EPA-AA-SDSB-80-12
                           Technical Report
         Evaluation of the Contamination Effects  of  Diesel Exhaust
                     on a Critical Flow Sample  System
                                  by


                           Eugene Danielson




                               May 1980
                                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  devel-
opments 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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Abstract

     Testing has been  conducted  to determine 1) the effectiveness
of complete diluted  diesel  exhaust stream filtering in preventing
contamination  of a  CFV  sample system,  and 2)  the  effect  of this
filtering on diesel  gaseous  emission meaurements.    Contamination
was evaluated by observing  the repeatability of gaseous emissions
measurements from  a gasoline  vehicle  which  was  operated  between
each of several  diesel  test  sequences.   Special  attention was given
to detecting hydrocarbon contamination by  1) measuring the concen-
tration of injected propane  (between diesel  tests), and  2)  by
comparing concentrations of hydrocarbons in background air sampled
through  the CFV (exposed)  sample  system  to  the  measured  concen-
trations  of  hydrocarbons  in background  air  sampled  through  the
background (unexposed)  sample system. These latter comparisons were
also made between diesel tests.

     The effect of  exhaust  stream filtering on the  levels  of CO,
C02 and  NOx  in diesel  exhaust  was determined  by  comparing  these
levels with and  without filtering.

     The results of  this testing indicate that  complete filtering
of diluted diesel  exhaust  immediately before the CFV inlet  is
effective  in  preventing  CFV  contamination.    Further,  filtering
of the  diesel exhaust before the CFV inlet does not appear  to
effect  the measured  levels  of CO, C02  and NOx  in diesel exhaust.
(HC is measured  before  the  CFV filter.)

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Introduction

     EPA's  new  interim transient  heavy-duty  diesel  site  at MVEL
(Ann Arbor) will utilize a CFV sample system.   Considerable concern
has  been  expressed  about  the  possibility of  contaminating this
sample system with  the heavy hydrocarbon and particulate material
contained  in diesel  exhaust.   The  only  known  laboratory where an
unproteded CFV is used  for  diesel  testing is the DOT  laboratory in
Cambridge,  Massachusetts.    Conversation with  personnel  at that
facility  indicate  that the main  CFV nozzle must  be  cleaned once
every  four hours  (test  time) in  order  to maintain  a  valid flow
calibration.  Such frequent cleaning would dramatically delay test
programs at MVEL, and hence, an alternative was  sought.

     Other laboratories  (notably GM labs)  filter  the  complete
exhaust stream when testing diesels on  a  CFV system.   This  is known
as bulk  stream  filtering,  and has  the advantage  of directly pro-
tecting the CFV system from diesel particulate  contamination.  This
means  that  potential  periodic shut downs for  nozzle cleanings can
be eliminated.

     However,  data  providing information on  the  effectiveness of
the  concept were  not  available.   In addition,  it was  unknown
whether or not  bulk  stream filtering of  the  diesel exhaust would
affect the measured  levels of the  bagged  emissions  (CO,  C02, and
NOx).   Therefore,  a  test  program aimed  at evaluating  the  effec-
tiveness  of bulk  stream  filtering and  its  impact on  the  bagged
emissions was  conducted using the  part  scale double-dilution  system
(i.e., a  light-duty  vehicle operated on  chassis dynamometer and a
350  cfm  CFV unit  connected  to  the primary  tunnel of  a  double-
dilution system).

Objective

     This  study  was conducted primarily to evaluate the effective-
ness  of  using  bulk  stream  filtering  to  protect  a CFV sample
system when testing diesel vehicles. A secondary objective of this
study  was to  obtain  an  indication  of the impact  of bulk  stream
filtering on the bagged diesel exhaust  emissions.

Test Procedure

     Before an analysis and discussion of the data is presented, a
detailed  description  of the test  sequence and equipment is  neces-
sary.

     Events 1 through  4,  listed  in  Table  1,  indicate the general
test sequence and  corresponding CFV  configuration used to  evaluate
contamination  (primary  objective).   The  basic  philosophy used in
this program was to expose the CFV to diesel exhaust  (Event 1), and
then  measure  the  effect on gasoline vehicle emissions (Event
2).   In  addition,  propane and background hydrocarbon samples were
taken  to  provide  additional  check on  hydrocarbon  contamination

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in  the  CFV.   After establishing  a baseline  of gasoline  vehicle
emissions and  propane  levels,  and  taking initial background mea-
surements,  it  was intended to repeat  the  sequence  five times
without interruption.

     However,  at  the  end of  the second  sequence,  it was  apparent
that  the  CO and  HC emissions  from the  gasoline  vehicle  (a 1976
Chevette) were not repeating.  It was suspected that  this  was being
caused by a malfunction  in the  "hot  stove" valve that controls  the
flow  of  heated  manifold air  entering the  carburetor.    However,
possible contamination could not be ruled out.   Some confirmatory
testing  was necessary.   This  confirmatory  testing  consisted   of
measuring  the   emissions  from  another  vehicle  (a  1977  Chevette)
using an  unexposed (to  diesel  exhaust)  CFV and  then subsequently
measuring its emissions using the exposed CFV.   With this  vehicle,
there were  essentially  no  differences in  the levels  of  measured
emissions between  the  two CFVs.   It was  concluded from this, that
the CO and HC nonrepeatability was  vehicle related.   Therefore,  the
1977 Chevette was used to finish the testing.

     This final series  of tests with the  '77  Chevette provided data
which were used to evaluate  diesel  contamination of  the CFV.  This
was the primary objective of  the study.   A  secondary objective  was
to  quantify the  effect  of  bulk stream  filtering  on  the bagged
diesel emissions  (CO,  C02,  and NOx).   This  evaluation  consisted
of  comparing filtered  diesel  exhaust emission  levels to unfiltered
diesel exhaust  emission  levels.   The  filtered  exhaust  data came
from  measurements  taken  during  Event  1.   The unfiltered  exhaust
data  came  from  measuring the bagged emissions during  a series  of
tests in which  no  bulk stream filter was used.   These nonfiltered
exhaust  measurements were  taken  using a  conventional PDP-CVS
because it  was  expected  that unfiltered diesel  exhaust would very
likely contaminate a CFV  system.

Results

     Contamination Evaluation

     The  emission  levels of the  two  Chevettes  plus  the  propane
injection and background levels are presented  in Figures  1, 2,  and
3.  All of  the  gasoline  vehicle  emission  levels  were measured over
the hot LA-4 cycle.

     Any contamination of the CFV by diesel  exhaust was expected to
primarily affect  HC measurements.   In  this   regard, the  HC data
presented in Figure 1  is of  primary  interest.   This  data  indicates
that  there  is no HC contamination of the  CFV  system  as measured by
any of the  comparisons available.   The measured HC  levels  of both
Chevettes remained  unchanged (except  for  the second sequences  of
the 1976 Chevette discussed  in the  test procedure section)  through-
out the  complete  sequence  of events.   Similarly,  the measured  HC
level during propane  injections also remained constant.   Finally,

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                                -5-

the background EC  levels  sampled through the  CFV  sample  line are
essentially equal  to  the  background  HC levels sampled through the
background line.   This is  significant because  the sample lines were
exposed to the diesel  exhaust  while  the background lines  were not
exposed to diesel  exhaust.    From these comparisons,  it  was con-
cluded  that  there  were no  residual diesel  hydrocarbons  contam-
inating the CFV sample system.

     Exposing the CFV sample system to  filtered diesel exhaust was
not expected  to  have any appreciable  effect  on the  CO,  NOx, and
CC>2 gasoline vehicle  measurements.   The data  presented in Figures
2 and  3 confirm  that these measurements were in  fact unaffected.
That  is,  there were  no steady  trends  (either increasing  or de-
creasing)  in  these measurements.   If  there had been deterioration a
definite trend should have  appeared  for the  number  of tests that
were conducted.

     Effect  of Bulk Stream  Filtering on Diesel Emissions (CO, NOx,
     and CC-2)

     The question has been raised as to whether or not bulk  stream
filtering affects  the measurements of CO,  NOx,  and C02  in the
diesel exhaust.  To help address  this question, measurements  of the
CO,  C02 and  NOx  levels in  the  filtered exhaust  were taken  during
the diesel events  (Table  1).   Immediately after  the contamination
evaluation testing was  completed, unfiltered  exhaust gaseous
emission  measurements were made using a conventional PDP-CVS.
Table 2 presents  a comparison  of  the  filtered  exhaust to unfiltered
exhaust levels  of CO, C02 and NOx.   From  this  comparison,  it
appears that  there is no appreciable change in the measured  bagged
emissions  levels.

     It should be  noted that hydrocarbon and particulate measure-
ments  were also  taken during both the CFV and  PDP-CVS  diesel
testing.   These  measurements  were taken in order  to quantify the
respective errors due to non-proportional sampling  (i.e., using the
CFV without  a  heat exchanger).   The analysis and  results of this
testing are  presented in a  yet  to be  published  Technical   Report
entitled  "Hydro-carbon  and  Particulate Sample Errors  Due  to Non-
Proportional  Sampling".

Discussion and Conclusion

     The  results  stated  previously indicate  that there  was no
apparent  contamination  of  the  CFV sample system  from diesel ex-
haust.   Contamination of  the CFV  sample  system would have been
expected to  be cumulative.   However, none of the  Chevette  tests,
nor any of the propane and background measurements  indicated any

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                                 -6-


contamination.    The bulk  stream filtering  seems  to have  suffi-
ciently  deterred contamination.   In addition, the bulk stream
filtering of the  exhaust  did not  appear  to have  any  appreciable
effect on the measurements  of  diesel CO,  C02 and  NOx.   Therefore
it was concluded  from  this  testing that bulk stream  filtering  is
one viable  method  of  protectng a CFV sample unit  from diesel
exhaust contamination.

Recommendat ion

     It  is  recommended  that bulk stream filtering be allowed  for
use in  protecting CFV  sample  systems from  diesel  contamination.

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                                    -7-

                             Table 1

                 CFV Diesel Contamination Testing
                 	Sequence of Events	
Event
Sample Type
           Diesel Vehicle Testing
           (4-Bag FTP + 2 Hot LA-4s)
CFV Configuration
                       CFV connected to 18-inch tunnel
                       per FR Vol.44, No.23, Feb. 1, 1979
                       Figure B81-4 except: 1) no heat
                       exchanger and 2) a bulk stream
                       filter was installed between the
                       dilution tunnel and the CFV.
           Gasoline Vehicle Testing
           (2 LA-4s) I/
                       Standard light-duty set-up per FR
                       Vol. 42, No. 124, June 28, 1977,
                       Figure B78-2.
           Propane Injection
           (Replicate samples)
           Background HC Check;
           Replicate samples taken
           with main CFV sample
           system and with back-
           ground sample system.
I/   For the initial baseline testing, 3 LA-4s were driven.

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                             Table 2

                   Gaseous Emissions Test Comparison

                            Peugeot 504D
                       Hot LA-4 Driving Cycle

                                    CO              C02            NOx
	Measurement System	      (gm/mi)         (gm/mi)        (gm/mi)  	

Unfiltered Exhaust - PDF          1.36 _+ 3.7%     361 _+ 2.7%     1.26 +_  2.0%
CVS connected to 18-inch
dilution tunnel per FR Vol.
44, No. 23, Feb. 1, 1979,
Figure B81-3.
Filtered Exhaust - CFV            1.42 +_  1.1%     367 +_ 1.6%     1.26 +_ 3.1
connected to 18-Inch
dilution tunnel per FR Vol.
44, No. 23, Feb. 1, 1979,
Fig. B81-4 Except: 1) No
heat exchanger, and 2) A
bulk stream filter was
installed between dilution
tunnel and CFV.
Difference                         + 4.4%             +  1.7%
NOTE:     1)  The bulk stream  filter was  changed after  each  diesel
              test sequence;

          2)  The pressure drop across  the  filter was monitored
              during all CFV diesel testing to  be sure  that  the
              upstream CFV pressure did not change  too  much.   (A
              large change in  this pressure would effect  the CFV
              flow rate).  The maximum  pressure drop observed was
              only 1 inch I^O.  This small  pressure change would
              have a negligible effect  on the CFV flow.

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              -9-
      SYMBOLS  — ABBREVIATIONS
       -   Denotes  tests  with  CFV sample  unit
          exposed  to  diesel exhaust.
       -   Denotes  tests  with  CFV  sample  unit  not
          exposed  to  diesel exhaust.
T5T5   -   Denotes  Diesel  Test  Sequence

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