  CT = £- C,, the total  concentration,
      and

  d = the concentration in the mixture
      of compound i.

The coefficients A, B,  and SE can be
found in  Tables 5-169 and  5-170 of
Brown,  et al. (1980) for selected com-
pounds.
  The above discussion involves the
prediction of an instrument response
when the actual  concentration of
mixture  components  is  known. In a
       practical situation, the reverse  is the
       case: the response is observed and it is
       desired to estimate the concentration of
       the constituents. Basically, this cannot
       be  done without some additional
       information. The compound identifica-
       tion of the constituents must be known.
       If the constituent proportions are also
       known, the total concentration can be
       computed assuming the above model is
       correct. The total concentration  (Cr) is
       estimated by solving Equation (1).
         Equation (1) cannot be solved explicitly
       for  total concentration.  An iterative
       solution is required. This can be done
       using the Newton-Rhapson method.
       Letting
                         p,a,CTi  e1/2Si - R   (2)
       where R  is the observed instrument
       response, and
                                                      ,-1  1/2Sl
                     2. pib,a,CT
        f(CT)= 2L Pib,a
 ,-1   1/2S2
    e   i
(3)
then the iteration formula is:

     Cl+i = C, - f(C,)/f (C,).         (4)

A reasonable starting value C0 is R, the
observed instrument response.

  Alternatively, a weighted logarithmic
average may be used. In this case:
       log (RL) = Z. p, [log a, + V4s? + b, log CT]
                 i                       (5)

       where RL is the estimated  instrument
       response using a weighted logarithmic
       average and logarithms are to base e.

       In contrast to the previously given
       weighted arithmetic  average model,
       Equation (1), this weighted logarithmic
       average  model. Equation (5) has an
       explicit solution for actual total con-
       centration:
        log CT =
                  log R -
                 IP,
(log a, + 1/2 s,2)
                              p,b,
                                        (6)
        For binary mixtures, the solutions are as
        follows. The arithmetic weighted aver-
        age  iteration formula is:
•In report EPA-600/2-81-002 (NTIS PB81-
136194)
                C, + 1 = C, - f(C,)/f'(Ci)

        where
                   bi 1/2S?
        f(CT) = piai CT e    +
                  bz  1/2 si
             p2a2 CT  e    -R,
                                 (7)
                                        and

                                        C0 = R or another suitable starting value.

                                        The logarithmic weighted average solu-
                                        tion is:

                                        log CT =
                          (8)
Results
  The models discussed above predict
the mixture response  by weighted
average or linear interpolation between
the response of two pure chemicals on
either an  arithmetic or  a logarithmic
scale. This "weighted average" model is
readily extendable to three or more
compounds. Asummary of the response
data and the precision  of these two
models is given in Table  1. Neither the
arithmetic nor logarithmic scale model
shows  any clear advantage
applied over the entire data set.
ever, the logarithmic model gives much
poorer estimates than the arithmetic
model in some cases. Both models are
able to predict  mixture response to
within  about  ±30  percent  of  the
observed value, which is  about as good
as the single chemical data on which
the models are based. There is some
advantage  to the logarithmic scale
model in that it  has a discrete solution,
while the arithmetic scale model must
be solved iteratively or graphically.

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Table 1.    Comparison of Percent Error for Arithmetic and Logarithmic Weighted A verage Models for Mixtures
                                                          Average Percent Error of Model Prediction
                                                          OVA
        Compound Mixtures
               Arithmetic
          Logarithmic
  Compound
Response Factor*
Compound
                            OVA

                            1.64
                            0.80
                            0.29
                            9.28
              TLV

             15.60
              1.22
              1.07
Cyclohexane
Methanol
Methyl Ethyl Ketone
                                                                TLV
Arithmetic
                                                                                                    Logarithmic
Acetic Acid and Chloroform
Acetic Acid and Cyclohexane
Acetic Acid and Acetone
Acetone and Chloroform
Acetone and Cyclohexane
Benzene and Methyl Ethyl Ketone
Benzene and Methanol
Chloroform and Cyclohexane
Methanol and Methyl Ethyl Ketone
Benzene, Methanol, and
Methyl Ethyl Ketone
25
31
33
39
31
-9
-1
29
-16

-9
20
11
27
17
28
19
-121
-5
-87

-50
-83
4
-3
-21
7
9
10
-13
12

12
-88
-37
-28
-80
3
9
8
-90
9

9
       Response Factor*
     OVA

     0.47
     4.39
    .0.64
  Acetic Acid
  Acetone
  Benzene
  Chloroform

 * Ratio of actual concentration to instrument response at 10,000 ppmv response (EPA -600/2 -81 -051).
**A 10,000 ppmv response to chloroform with TLV is not achievable.
TLV

0.70
2.01
1.12
                                          D. A. DuBose, G. E. Brown, andG. E. Harris are with Radian Corp., P.O. Box 9948,
                                           Austin, TX 78766.
                                          Bruce A. Tichenor is the EPA Project Officer (see below).
                                          The complete report, entitled "Response of Portable VOC Analyzers to Chemical
                                           Mixtures," (Order No. PB 81 -234 262; Cost: $8.00, 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:
                                                 Industrial Environmental Research Laboratory
                                                 U.S. Environmental Protection Agency
                                                 Research Triangle Park, NC 27711
it US GOVERNMENT PRINTING OFFICE, 1981—757-012/7336

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