United States
Environmental Protection
Agency
National Risk Management
Research Laboratory
Cincinnati, OH 45268
Research and Development
EPA/600/SR-99/048   June  1999
Grilling)
SuhY. Lee
  The U.S. EPA, working through the
Clean Air Technology Center (CATC)
and the U.S.-Mexico Border Information
Center on Air Pollution (Centra  de
Informacion Sobre  Contaminacion  de
Aire Par  la Frontera entre EE.UU. y
Mexico, or CICA), along with the Mexi-
can Institute National de Ecoligfa (INE),
has jointly initiated a program to estab-
lish a reliable emissions inventory  for
street vendor cooking devices  (char-
coal grilling), a significant source of air
pollutants in the Mexicali-Imperial Val-
ley area.
  This Project Summary was developed
by the National Risk Management Re-
search Laboratory's Air Pollution Pre-
vention and Control Division, Research
Triangle Park, NC, to announce key find-
ings of the research project that is fully
documented in a separate report of the
same title (see Project Report ordering
information at back).

Overview
  Emissions  from street vendor cooking
devices,  prevalent  in the streets of
Mexicali,  Mexico, were investigated  ex-
perimentally by measuring levels of  par-
ticulate  matter (PM),   particle  size
distributions,  volatile  organic compounds
(VOCs), semivolatile  organic compounds
(SVOCs), aldehydes, and oxides of nitro-
gen and  sulfur, emitted  when  meat  is
cooked on a grill over a charcoal fire.  The
test grill was carefully chosen to simulate
street vendor cooking devices in Mexicali.
Nine test  runs  were planned for the  pro-
gram.  In order to investigate the emission
rate, both beef and chicken were tested.
Furthermore, both meats were marinated
with  a mixture  similar to that  used by
street vendors. Initially, it was planned to
use  only charcoal from Mexicali;  how-
ever, difficulties in  obtaining sufficient
quantities necessitated using local  char-
coal  for some of the tests. Both types of
charcoal were compared to  ensure simi-
lar  physical and  chemical  properties.
Some of the tests conducted were with
non-marinated beef for comparison. Two
blank runs were  performed sampling char-
coal  fires without meat.  Finally,  a simple
control device,  normally  used in an ex-
haust fan to trap  grease over a kitchen
stove, was evaluated for its effectiveness
in reducing emissions. A summary of the
test condition is  shown in Table 1.
  Each test run averaged approximately
3 hours  of charcoal  burning, of which
meat-cooking  lasted 1 to 2 hours. For
each  test run,  approximately 5-6  kg of
meat was cooked, and an average of 6
kg of charcoal was burned. Total PM and
SVOCs  were sampled  using the  EPA
MM5G Method.  PM with aerodynamic di-
ameters equal to and below 10 pm (PM10)
and 2.5  pm (PM25) were evaluated  using
an Andersen Mark III inertia!  cascade im-
pactor.  VOCs  were sampled  using
SUMMA canisters.  VOC  and SVOC
samples were analyzed  by  a GC-Mass
spectrometer.  Aldehydes were  sampled
using DNPH cartridges and  analyzed by
High  Performance Liquid Chromatogra-
phy (HPLC) as described in  EPA Method
1P-6A. Carbon  monoxide (CO),  oxygen
(O2),  carbon dioxide  (CO2),   nitric  oxide
(NO), total  hydrocarbons (THCs), and
sulfur dioxide  (SO2) were measured with
continuous emission monitors (CEMs).

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  All  of the emission parameters  mea-
sured during the test runs are shown  in
Table 1. The summary of test conditions
appears to  be reasonable,  except for the
SO2  measurements. Wide  fluctuations  of
the SO2 CEM readings for all the test runs
suggest a malfunction of the SO2  instru-
ment or that the measuring range  of the
instrument was too high  for the low level
of SO2 present.  Emission  results  of the
test runs are summarized  in  Tables 2  to
4. The results are tabulated as emissions
based on total  cooking  time (Table 2),
emissions per unit weight of meat and
charcoal  used  (Table 3), and emissions
per unit weight of meat cooked (Table 4).

Conclusions
  Based  on an  analysis of  the test re-
sults, the following  can  be concluded
about emissions from street vendor cook-
ing devices:
  • Emissions of total PM,  total VOCs,
    and total  SVOCs from street vendor
    cooking are basically the result  of
    cooking meat; i.e., charcoal does not
    contribute to the  emissions.
  • Marinated  meat yields increased to-
    tal VOCs  and total PM emissions
    compared to non-marinated meat.
  • There are no significant differences
    in emission  rates between chicken
    and beef.
  • Emissions of CO  and NO derive from
    the charcoal fire rather than the cook-
    ing meat.
  • Emission  of THC is almost entirely
    due  to the  initial  burning  of HCs
    present in the charcoal. THC emis-
    sion  was confined  only during the
    first half hour of charcoal light  off.
  • Based  on very limited observations,
    the simple screen placed in the stack
    (emission control device)  appeared
    to be very effective in reducing emis-
    sions of  PM,  VOCs,  SVOCs, and
    THCs from the street vendor cooking
    devices; however, since only one test
    was  performed to evaluate this de-
    vice, the  results  cannot be consid-
    ered conclusive.
  • Particle size distribution of all the test
    runs was very similar.  Most particles
    had an aerodynamic diameter of less
    than  2.5 pm (PM25).  Only 20 wt%  of
    the particles had  aerodynamic diam-
    eters between 10 and  2.5 pm.
Table 1. Summary of Test Conditions
Test Number
MC1
MC2
MC3
MC4
MC5
MC6
MC7
MC8
MC9
Type of Meat
Beef
Chicken
Beef
None
None
Beef
Chicken
Beef
Beef
Marinade
Yes
Yes
No
None
None
Yes
Yes
No
No
Emission Control
No
No
No
No
No
No
No
No
Yes
Table 2. Total Emission Rates, g/hr
Test
Number
MC1
MC2
MC3
MC4
MC5
MC6
MC7
MC8
MC9
Test Condition
Beef- Marinade
Chicken - Marinade
Beef- No Marinade
Charcoal Only
Charcoal Only
Beef- Marinade
Chicken - Marinade
Beef- No Marinade
Beef- No Marinade
- control screen
NO
5.21
16.46
8.46
13.15
16.34
14.16
6.62
5.17
6.26
THC
20.38
20.17
13.20
1.43
4.53
6.89
3.53
14.47
1.19
PM
18.06
22.65
19.53
1.27
2.81
32.49
34.94
30.41
23.70
CO
385.6
376.3
462.9
435.7
494.3
484.3
556.7
518.1
574.5
Aldehydes
2.579
2.160
1.976
0.360
0.346
3.177
3.281
2.819
1.776
VOCs
2.334
2.383
2.169
0.253
0.485
2.941
3.607
2.598
1.157
SVOCs
0.0056
0.0259
0.0152
ND*
ND
0.006
0.0087
0.003
ND
*ND - none detected
Table 3. Total Emissions per Unit Weight of Meat plus Charcoal, g/kg of meat plus charcoal
Test
Number
MC1
MC2
MC3
MC4
MC5
MC6
MC7
MC8
MC9
Test Condition
Beef- Marinade
Chicken -
Marinade
Beef- No Marinade
Charcoal Only
Charcoal Only
Beef- Marinade
Chicken -
Marinade
Beef- No Marinade
Beef- No Marinade
-control screen
NO
2.55
7.85
3.33
5.98
10.30
4.35
1.90
1.35
1.51
THC
9.98
9.62
5.19
0.65
2.85
2.11
1.02
3.77
0.29
PM
8.85
10.80
7.68
0.58
1.77
9.97
10.05
7.91
5.71
CO
188.9
179.4
182.1
198.1
311.5
148.7
160.2
134.8
138.5
Aldehydes
1.263
1.030
0.777
0.163
0.218
0.975
0.944
0.734
0.428
VOCs
1.105
1.089
0.826
0.115
0.300
0.866
0.998
0.653
0.268
SVOCs
0.002
0.0116
0.0053
ND*
ND
0.0018
0.0022
0.0008
ND
*ND - none detected

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Table 4. Total Emission per Unit of Meat, g/kg of meat cooked
Test
Number
MC1
MC2
MC3
MC4
MC5
MC6
MC7
MC8
MC9
Test Condition
Beef- Marinade
Chicken - Marinade
Beef- No Marinade
Charcoal Only
Charcoal Only
Beef- Marinade
Chicken - Marinade
Beef- No Marinade
Beef- No Marinade
- control screen
NO
2.36
6.37
3.32
NA*
NA
4.70
2.02
1.45
1.76
THC
9.21
7.80
5.19
NA
NA
2.29
1.08
4.06
0.33
PM
8.16
8.76
7.67
NA
NA
10.79
10.68
8.52
6.64
CO
174.3
145.5
181.8
NA
NA
160.8
170.2
145.2
161.1
Aldehydes
1.165
0.835
0.776
NA
NA
1.055
1.003
0.790
0.498
VOCs
1.055
0.921
0.852
NA
NA
0.977
1.102
0.728
0.325
SVOCs
0.0025
0.0100
0.0060
NA
NA
0.0020
0.0027
0.0008
0
*NA - not applicable

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  S. Lee is with ARCADIS Geraghty & Miller, Research Triangle Park, NC 27709.
  Paul M. Lemieux is the EPA Project Officer (see below).
  The complete report, entitled  "Emissions from  Street Vendor Cooking Devices
    (Charcoal Grilling),"  (Order No. PB99-146995; Cost: $33.00,  subject to
    change) will be available  only from
          National Technical Information Service
          5285 Port Royal Road
          Springfield, VA 22161
          Telephone: (703) 605-6000
  The EPA Project Officer can be contacted at
          Air Pollution Prevention and Control Division
          National Risk Management Research  Laboratory
          U.S. Environmental Protection Agency
          Research Triangle  Park, NC 27711
United States
Environmental Protection Agency
CenterforEnvironmental Research Information
Cincinnati, OH 45268
     BULK RATE
POSTAGE & FEES PAID
         EPA
   PERMIT No. G-35
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Penalty for Private Use
$300
EPA/600/SR-99/048

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