United States
                                Environmental Protection
                                Agency
                                Environmental Monitoring Systems- ,'-,  "•'"
                                Laboratory                  * p£  A
                                Research Triangle Park NC 27711    fi\*
xvEPA
                                Research and Development
                                EPA-600/S4-82-062  Oct. 1982
Project  Summary
                                Techniques to  Measure
                                Volumetric  Flow  and
                                Particulate Concentrations  in
                                Stacks  with  Cyclonic  Flow
                                J. Douglas Sterrett, Allen R. Barbin, Joe W. Reece, W. Glenn Carter,
                                and Bruce B. Ferguson
                                  The ability of a venturi to accurately
                                measure volumetric flow in cyclonic
                                flow  situations  was examined. A
                                mathematical  model,  which  was
                                developed to describe the effect of the
                                venturi  on  the flow,  correctly
                                predicted the  intensification of the
                                swirling motion in the venturi throat
                                and the  acceleration of the  axial
                                velocity component in the core of the
                                flow  field. Experimental  results
                                showed  that  the  venturi  can
                                accurately measure volumetric flow,
                                even in the presence of fairly strong
                                swirling flow. An analysis of the effect
                                of a venturi on particulate distribution
                                showed that, even though the venturi
                                converging section directed particles
                                toward the center  of the venturi
                                throat, the intense swirl present in the
                                venturi throat quickly convected the
                                particles back to the wall.
                                  Both egg crate and e'toile devices
                                were  evaluated to determine their
                                ability to  straighten swirling flow. It
                                was found that the egg crate flow
                                straightener  would  effectively
                                straighten  swirling flow when  the
                                length of the straightener was equal to
                                or greater than its cell size. It was also
                                determined that significant energy
                                savings could result if cyclonic flows
                                were straightened at the base of tall
                                stacks.  Empirical equations were
                                developed to predict the head losses
                                for the various egg crate assemblies
                                that were studied. A field study to
                                determine the effect of an egg crate
                                device  on particulate distribution
                                across the stack  gave inconclusive
                                results.
                                  This  Project  Summary  was
                                developed by EPA's Environmental
                                Monitoring  Systems Laboratory,
                                Research  Triangle  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

                                 Cyclonic flows  are frequently
                                encountered in the exhaust  stacks of
                                stationary sources which come under
                                present  Federal and  state  emissions
                                regulations. Particles in a cyclonic flow
                                are  subject  to   a  strong radial
                                acceleration  field   and  many  are
                                convected to the stack wall where they
                                cannot be quantitatively collected with
                                conventional  sampling techniques.
                                Mitchell  et al.* suggested that an in-
                                stack  installed venturi by itself might
                                •Mitchell, W J , B. E Blagun, D. E. Johnson, and
                                M R. Midgett. Angular Flow Insensitive PitotTube
                                Suitable for Use with Standard Stack Testing
                                Equipment  EPA-600/4-79-042, U.S. Environ-
                                mental Protection Agency, Research Triangle Park,
                                NC, 1979

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straighten   cyclonic  flow  and
redistribute the particulate sufficiently
to sample it with conventional methods
such as EPA Method 5.
  The initial objective of this study was
to determine the validity of this theory
through  laboratory  and  field
measurements. The  results showed
that the venturi was not adequate  for
this purpose. Thus, additional work was
conducted to  evaluate the  ability of
other devices such as low-pressure drop
egg crates  to  straighten the flow and
simultaneously move the particle back
towards the center of the stack.

Experimental
  The wind tunnel shown in Figure 1
was used to investigate the  effects of
the venturi on  cyclonic flow. Air enters
the wind tunnel through a conical flow
regulator, passes  through  a  set  of
honeycomb straightening  vanes, and
then   flows   through   a   carefully
calibrated Herschel-type  venturi. The
air  then  enters the suction  side of a
centrifugal   blower.  Immediately
downstream from the blower,  the  air
enters a tangential admittance  swirl
generator, which cascades the air into
the test section through four longitud-
inal and externally  adjustable slots.
Hinged vanes  located in these  slots
allow the angle of admittance to  be
controlled so that very intense swirling
flows can be generated.
  This swirl generator was also used to
elevate the ability of various low-head
loss straightening vanes (Figure 2) to
straighten cyclonic flow. Starting with
an overall straightener length, L, of two
pipe  diameters,  each  straightening
device was tested at flow rates of 7,  10,
               Conical Flow
                 Regulator
               Flow Rate Venturi
                           45.7
and 13 mVs. At each of these flow rates,
head loss data were recorded for five
different swirl intensities. If the device
straightened  the  cyclonic  flow,  its
length  was shortened and  the device
retested. This process continued until
the  flow field  was  no  longer
straightened.
  After  the wind tunnel studies were
completed, the ability of the egg crate to
straighten  cyclonic  flow  and  to
redistribute  the   particulate  was
evaluated at a fertilizer plant. The stack
at the plant was 76 cm in diameter and
11 m high. Stack temperature was 32
°C, moisture  was  5  percent, and the
axial volumetric flow   was  approxi-
mately! 27 mVmin. Exhaust gases from
the fertilizer blending operation entered
tangentially at the base of the stack and
then passed  through a  water  spray
chamber and  a turning vane to produce
swirling flow. The swirling flow caused
particulate laden water droplets to move
to the  stack  wall where  they drained
downward and exited with the scrubber
water.
  A galvanized  steel egg crate of cell
size D/4 (19 cm) and length D/2 (38 cm)
was  installed in the stack  at a point
seven pipe diameters downstream of
the turning vane (four pipe diameters
from the  stack exit).  Particulate  and
velocity  measurements  were  made
through sampling ports located two pipe
diameters downstream and two pipe
diameters upstream from the center of
the egg crate.  EPA Methods 1 (sampling
point selection),  2 (velocity and volu-
metric  flow),  and  5  (particulate
sampling) were used in thetesting. Flow
                         45.7
                                           Test Venturi
                                   (Dimensions in centimeters/
                            Flow Straightening Vents
                               Flow
                                         7.62m
                              1.5ml
       Electric Motor
                        • Swirl Generator

Figure 1.   Experimental facility plan review.

                                  2
           See Detail Above -
angle  with  respect  to  the   stack
longitudinal axis was measured using a
United  Sensor®  3-dimensional pttot
tube.
Results and  Conclusions
Venturi Studies
  It was found that an in-stack venturi
designed as described in this study will
accurately measure volumetric flow in
cyclonic flow situations. However, it will
neither  straighten cyclonic flows nor
redistribute the  particulate because the
total angular  momentum is conserved
as the gas  passes through the venturi
throat.  It  was  also found that the
characteristic   region  of  low  axial
velocity  m the center of the gas stream
is  accelerated in  the venturi throat  to
give a nearly rectangular velocity profile
in  the venturi throat, itself
  Some possible benefits of an m-stack
installed venturi designed according to
the  specifications developed  in this
study are:
 •  Properly calibrated,  a venturi can
     stand  alone  as a  volume  flow
     measuring device; and
 •  The  increased  velocity  in  the
     venturi throat could make more
     accurate sampling  in stacks with
     low velocities  since  most  pitot
     tubes are inaccurate below 10ft/s.


Flow Straightener Studies

  Egg crate flow straighteners were
found to be effective in  removing the
swirl component of the flow at lengths
equal to or greater than the cell size. The
                                         Figure 2.   Egg crate and 8-vane etoile-
                                                   type flow straighteners.

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straightening effectiveness was greatly
reduced when the length was reduced
below the cell size.
  The e'toile type straightener was able
to straighten  swirling  flow, but  the
overall effective  length requirements
were greater  than those for the  egg
crate; the head loss across the e'toile
straighteners  was also higher.  For
example, the minimum effective length
for an eight-vane e'toile straightener
was two  stack diameters.
  The  field   testing   results   were
inconclusive in relation to the ability of
the egg crate  to  redistribute the flow
back towards  the  center of the  stack.
However, the egg crate did destroy the
strong swirling flow present (Table 1)
since the flow angle at  all 20 traverse
points downstream of  the egg  crate
deviated  less  than 4° from  the  stack
axis. Also, static pressure measurements
upstream and downstream  of the  egg
crate were identical, demonstrating that
the head loss was negligible. Thus, we
conclude that the egg crate can be a
cost-effective means to destroy cyclonic
flow patterns.
  In  the  paniculate testing, eight,  60-
min sampling runs were accomplished
using two  Method 5 trains sampling
simultaneously. (Train A sampled two
pipe diameters downstream of  the  egg
crate and Train B sampled two pipe
diameters upstream.) In the first three
runs, each train sampled a total  of 20
points (10 points on each diameter). In
these and the other five runs,  Train A
sampled  with  its nozzle and  pilot tube
aligned with the stack axis, while Train
B sampled with its nozzle and pilot tube
aligned with  the direction of the  gas
flow at the sampling  point. (Train B
sampling  time  at each  point  was
adjusted so that the ratio of the volume
of gas collected at each pointtothetotal
axial  volumetric  flow  in  the  stack
remained constant.)
  In  the last five runs single-point
sampling rather than traversing was
employed.  In  these  runs.  Train  A
sampled at the same point - a point 58
cm in from the port hole, but Train B
sampled  a different point in each run,
i.e., Run 4 (71 cm).  Run 5 (67 cm),  Run 6
(63 cm), Run 7 (58 cm),  and Run  8 (49
cm). The objective of these five runs was
to determine the paniculate distribution
upstream of the egg crate in relation to
the concentration  at  a specific  point
downstream of the egg crate.
  The results of the eight runs (Table 2)
show that in  all  runs the particulate
concentration  determined   upstream
Table 1.   Flow Angles Measured Downstream of the Egg Crate
Distance from
Stack Wall (cm)
2.5
7.6
12.7
17.8
22.8
27.9
33.0
38.1
43.2
48.3
53.3
58.4
63.5
68.6
73.7
Flow Angle
Port A (9)
46
52
58
65
68
57
0
-54
-52
-46
-40
-34
-28
-20
-20
Flow Angle
Port B (9)
45
47
50
50
53
56
58
-1
-45
-44
-41
-37
-37
-32
-26
Table 2.  Comparison of Particulate Concentrations and Volumetric Flow Upstream
          and Downstream from the Egg Crate
Run
Number
1
2
3
A verage
4
5
6
7
8
A verage
Concentration (mg/m3)
Upstream Downstream
130
147
26
101
22
31
103
35
64
47
130
154
22
102
18
31
86
33
55
45
Volumetric
Upstream
137
138
115
130






Flow (m3/min)
Downstream
125
120
115
120






compared well with that determined
downstream.  Further,  the  close
agreement between the two trains in
the  last  five runs  shows  that  the
particulate concentration  was evenly
distributed upstream of the egg crate.
This demonstrates  that  the swirling
flow effectively removed large particles,
i.e., the remaining particles were small
enough to follow the  gas flow lines.
Thus, the degree of redistribution of
particulate by the egg crate cannot be
determined from these results. Resource
limitations and the fact that no additional
sources were available for testing pre-
vented conducting additional field tests.
field tests.

Reference
1.  Mitchell, W. J., B. E. Blagun, D. E.
    Johnson,  and  M.  R.   Midgett.
    Angular Flow Insensitive Pilot Tube
    Suitable  for  Use  with  Standard
Stack  Testing  Equipment.  EPA-
600/4-79-042, U.S. Environmental
Proteclion Agency,  Research
Triangle   Park,  North   Carolina,
1979.
                                                                                    * US. GOVERNMENT PRINTING OFFICE: 1982-559-017/0848

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       J. Douglas Sterrett. Allen R. Barbin. Joe W. Reece, W. Glenn Carter, and Bruce B.
         Ferguson are with Harmon Engineering and Testing, Inc., Auburn, AL 35810.
       William J. Mitchell is the EPA Project Officer (see below).
       The complete report,  entitled "Techniques to Measure Volumetric Flow and
         Paniculate Concentrations in Stacks with Cyclonic Flow," (Order No.  PB
         82-259 789; Cost: $10.50, 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
Postage and
Fees Paid
Environmental
Protection
Agency
EPA 335
Official Business
Penalty for Private Use $300
        PS    0000339

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