United States Environmental Protection Agency Air and Energy Engineering Research Laboratory Research Triangle Park NC 27711 Research and Development EPA/600/S7-87/009 May 1987 &ER& Project Summary Evaluation of Fabric Filter on Boiler 108 at the Naval Amphibious Base, Little Creek, VA J. M. Foster, J. C. Mycock, J. W. Richardson, and J. D. McKenna The operating characteristics of the reverse-air baghouse controlling emis- sions from Boiler 108 at the Naval Am- phibious Base (NAB), Little Creek, VA, were determined via collection of data (by Navy personnel) on boiler and bag- house operation (hours of operation, coal feed rate, steam load, air load, bag- house inlet temperature, and baghouse module pressure drop), and periodic in- spection and testing of selected bags. Tests of physical characteristics of the fiberglass bags revealed normal de- terioration of fabic strength with in- creasing time of exposure to flue gas. Fill fibers were more affected than warp fibers. A long plateau in bag life was observed; fabric characteristics after 1,500 hours of actual operation and after 7,600 hours did not differ greatly. Statistical analyses of fabric test data indicated effects on fabric due both to length of exposure time and position in the baghouse, and interaction of those effects. Other analyses indicated that exposure time was the dominant effect. Operating costs for reverse air and in- duced draft fans were calculated for the years 1983,1984, and 1985. This Project Summary was devel- oped by EPA's Air and Energy Engineer- ing Research Laboratory, Research Tri- angle 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 Boiler 108 at the Naval Amphibious Base (NAB), Little Creek, VA, is stoker- coal-fired, rated at 90,000 Ib/hr* of steam but usually operated at 40,000- 60,000 Ib/hr. The baghouse controlling participate emissions from Boiler 108 is a reverse-air-cleaned Griffin Environ- mental fabric filter employing 3 x 1 twill fiberglass bags, and was studied from its August 1983 start-up until Septem- ber 1985, for the purpose of defining its performance and operating characteris- tics. The Navy collected data on boiler and baghouse operation and mainte- nance, and ETS, Inc. performed physical tests on bags removed periodically from the baghouse in order to monitor wear on the bags and predict bag failure and expected life. Project Design The project included: • The collection of boiler operating data. • The collection of baghouse operat- ing data. • The calculation of fan power con- sumption. • The calculation of cleaning power consumption. • Graphic representation of relation- ships between parameters. •Users more familiar with the metric system may use the conversion table at the end of this Sum- mary. ------- • Identification of problems of bag- house operation and maintenance. Navy personnel at the steam plant collected operating data for the boiler and baghouse. ETS laboratory person- nel examined test bags for holes, abra- sion, dust cake characteristics, and other gross visual attributes. Randomly selected bags were also examined under magnification. Test bags were subjected to the following laboratory tests to determine fabric characteristics and strength: Permeability (as received and after vacuuming to 10 and 30 in. of oil). Organic Content (loss on ignition). Tensile Strength (warp and fill fibers). Mullen Burst. MIT Flex (warp and fill fibers). Fabric weights as received and after vacuuming to 30 in. of oil also were recorded. Test bags were taken from near the centers of modules (representative av- erage bags) and from locations near module doors (possible worst-case bags, in the event of leakage around doors). Description of Baghouse 108 Design specifications for the emis- sions control system included: Baghouse Flow 49,800 acfm Tempera- 350°F (maxi- ture mum 500°F) Pressure 7 in. h^O drop (AP) (dirty) Full load dust load- ing 1,000 Ib/hr Gas-to- 2.5 max cloth (G/C) (during ratio cleaning) Collection 99.9% (by efficiency weight) Coal—Bituminous with maximum 1.5% sulfur (S). Bags—Woven fiberglass with a coat- ing of Teflon B for 10% add-on weight, or a combination of silicon graphite and Teflon. Fabric weight of 14 oz/yd2 minimum, with a permeabil- ity of 60 ft/min. Bags were rated for maximum operating temperature of 500°F. Bags were 8 in. in diameter by 25 ft long. Bag spacing inside the baghouse was 2 in. Anti-collapse rings were sewn into the bags at 4- or 5-ft intervals. Baghouse 108 had an optional pres- sure drop-triggered cleaning control (set at 6 in. H20) but was normally cleaned twice every 24 hours on a tim- ing cycle. During the winter, cleaning might occur three times per 24-hour pe- riod. Baghouse 108 was equipped with an automatic, pressurized fly ash handling system. Description of Test Bags Three new bags were evaluated, as well as three bags exposed to flue gas but never actually in service in the bag- house. Five series of nine bags each, removed from the baghouse after vary- ing hours of operation, were also tested: Series Hours of Operation I IV V 378 513 1189 1504 7602 Boiler and Baghouse 108 were oper- ated intermittently, and the bags re- mained in the baghouse during down- time. The hours of operation given above do not include downtime, but it was assumed that downtime exposure results in some additional stress to the bags, although the type and amount were not quantified. Results of an Inspection of Baghouse 108 Approximately 2 weeks after start-up of Baghouse 108, ETS personnel con- ducted a thorough inspection of each module, noting conditions such as ash build-up, holes in bags, and acid attack. There was evidence of condensation and acid attack, and dust was observed on the outside of some bags, suggest- ing dirty-side to clean-side leakage in- side the baghouse. Results of Fabric Tests The woven fiberglass bags, with about 5% organic finish according to loss-on-ignition test results, were 8 in. in diameter by 25 ft long. Visual and mi- croscopic examination revealed, in gen- eral: abrasion along the seam, some holes, pearling, and fill fibers dirtier than warp fibers. Fabric weights varied little from one series of test bags to another. Table 1 shows the average results of all fabric tests, expressed as percent- ages of new bag test values. It ap- peared, despite some low values in fab- ric strength measurements (e.g., breakage of fill fibers at under 1 00 flexes in the MIT flex test), that fabric strength remained on a plateau. As of July 1986, the original bag set was still in place, and no massive bag failures had oc- curred. Visible emissions were not a problem with Baghouse 108. They were meas- ured at under 20% during acceptance tests at full boiler load in 1983, and re- mained low as of July 1986. Effect of Position in the Baghouse and Length of Exposure on Fabric Test Values ETS personnel performed a statistical analysis of data including values from fabric tests, position in the baghouse, and length of exposure time, in order to gauge the effects of baghouse position and exposure time on fabric test results. Generally, both baghouse position and exposure time affected fabric test re- sults, and there was interaction be- tween those effects. Although statistical tests indicated that there were separate (but interact- ing) effects on fabric test values due to length of exposure time and postition in the baghouse, it was found that the ef- fect due to position probably was not the major reason for differences be- tween fabric test values. A more obvi- ous effect was due to length of expo- sure time on fabric characteristics. Comparing fabric test values showed that permeability declined steadily with exposure time, as did values in tests of fabric strength (Mullen burst, tensile strength, and MIT flex), particularly for fill fibers. Calculation of Fan Power Costs Operating costs for the induced draft (I. D.) and reverse air (RA) fans were cal- culated using hours of operation during 1983,1984, and 1985, and Virginia Elec- tric and Power Co. (VEPCO)-quoted cost of electricity. /. D. Fan Data Baghouse 108 inlet average gas flow at full boiler load (data from acceptance test, 12/10/83) was 47,561 acfm <&> 371°F. I. D. fan power cost was calculated using the representative inlet volume of 50,000 acfm (fv 370°F. Baghouse 108 flange-to-flange pressure drop normally ran 2-4 in. H20, according to NAB per- sonnel. ------- 1 Tmble 1. Summary of Physical Characteristics of Test Bags (Expressed as % of New Bag Values) Series 1 II III IV V Date Pulled 09/07/83 11/08M3 01/24/84 after 05/15/84 after 09/27/85 Date Rec'd 09/09t83 11/18/83 01/26/84 06/08/84 10/24/85 Actual Operating Time, hr 378 513 1189 1504 7602 Permeability As Vacuum Rec'd 10 in. 30 in. 7 7 6 8 7 34 23 37 42 27 46 36 54 67 45 Mullen Burst 96 90 86 70 68 Tensile Strength Warp Fill 99 89 91 63 57 105 87 91 61 62 MIT Flex Warp Fill 190 101 75 23 28 94 54 45 13 14 Loss on Ignition 89 82 93 89 109 RA Fan Data An RA gas flow of 10,000 acfm was assumed. RA fan power costs were cal- culated for pressure drops across the RA fan of 0.5, 1.0, and 1.5 in. H2O. Baghouse 108 Operating Hours Operating hours for Baghouse 108 were: 1983—1519 hours, 1984—4081 hours, and 1985—2002 hours (as of the last bag pull). Cost of Electricity for NAB, Little Creek, VA The April 1986 quotation by VEPCO for industrial power cost in Norfolk, VA (schedule 6, Virginia jurisdiction) was $0.045446/kWh. Metric Conversions Readers more familiar with the metric system may use the following values to convert the nonmetric units used else- where in this Summary. Nonmetric Times Yields Metric acfm °F ft ft/min in. in. H20 in. (vac) Ib/hr oz/yd2 0.000472 5/9(°F-32) 0.305 0.00508 0.0254 0.249 3.38 0.000126 0.0339 am3/s °C m m/s m kPa kPa kg/s kg/m2 Fan Power Costs System AP, in. H20 2 3 4 1983 $1350 2025 2700 1984 $3627 5440 7253 1985 $1779 2669 3558 1983 $ 67 135 202 1984 $ 181 363 544 1985 $ 89 178 267 RAAP, in. H2O 0.5 1.0 1.5 Assuming round-the-clock baghouse operation for 50 weeks a year and a vol- ume of 50,000 acfm with the baghouse operating at 4 in. H2O pressure drop, the I. D. fan power cost would be just under $15,000 per year, and each inch of pres- sure drop would cost over $3,700 per year Conclusions Baghouse 108 performed well in con- trolling paniculate emissions from the coal-fired boiler it serves. The original set of fiberglass bags, with very few re- placements, remained in service 3 years after start-up. Joyce M. Foster, John C. Mycock, John W. Richardson, and John D. McKenna are with ETS, Inc.. Roanoke. VA 24018-4394.. Dale L. Harmon is the EPA Project Officer (see below). The complete report, entitled "Evaluation of Fabric Filter on Boiler 108 at the Naval Amphibious Base, Little Creek, VA," (Order No. PB 87-171 286/AS; Cost: $13.95, 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: Air and Energy Engineering Research Laboratory U.S. Environmental Protection Agency Research Triangle Park, NC 27711 ------- United States Environmental Protection Agency Center for Environmental Research Information Cincinnati OH 45268 Official Business Penalty for Private Use $300 EPA/600/S7-87/009 0000329 PS U S EN¥IR PROTECTION ASENCY REGION 5 LIBRARY 230 S DEARBORN STREET CHICAGO IL 60604 ------- |