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 ------- 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. ------- 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 ------- 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 ------- |