EVALUATION  OF  THREE  LOW  COST
      EXHAUST ANALYZERS
                 by
             Charles Urban
                 for
 U.S. ENVIRONMENTAL PROTECTION AGENCY
         Ann Arbor, Ml. 48105
              May 1984
          SOUTHWEST RESEARCH INSTITUTE
          SAN ANTONIO                 HOUSTON

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EVALUATION  OF THREE LOW COST
         EXHAUST  ANALYZERS
                                  PROPERTY OF:
                                  NATIONAL VEHICLE AND FUEL EMISSIONS
                                  LABORATORY LIBRARY
                                  2000 TRAVERWOO0 DRIVE
                                  AA'N ARBOR. Ml 48105
                        by
                 Charles Urban
                        for
 U.S.  ENVIRONMENTAL  PROTECTION AGENCY
            Ann Arbor, Ml.   48105
                        Approved:
                        Karl J. Springer, Director
                        Department of Emissions Research
                        Engines, Emissions and Vehicle Research Division

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SOUTHWEST RESEARCH  INSTITUTE
POST OFFICE DRAWER 28510 • 6220 CULEBRA ROAD • SAN ANTONIO, TEXAS. USA 78284 • (512) 684-5111'TELEX 76-7357
ENGINES. EMISSIONS. AND VEHICLE RESEARCH DIVISION
TELEX: 767357
TWX: 910-871-1084
TO:
    Robert J. Garbe, Project Officer
    William Clemmens, Branch Technical  Representative
    Control Technology Assessment  and Characterization Branch
    Environmental Protection Agency
    2565 Plymouth Road
    Ann Arbor, MI  48105
FROM:     Charles M. Urban
          Department of Emissions  Research
          Southwest Research  Institute
          6220 Culebra Road
          San Antonio, Texas   78284

SUBJECT:  Submittal of Test Results  for work conducted under Work
          Assignment No.  18,  Contract 68-03-3162,  SwRI, Project 03-7338-018.

          Contract Title:  "Pollution Control Assessment for the Emission
                           Control Technology Division, Ann Arbor, Michigan"
          Assignment No.  18 Title:   "Low Cost I/M Analyzer Study"
I.
INTRODUCTION
     Three "low cost" exhaust  analyzers  were provided to SwRI by the
EPA for evaluation under a  specific  series of tests.  This evaluation
involved measuring various  concentrations  of CO in vehicle exhaust
using a reference analyzer  and  the three "low cost" analyzers.  The
Statement of Work is given  in Attachment A-l.
II.
TEST PLAN
      The test plan  followed was  the same as that given in the Work
Plan for Work Assignment No. 18.   A copy of the technical approach for that
Work Plan is given in Attachment  A-2.   Some additional evaluations, over
and above those given in the Work Plan,  were conducted.

III.  CAR, ANALYZERS, AND MISFIRE UNIT

      The car used was  a 1981 Ford Mustang with a 2.3 liter engine and a
three-way exhaust catalyst.  A commercial grade unleaded gasoline was
used.  The air pump  was disconnected to enable attaining the higher levels
of exhaust CO requested.

      An Electronic  Ignition Misfire unit that had been utilized in
several previous EPA projects was used  in this work assignment.  This
unit was described in the final report  EPA-460/3-80-003.
          SAN ANTONIO. TEXAS
          WITH  OFFICES  IN HOUSTON. TEXAI
                                       AND WASHINGTON. 0 . C .

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      The reference analyzer used was a Beckman 315A Infrared Analyzer
appropriately configured for full scale ranges of 6,3 and 1.5 percent
CO.  It was determined at the start of the testing that use of the 6
percent range was adequate over all the test points.  The use of a
single range greatly facilitated the testing, and was felt to improve
the overall integrity of the results.  Use of a single range enabled
concentrating on those items of greater importance and reduced elapsed
time, which minimized drift for all analyzers used.  The calibration
curve for the reference analyzer is given in Attachment A-3.

      The three exhaust gas analyzers  tested included the following:

      • KAL-EQUIP CO. Model 4089 (Part No. 97-3665)
      • HEATHKIT  Model CI-1080
      • PEERLESS Model 600

Based on the copyright and other dates on the instructions provided, these
analyzers are from the early 1970's.  The sensing element in the Heathkii .
analyzer is a thermistor bead, and it is assumed that the other two analyzers
also utilized thermistor beads.  Such instruments using thermistors measure
the overall thermal conductivity of the gas being sampled and compare those
values with the thermal conductivity of air.

      In the manuals provided, the accuracy of these analyzers was not
given.  However, with the Kal-Equip analyzer, a possible indication of
accuracy was given.  In a factory calibration, a tolerance of plus or
minus three divisions of air fuel ratio (i.e., plus or minus 0.3 air
fuel ratio) was allowed.  Therefore, the tolerance on CO would be plus
or minus one percent CO (e.g., 2.5 to 4.5 percent CO for a value of 3.5
percent).

      Copies of the data sheets developed and used for the evaluations
conducted under this work assignment are given in Attachment A-4.

IV.   TEST RESULTS

      The specified exhaust CO concentrations of 1, 2, 3 and 5 percent were
obtained by adjusting the carburetor idle air fuel mixture.  The air pump
was disconnected throughout these analyses, except when obtaining near zero con-
centrations of CO in the  exhaust.

      Results of the analyses are summarized in Attachments  B-l and B-2.
The averages of the results are resummarized in Table 1 and are shown
graphically in Figure 1.

      The Kal-Equip analyzer was evaluated in one series of tests and the
Heathkit and Peerless analyzers were evaluated simultaneously in a separate
series of tests.  The odd run number evaluations involved starting at the
one percent CO value,and the even run number evaluations involved starting
at the five percent CO values.

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    O  4
    U
    O
    u
       5



       4
                  2    3
         0    1
         0    12     345


             Ref. Analyzer, %CO
Legend: •- W/0 Engine Misfire
                            - 6% Engine Misfire
Figure 1.  Performance o.f. Low Cost Analyzers

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                    TABLE 1.  BRIEF. SUMMARY OF RESULTS
                       Measured CO Values in Percent
Ref.
4..b
0
1
2
3
5
Anal.a
24»b
0
1
2
3
5
Kal-Equip
Base
—
0.4d
1.5*
2.6d
5.7d
Misfire0
—
0.5
0.9
1.3
3.0
Heathkit.
Base
1.5
1.9
2.6
3.3
4.9
Misfire0
—
1.1
1.8
2.4
3.5
Peerless
Base
1.5
1.6
2.1
2.6
3.6
Misfire0
—
2.1
2.4
2.6
3.3
 Set values were generally within plus or minus 0.2 of the values shown.
 There were no significant differences between the measured values at the
.two probe locations.
 Probe location from end of vehicle exhaust pipe.
,Six percent misfire setting.
 Next day repeat values were 0.2, 1.1, 2.1, and 4.7


       For the analyses with the reference analyzer probes at 4 inches  and
 24 inches from the exit of the vehicle exhaust pipe, measurements of the
 initial position were repeated.  The results were than compensated for
 any. drift in the CO concentration.   In no case was there any shift in  the
 value when changing from one probe to the other.  There was, of course,
 an initial blip with the first switch at each exhaust CO concentration.
    •  The set point shifted or drifted as much as one percent CO with the
Kal-Equip analyzer.    A  next day repeat evaluation with the Kal-Equip
analyzer produced measured CO values of 0.2, 1.1, 2.1, and 4.7 percent for
1, 2,  3, and 5 percent exhaust concentrations  After careful setting of
the control on this analyzer, a 0.5 percent CO drift was observed after
five minutes with the probe in room air.

      Not shown on the summaries are the results of some added evaluations
which were conducted. With essentially no CO in the exhaust, the average
readings were 1.5 percent CO with the Heathkit and with the Peerless analyzers.
With a calibration gas containing 9 percent CO in nitrogen, the CO readings
on the Heathkit and Peerless analyzers dropped less than 0.5 percent CO from
the room air set point of 3.5 percent CO (i.e., readings of about 3 percent CO)

-------
It should be pointed out that with room air the analyzers are set to read
3.5 percent CO.  With a 10.7 percent CC>2 calibration gas, the CO readings
on these two analyzers were about 1 percent.
V.
CLOSURE
      This submission of the test results completes all of the requirements
in Work Assignment 18.

Prepared by:
Charles M. Urban
Senior Research Engineer
Department of Emissions Research
Submitted by:
Charles T. Hare
Manager, Advanced Technology
Department of Emissions Research
                                           Karl J./^prdJnger
                                           Director   v
                                           Department of Emissions Research

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                      ATTACHMENTS

A-l  Statement of Work
A-2  Statement of Technical Approach
A-3  Calibration Curve for the Reference CO Analyzer
A-4  Data Sheets

B-l  Results Without Ignition Misfire
B-2  Results With Ignition Misfire

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                                                ATTACHMENT A-l
                      Statement of Work

The testing will consist of  replicate  measurements of vehicle
exhaust  at  several  tailpipe   CO  concentrations  at   idle,
measuring  simultaneously*  with  three   low  cost  CO analyzers
and a  reference  analyzer.**  The  CO  exhaust concentrations
should have values  near  1%,  2%,  3%, and  5%  CO such that each
value  can  be  replicated  to  within  .03% CO  (300  ppm)   (the
reference  CO  meter shall  be  used  for  determining  the  CO
level)  .   The  low  cost  analyzer  shall  be  operated  per the
manufacturers  instructions.   The  reference  analyzer   shall
measure CO at  two  locations;  one at the  same  location as the
shortest low cost analyzer probe,  the  other  location shall be
at  least  20   inches  upstream from the  end  of  the  vehicle
tailpipe  (to  avoid tailpipe  dilution).    The  vehicle   shall
have a 4-  or  6-cylinder engine,  and be  capa&le of producing
the CO levels  indicated  (more  than one vehicle can be used if
desired).  The tests shall  be  run with  a  warmed-up vehicle.
Replicate   the   concentrations    serially,   starting   with
ascending  order,  then  with  descending  order,  and  so   forth
until  five values  are  recorded  at each  level.   Provide TSS
with the upstream  and  downstream CO values  for  the reference
analyzer;  CO  values from  the  low  cost analyzers;  average CO
levels  for each  level,  analyzer,  and location;  and  the CO
standard  deviation  for  each  level,  analyzer,  and location.
Indicate   the  fuel  type   used,   (Indolene  or  commerical).
Repeat  the  above   procedure  using  a  misfire  generator  (6%
misfire) and provide the same data.
*If  the tailpipe  cannot contain  all  of  the  probes without
distributing  the  flow,  reduce  the  number  of  analyzers per
test  ana  repeat  tiie test for the  analyzers  not tested in the
first group.
**The reference  analyzer snail conform  to  and be operatea  in
accordance with  40  CFR 86 Subpart  D  (Heavy-duty  raw  exhaust) .

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                                                          Attachment A-2
II.  STATEMENT OF TECHNICAL APPROACH

     The approach to be taken is as follows:

        • Receive the three low cost CO analyzers supplied by the EPA
          Technical Project Monitor.

        • Check out the CO  analyzers in accord with the  manufacturers'
         instructions, which are  to be provided  by the  EPA along with
         the  analyzers.  Analyzers  meeting the requirements in  the  manu-
         facturers'  instructions  will  be  used in this task;  any analyzer
         not  meeting the requirements  will be dropped from further  evaluation.

        • Using a  vehicle with  a 4-  or  6-cylinder engine,  develop a  method
         for  obtaining tailpipe CO  emissions of  1,  2, 3,  and 5  percent  by
         volume  (±0.3%, or minimum  variation practical).   One of the
         following methods or  a combination will be used:

              -  Idle mixture adjustment

              -  Intake restriction  (i.e.,  choking)

              -  Control of injected air (if and  when a  catalyst is  used)

         It is anticipated that an  oxidation catalyst-equipped  car  will
         be used  for the initial  evaluation.

        • Tailpipe CO readings  will  first  be taken with  the low-cost analyzer
         having  the shortest exhaust probe, and  with the  reference  analyzer.
         The  reference analyzer will have one probe located the same as
         that of  the low-cost  analyzer, and one  probe located at least  20
         inches  upstream from  the outlet  of the  tailpipe.   The  procedure
         will be  as follows:

              -  Warm-up the engine  over an FTP,  by  operating at 40 mph
                 for 15 minutes, or  by  equivalent operation.

              -  Measure exhaust CO  at  idle mixtures producing approximately
                 1, 2,  3, and 5% CO, and then at  5,  3, 2,  and 1% CO.

              -  Clear the  engine  by operating at increased engine speeds
                 for a few  seconds,  and check zero and/or  spans  on the
                 instruments.

              -  Repeat the measurement sequences of exhaust CO.

              -  Clear the  engine, zero, and span.

              -  Repeat the measurement sequence  of exhaust CO from  the
                 1 through  5% values.

              -  Zero and span  the instruments.

              Note:  Idle  is generally not a stable condition,  and  therefore,
                      does  not  generally produce  stable  or repeatable CO
                      values, especially,within  ±0.3 at  the higher CO setting.

-------
                                                  ATTACHMENT A-2 (Cont'd)
              If the CO values become more stable without clearing
              the engine,  the clearing will be omitted.   The engine
              idle speed will not be readjusted at the various CO
              levels as long as the speed remains within reasonable
              limits (i.e.,  within ±100 rpm).   If found necessary,
              the grder in which the idle CO values are measured may
              be altered.

•  Repeat the tailpipe CO reading sequence with the remaining two
  low-cost analyzers (simultaneously, if practical to do so).
  These evaluations will include measurements  with the reference
  analyzer at only one probe location:  at least 20 inches upstream.

•  Review the data to assure it appears reasonable and that there are
  at least four acceptable data points for each condition.

•  Install the available misfire generator on a 4- or 6-cylinder
  engine that does not have a catalyst (can be a catalyst-equipped
  car on which the catalyst has been removed).  With a 6 percent
  misfire setting, develop a method for obtaining the various  tailpipe
  CO emission levels.  Repeat the tailpipe CO  reading sequence with
  the low-cost and reference analyzers, and review the data.

  Note:  The level of effort assumes that the  misfire generator
         still functions properly (it has not  been used in
         approximately two years).   Hydrocarbon readings may
         also be taken if it proves practical  to do so,  but any
         such reading will not be used in determination of
         validity of the data.

•  Tabulate the CO data, and determine the averages and standard
  deviations for each combination of CO level-analyzer-probe location.

•  Record identification data from the cars and the analyzers used,
  and determine the probe locations in the exhaust pipe.  The  fuel
  will be identified by type only;  no analyses of the fuel will be
  conducted.

•  Return or retain the low cost analyzers as subsequently requested
  by the EPA Tehcnical Project Monitor.

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                                         CALIBRATION CURVE  FOR  THE  REFERENCE CO ANALYZER
                                                                                                                     ATTACHMENT  Af 3 „.
CURVE  FIT USING Y=X/(A+B*X+C*X**2+0»X«»3)
  C  U      G/D-2 NDIR  CO
      5/04/1984  RANGE-1
  S/N  201048
0-6  %
DANNY
A=    .3140212E+02   B=  -.1527510E+00

TABULATION USING EQUATION
            C=   -.6650272E-04   D=    .7999959E-07  FULL SCALE=
                                                          6.0
METER
.50
1.00
1.50
2.00
2.50
3.00
3.50
4.00
4.50
5.00
5.50
6.00
6.50
7.00
7.50
8.00
8.50
9.00
9.50
10.00
10.50
11.00
11.50
12.00
12.50
13.00
13.50
14.00
14.50
15.00
15.50
16.00
16.50
17.00
17.50
18.00
18.50
19.00
19.50
20.00
CONC
.02 y
.03 y
.05 y
.06 /
.08 y
.10 y
.11 y
.13 /
.15 /
.16 y
.18 y
.20 y
.21 y
.23 >
.25 y
.27 y
.28 y
.30 y
.32 y
.33 y
.35 y
.37 y
.39 y
.41 y
.42 y
.44 /
.46 y
.48 y
*50 y
.52 >
.53 >
.55 >
.57 /
.59 >
.61 >
.63 >
.65 ,
.67 >
.69 >
.71 t
METER CONC
' 20.50 .73
' 21.00 .75
' 21.50 .77
' 22.00 .79
' 22.50 .81
' 23.00 .83
' 23.50 .85
' 24.00 .87
' 24.50 .89
' 25.00 .91
f 25.50 .93
f 26.00 .95
' 26.50 .97
' 27.00 .99
' 27.50
' 28.00
' 28.50
' 29.00
' 29.50
' 30.00
' 30.50
' 31.00
' 31.50
' 32.00
' 32.50
' 33.00
' 33.50
' 34.00
' 34.50
' 35.00
' 35.50
' 36.00
' 36.50
f 37.00
f 37.50
f 38.00
f 38.50
t 39.00
1 39.50
f 40.00
.01
.03
.06
.08
.10
.12
.14
.17
.19
.21
.23
.26
.28
.30
.32
.35
.37
.39
.42
.44
.47
.49
.51
.54
.56
.59

/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
METER CONC
40.50
41.00
41.50
42.00
42.50
43.00
43.50
44.00
44.50
45.00
45.50
46.00
46.50
47.00
47.50
.61
.64
.66
.69
.71
.74
.77
.79
.82
.84
.87
.90
.92
.95
.98
48.00 2.01
48.50 2.03
49.00 2.06
49.50 2.09
50.00 2.12
50.50 2.15
51.00 2.17
51.50 2.20
52.00 2.23
52.50 2.26
53.00 2.29
53.50 2.32
54.00 2.35
54.50 2.38
55.00 2.41
55.50 2.44
56.00 2.47
56.50 2.50
57.00 2.53
57.50 2.57
58.00 2.60
58.50 2.63
59.00 2.66
59.50 2.69
60.00 2.73

/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
/
METER
60.50
61.00
61.50
62.00
62.50
63.00
63.50
64.00
64.50
65.00
65.50
66.00
66.50
67.00
67.50
68.00
68.50
69.00
69.50
70.00
70.50
71.00
71.50
72.00
72.50
73.00
73.50
74.00
74.50
75.00
75.50
76.00
76.50
77.00
77.50
78.00
78.50
79.00
79.50
80.00
CONC
2.76
2.79
2.82
2.86
2.89
2.93
2.96
2.99
3.03
3.06
3.10
3.13
3.17
3.21
3.24
3.28
3.32
3.35
3.39
3.43
3.47
3.51
3.54
3.58
3.62
3.66
3.70
3.74
3.78
3.83
3.87
3.91
3.95
3.99
4.04
4.08
4.12
4.17
4.21
4.26
METER
f 80.50
f 81.00
f 81.50
f 82.00
f 82.50
f 83.00
/ 83.50
/* 84.00
/ 84.50
/ 85.00
/ 85.50
/ 86.00
/ 86.50
/ 87.00
/ 87.50
/ 88.00
/ 88.50
/ 89.00
/ 89.50
1 30.00
/ 90.50
/ 91.00
/ 91.50
/ 92.00
/ 92.50
/ 93.00
/ 93.50
/ 94.00
/ 94.50
/ 95.00
/ 95.50
/ 96.00
/ 96.50
/ 97.00
/ 97.50
/ 98.00
/ 98.50
/ 99.00
/ 99.50
/ 100.00
CONC
4.30 /
4.35 /
4.39 /
4.44 /
4.49 /
4.53 /
4.58 /
4.63 /
4.68 /
4.73 /
4.77 /
4.82 /
4.88 /
4.93 /
4.98 /
5.03 /
5.08 /
5.13 /
5.19 /
5.24 /
5.29 /
5.35 /
5.40 /
5.46 /
5.52 /
5.57 /
5.63 /
5.69 /
5.75 /
5.81 /
5.87 /
5.93 /
5.99 /
6.05 /
6.11 /
6.18 /
6.24 /
6.30 /
6.37 /
6.43 /
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-------
                                                                  ATTACHMENT A-4
                                                                      Sheet 1 of 2
                              LOW COST. I/M ANALYZER STUDY
                               SwRI Project 03-7338-018
                                  Date
                                                     By
ANALYZERS:

  Calibration Check O.K.:

    KAL-EQUIP [""I

    . Connect to  Battery
    .-•Adj.  Set Control
                            HEATHKTT
PEERLESS ||
       Yes I

AUTOMOBILE:

  Year
                No I     I
                              Connect to Battery
                              Balance Meter
                                Yes |    | No 1    |
  Balance Meter
  Adj. Set Pointer
  Turn ON and Balance
. Adj. Set every 15 min.
            |  Nc|    I
Yes
               Make
                                            Model
Engine CID Q.,3

Fuel Used: Uj
                         Catalyst:  None |     |   Oxid.'l    |   3- way | X I

                         G**t>o\ /*.€-            •
CO MEASUREMENTS  IN  PERCENT:

  Misfire Setting:  None
                            6%
   . Warm-up  engine  -  15  minutes  at 40 mph,  or equivalent.
Set
% CO*
1
2
3
4
5
5
.4
3
2
1
Ref. Anal.
4"










24"










Kal-
Equip










Ref.
24"










Heath-
Kit










Peer-
less











































* +_0..3%, or minimum variation practical.
                               Continued

-------
                                                                 ATTACHMENT  A-4  (Cont'd)
                                                                    Sheet 2 of 2
 Misfire Setting:  None
6%
 .  Clear Engine at increased speed.
 .  Check calibration of all instruments
Set
% CO*
1
2
3
4
5
5
4
3
2
1
Ref. Anal.
4"










24"










Kal-
Equip.










Ref.
24"










Heath-
kit










Peer-
less











































 .  Clear Engine at increased speed.
 .  Check calibration of all instruments.
Set
% CO*
I
2
3
4
5
5
4
3
2
1
Hef. Anal.
4"










24"










Kal-
Equip.










Ref.
24"










Heath-
kit










Peer-
less



























,















 .  Check calibration of all instruments.
*+_ 0.3%,  or minimum variation practical.

-------
RESULTS WITHOUT IGNITION MISFIRE
                                         ATTACHMENT B-l
   LOW COST  I/M ANALYZER  CO  RESULTS
   Misfire Setting:  None  /X /6%/7

Set % CO
Run 1
Run 2
Run 3
Run 4
Run 5
Run 6
Average
Std. Dev.

Ref . Anal, at 4"
1
/. /
0.1
• I.D
o.%
/•I
I.D
(,D
O.I


2
£.0
2J
2.2
3.0
3.2
£.0
£.1
0. I


3
3.1
3.0
3.0
3.1
3.1
23
3.0
o, 1













5
42
4.1
3.1
f.O
f.!L
f.Si
f.O
o.Z


Ref. Anal, at 24"
1
/./
0.9
1.0
*t
/./
l.t
1.0
O.I


2
3.0
3.1
J..Z
3-°
&•*-
2.0
3.1
l
3.1
3.g
3.0
O.I













5
4.9
q.%
/./
f.o
£&
5-.Z
S.o
Q.&


Kal-Equip.
1
0.1
o.f
.o
&.&
$'7
0,^


»
Set % CO
Run 1
Run 2
Run 3
Run 4
Run 5
Run 6
Average
Std. Dev.

Ref. Anal, at 24"
1
Q-*
o.t
1,1
0.9
/./
&.$
0.1
O.I


2
/'$
2-1
J.b
1-9
1.1
2.0
2.0
O.I


3
J.O
3*0
*9
3.0
j,a
3.0
J.o
OJ













5
J.o
f.3
j.O
f>l
f.JU
'f.l
S'/
OJ


Heathkit
1
a.o
1.9
/.1
z.l
l.l*
$.0
1.1
0,0,


2
*1
2-b
J.+
J.b
*•₯
*7
2,b
S.I


3
3.*
3.4
3. 1
3.(*
3.2,
3.3
3.5
0.5L













5
*7
J.o
•*1
.S,f
4.1
M
W
0.3














Peerless
1
/r
/,&>
1,1*
/.s
1.6
/.b
{>(?
Q,l


2
1.?
3.3
2.0
2.3
2-1
c2J
2, 1
0.3


3
*r
3.V
J.S*
2.2
A.tff
3.?
3.b
D, 1













5
3*?
3.1
5.
-------
RESULTS WITH IGNITION MISFIRE
                                       ATTACHMENT  B-2
LOW COST  I/M ANALYZER CO RESULTS
Misfire Setting: None /  /6%/X/

Set % CO
Run 1
Run 2
Run 3
Run 4
Run 5
Run 6
Average
Std. Dev.


Ref. Anal, at 4"
1! 2




















3





















5










Ref. Anal, at 24"
1
/.a.
/.D
1.3.
/.I
1,2
/.D
I.I
D.(


2
2.1
• Z.O
3..I
/.1
3-f
2.3
*1
O.I













5
4.0
4.1
f.a.

4.f
S.I
S,/
£.1
*3
/./
Q.(f


2
3.C
1.3.
/.iff
2.3.
1.9
/.r
/.z
0,^


3
3.0
j?.r
2.Z
2.Z
J-2
J.O
2.4
o.^













5
3.X
s.₯
'3.?
J.f
3,3
3.?
3.4
0,Z


Peerless
1
z.o
z.o
a.o
a.)
3.2
J./
3.1
O.I


2
A*
*-3
*₯
j-t
J.3
J-₯
2.4
#,/


3
a. 7
£.(0
£.(0
3-7
J.b
j.b
Z.I*
°-(













5
3.3
3-3
3.2.
3.3L,
3.ZL
3-3
3.3
0,1



-------