EPA-AA-SDSB-82-10
                         Technical Report
               Testing of the Mack ETSA-676 at MVEL
                                by


                            Alex Azary
                            April 1982
                              NOTICE

Technical Reports do not necessarily represent final EPA decisions
or positions.  They are  intended to present technical analysis  of
issues using  data  which are  currently  available.   The  purpose  in
the  release  of  such  reports is  to  facilitate the  exchange  of
technical  information  and  to  inform  the  public  of   technical
developments which may form  the basis for  a  final EPA decision,
position or regulatory action.
             Standards Development and Support Branch
               Emission Control Technology Division
          Office of Mobile  Source Air Pollution Control
                Office of Air,  Noise and Radiation
               U.S. Environmental Protection Agency

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                         Table of Contents




Section                                                        Page




I.   Summary	1




II.  Introduction 	   1




III. Test Results and Correlation With Other Labs	2




IV.  Analysis of Testing Problems 	   3




V.   Conclusion	4




VI.  Recommendations	4

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I.   Summary

     The Mack ETSA-676 heavy-duty diesel  engine  has  been tested  at
EPA as  part  of  the EMA/EPA  testing  program.   The purpose  of  this
program  is   to  analyze   lab-to-lab  variability  in   emissions
measurements and  to assess how well  the emissions  data generated
at  EPA correlates  with data  acquired  through  testing at  other
laboratories.   This  engine was scheduled to  be tested  in  turn  by
Mack Trucks, Inc.  (Mack),  Caterpillar Tractor Co. (Cat), and  EPA,
and then to be returned to Mack for the  final tests  on this engine
as part of the program.

     EPA's   correlation  with  other  labs   has  been   generally
acceptable   with   a  tendency  to   somewhat   higher   particulate
measurements in comparison  with  those  of  other  labs.   This was
reviewed in  detail  in  other  reports[l,2]  and  will not be  dealt
with further here.

     EPA's transient test  particulate measurements for  this engine
were 7.8 percent  higher  than Mack's and  31.12  percent  higher  than
Cat's:   .77,  .71,  and .53  g/BHP-hr,  respectively.  The transient
values   for  NOx were  25.2  percent  higher than Mack's and  19.3
percent  higher  than  Cat's:   8.45,  6.32,   and  6.82   g/BHP-hr,
respectively.   The HC  emissions measurements  at   EPA  were  49.1
percent lower than Mack's  and  28.1 percent  lower than  Cat's:   .57,
.85, and .73 g/BHP-hr, respectively.

     Steady-state emission values did not follow the  same  pattern
as   the  above   listed   transient    test  data.    EPA's   13-mode
particulate measurements were  53.5  percent  higher than  Mack's and
20.9 percent  lower  than   Cat's:   .86,  .40,  and  .68  g/BHP-hr,
respectively.   NOx  measurements  were  8.5  percent  higher  than
Mack's   and  19.2 percent lower than  Cat's:   6.83,   6.25, and  8.14
g/BHP-hr,  respectively.  HC emissions were 20.8  percent  lower  than
Mack's   and  8.3 percent  lower  than  Cat's:    .48,  .58,  and  .52
g/BHP-hr,  respectively.

     Mode  6 and Mode 11 particulate emission  measurements were not
reported by  Mack  and  the only comparison made is between  Cat and
EPA.   Cat  particulate measurements  were 22.4  percent  lower  than
EPA's in Mode 6 and 58.0 percent higher than EPA's in Mode 11.

     The engine has been returned to Mack for  the  final  test  in
the  schedule  and  in  view  of  the  somewhat  inconsistent  data
generated  by this  engine at the labs involved,  a  final  evaluation
of  correlation  should  be  delayed   pending  review of  the  data
forthcoming from Mack's second test  series.

II.  Introduction

     This  report is one of a series of reports presenting results,
analysis and conclusions  of testing  heavy-duty diesel  engines  at

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the EPA's  Motor Vehicle  Emission Lab  (MVEL).   These engines  are
tested in  both  transient  and steady-state modes and  the  resulting
data  is  compared with  that  of  other  test  labs  to  determine  the
amount of variability between labs.

     This  report   discusses  the  results   of  testing  a   Mack
heavy-duty  diesel  engine,  model  ETSA-676.   Reviewed  are  some
problems encountered  during  the course  of  testing  the engine  and
the  procedures  followed  to   isolate  and  solve   the   problems
satisfactorily.   Finally,  recommendations for  improved  procedures
will be presented.

III. Test Results and Correlation With Other Test Laboratories

     A  series  of  transient  tests  were  run on  this engine  from
November 16,  to December  1,  1981, at  which time the  particulate
measurements inexplicably  rose  from a  range of .553  to  .837  grams
per BHP-hr to values  of 1.046+ grams per BHP-hr.  The  testing  was
stopped while propane  checks  were initiated to  detect leaks  and
the components in the system were  checked.   A leaking thermocouple
fitting in the  mini-tunnel,  a  cracked  sampling line  and  secondary
dilution air inlet  temperature variations  all  contributed to  the
erratic readings and were corrected.

     Testing was resumed with more  consistent performance  and data
were  processed  and compared with  that  of  other  labs.    The  test
results from the three  labs  involved in  testing the  Mack  ETSA-676
engine are  shown in  Table 1.    Shown  are composite  emissions  for
transient  tests,  and  13-mode  steady-state  emissions.   Table  2
shows the detail of the data summarized  in  Table 1.   Table 3  lists
the cycle  performance  data  for  the  tests, indicating   that  all
tests listed were valid.

     Examining  the  data  in  Table  1,   the  values for  NOx  differ
substantially among the three testing  labs  using EPA's values as  a
base:    Cat:transient   -19.3  percent,*  13-mode  +19.2   percent;
Mack:transient -25.2 percent, 13-mode -8.5 percent.

     In contrast,  other's measurements  of  HC  emissions   are  well
above  those  of  EPA:    Cat:transient +28.1  percent,  13-mode  +8.3
percent; Mack:transient +49.1 percent,  13-mode +20.8  percent.

     The values for particulates  show  an even  greater  dispersion:
Cat:transient -31.2 percent,  13-mode -20.9  percent;  Mack:transient
-7.8 percent, 13-mode -53.5  percent.   As was noted earlier in  the
report, the particulate measurements at EPA are higher than  those
of other labs.
       ^-,-r          x Mfr - x EPA   ,nr.
       Difference =  	—	 x 100
                          x EPA

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IV.  Analysis of Testing Problems

     As a result  of  experience gained in testing  the  baseline  and
other engines,  a  set of  recommended  procedures was  set  up to  be
observed during  subsequent testing of  heavy-duty engines.   These
procedures were followed  during the  testing  of this  Mack  engine.
There  were,  however,  some   problems   incurred   which   at  times
required  tests  to  be  voided.   As  mentioned  above,  a  set   of
transient  tests  was invalidated   because  of  a  sudden  rise   in
particulate  measurement.   A  series  of   propane   leak  tests were
performed  to  identify   the   cause(s).   Among   items found   and
corrected were:

     1.    Leaking thermocouple fitting on mini-tunnel - sealed.

     2.    Sample line split at fitting - repaired.

     3.    Inlet and outlet temperatures  running  higher than spec.
- increased length of sample lines.

     4.    Outlet from  exhaust DGM was  within  6" of  inlet  to  DGM
- relocated exhaust DGM to vent to air handling system.

     5.    Scrubbed main tunnel.

     6.    Inspected all lines and fittings.

     7.    Verified calibration of all components.

V.   Conclusion

     Although  previous   engines   tested  at  EPA  had   exhibited
particulate measurements  higher than those measurements  at  other
labs, the inconsistent values  obtained from this  engine at  EPA  and
Caterpillar  preclude any valid  conclusion  being drawn  at this
time.   The   HC  and  NOx  values  are  also  without  a  predictable
pattern.

VI.  Recommendations

     Any  final  evaluation of  test  data  produced  from  previous
tests of  this  engine should  be  withheld until  the  second  set  of
tests  being  conducted  by Mack  are concluded.   The  results from
these  tests  should  then   be  reviewed  and evaluated  against  the
previous  test  data  produced  at  all  labs  involved with this
engine.  At this time it  may  be  determined  if indeed the  engine  is
erratic  in   performance  or  our labs  have  other problems  to  be
isolated and solved.

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                            References

     1.    "Emissions  Testing  of  a  DDA  6V92TA Heavy-Duty  Diesel
Engine    Under    Transient    Conditions,"    Danielson,    Eugene,
EPA-AA-SDSB-80-16, September 1980.

     2.    Emissions Testing of  an IHC DTI-466B Heavy-Duty  Diesel
Engine    Under    Transient    Conditions,"    Danielson,    Eugene,
EPA-AA-SDSB-80-18, September 1980.

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                             Table I

            Summary of Mack ETSA-676 Emissions Tests
                            (g/BHP-hr)

Test
Mack

Cat



EPA


[1]
m


NOx


Site Stat Trans. [1] 13-Mode Mode 6 Mode 11
X
s
s/x x 100
% Diff.[2]
X
s
s/x" x 100
% Diff.[2]
x
s
s/x x 100
Composite C/S-H/S
•
% rHfferpnrp -
6.32
.430
6.8%
-25.2
6.82
.163
2.4%
-19.3
8.45
.265
3.1%
data.
x~ Other -
6.25
.040
.6%
5.30
.057
1.1%
5.70
.311
5.5%
-8.5 -25.8 -11.2
8.14
.387
4.7%
+19.2
6.83
.997
14.6%
x~ EPA
•x
7.60
.255
3.4%
+6.4
7.14
.634
8.9%
100
6.89
.471
6.8%
+7.3
6.42
.382
6.0%


Trans. [1]
.85
.118
13.8%
+49.1
.73
.007
1.00%
+28.1
.57
.064
11.2%

HC


13-Mode Mode 6 Mode 11
.58
.005
.8% 9
+20.8 +520
.52
.055
10.6% 1
+8.3 +20
.48
.020
4.2% 7

.062
.006
.7%
1.39
.057
4.1%
.0 -2.1
.012
.016
.3%
.0
.010
.0017
.0%

1.42
.103
7.2%
0.0
1.42
.021
1.5%


Trans. [1]
.71
.033
4.6%
-7.8
.53
.150
28.4%
-31.2
.77
.030
3.9%

Part.


13-Mode Mode 6 Mode 11
.40
.010
2.5%
-53.5
.68 1
.069
10.1% 10
-20.9 -20
.86 1
.094
10.9% 1

-

.35
.141
.5% 2.
.9 +58.
.74
.020
.1%



79
019
4%
0
50



x EPA

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Transient
Emissions
NOx




HC




Part







Cold x
Hot x
Comp x
Hot_ S
s/x x 100
Cold x"
Hot x
Comp x
Hot S
s/x x 100
Cold x"
Hot x
Comp x
Hot S
s/x x 100
Table 2
Test Site

Mack
6.06
6.83
6.32
.390
5.7%
.99
.78
.85
.066
8.5%
.70
.66
.71
.019
2.9%


Cat
7.04
6.68
6.82
.156
2.3%
.80
.74
.73
.015
2.0%
.66
.56
.53
.059
10.5%


EPA
8.80
8.39
8.45
.296
3.5%
.64
.56
.57
.064
11.4%
.83
.76
.77
.027
3.6%
Filter Efficiency
             x                98.0            98.0           98.2
             s                  -              0.95           2.19

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                   Table 3
EPA/MVEL Mack ETSA-676 Cycle Performance Data
Type/
Limit




C/S
H/S
C/S
H/S
C/S
H/S
C/S
H/S
C/S
H/S

Error
100



35.2
34.3
34.7
34.2
34.7
34.8
34.8
34.5
34.6
34.4

Slope
.970-
1.030


.980
.980
.979
.980
.973
.972
.974
.974
.970
.969
Speed
y- Intercept
+50 RPM .97



24.1
26.0
18.7
17.6
13.9
12.7
26.4
26.5
1.04
1.88
Torque
R2
min



.995
.995
.995
.996
.995
.995
.995
.995
.995
.995
Error
13% .
of Max
Torque

6.4
6.4
6.6
6.6
6.5
6.3
6.4
6.2
6.4
6.4
Slope
77/.S3
1.03
Cold/
Hot
.986
.978
.987
.980
.993
.990
.991
.990
.991
.983
y-Intercept
+15# ~.



5.48
8.35
-2.63
-1.01
-2.9
-1.5
-9.81
-1.121
-2.78
-0.78
R2
85/88
min
Cold/
Hot
.942
.943
.936
.936
.942
.945
.942
.946
.942
.944
Error
8%
of Max
HP

6.5
6.4
6.7
6.7
6.5
6.4
6.5
6.4
6.4
6.4
Slope
S7/.89
-1.03
Cold/
Hot
1.02
1.02
1.01
1.00
1.00
1.00
1.01
1.01
.991
.987
HP
y-Intercept
+5.0 BHP .91



-1.09
-.787
-2.26
-2.15
-2.2
-2.1
-1.90
-1.84
-2.19
-2.02

R2
min



.955
.956
.950
.949
.954
.955
.953
.956
.953
.954
Integrated
HP-Hr
-15% to
+5% Ref.


1.01
1.02
.981
.986
.978
.986
.991
.998
.964
.970

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