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). ------- 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 ------- 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 ------- 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 Official Business Penalty for Private Use $300 EPA/600/SR-99/048 ------- |