United States Environmental Protection Agency Air and Energy Engineering Research Laboratory Research Triangle Park, NC 27711 Research and Development EPA/600/SR-94/061 May 1994 EPA Project Summary Field Performance of Woodburning Stoves in Crested Butte During the 1991 -1992 Heating Season Dennis R. Jaasma, Curtis H. Stern, and Mark Champion The 1991-92 field performance of 11 woodburning stoves in and around Crested Butte, CO, were evaluated. Measurements included particulate matter (PM), carbon monoxide (CO), total unburned hydrocarbons (THCs), and weekly average burn rates. The monitored stoves included EPA-certi- fied catalytic and noncatalytic stoves. The main emphasis of this continuing study is to characterize the emissions of EPA-certified stoves as they age with normal use. Emissions from a previously moni- tored Phase II (stoves certified to EPA's 1990 standard) noncatalytic stove ap- peared to be unchanged when varia- tions in fuel moisture content and burn rate were taken into account. A sec- ond Phase II noncatalytic stove also performed with emissions at levels which had been observed for noncata- lytic stoves in previous monitoring. On average, the catalytic stoves had PM emission factors about 50% greater than those measured during the 1989- 90 study, when most of the monitored catalytic stoves had fresh catalysts. This increase is likely due to catalyst degradation. An average emission in- crease of 147% was measured for two Phase I (stoves certified to lEPA's 1988 standard) catalytic stoves, both of which were monitored in previous years. Two Phase II catalytic stoves, both of which were new this season, performed at the same emission level observed during the 1989-90 study of stoves with fresh catalysts. This Project Summary was devel- oped by EPA's Air and Energy Engi- neering Research Laboratory, Re- search 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 The town of Crested Butte contracted with Virginia Polytechnic Institute and State University (VPI) for the field mea- surements of woodstove emissions in Crested Butte during the winters of 1988- 89 and 1989-90. These measurements were intended to determine the effect of a town-wide changeover from conven- tional to EPA-certified woodstoves. Both particulate matter (PM) and carbon mon- oxide (CO) emissions were measured during these studies. The current (1991- 92) study was intended to monitor the performance of Phase II stoves in Crested Butte as they age. The previous studies created a large database of emissions from conventional and Phase I stoves, giving baseline data for comparison to Phase II models. Be- cause some certified stoves were moni- tored during more than one study, the current study enables some comparisons between current performance and perfor- mance 2 or 3 years ago. Any one season of study will not tell the whole story of long-term woodstove performance. The results of this study, therefore, can best be used in comparison with results from previous and future studies. The hardware used for the measure- ments is known as the "VPI sampler." This sampler has been compared to an EPA reference method for woodstove PM Printed on Recycled Paper ------- (Method 5G) and has been found to be accurate. During this study hydrocarbon emis- sions were measured for the first time using this sampler. Collected gas samples were pumped into Tediar® bags and sent to VPI for analysis. Both total and non- methane hydrocarbons were measured. Problems with sample storage procedures- resulted in data which are interpreted as approximate lower estimates for volatile hydrocarbon emissions. Summary and Conclusions The primary thrust of the 1991-92 moni- toring was quantification of degradation of emissions control performance. Degra- dation can be quantified by comparing results from individual stoves monitored during different heating seasons, and in this study there were three stoves (two catalytic, one noncatalytic) which can be evaluated this way. The previously moni- tored Phase I catalytic stoves (CAT05 and CAT07) showed respective emissions increases of 105% and 189% for PM emission factors relative to their perfor- mance two seasons ago. Structural fail- ure (CAT07) and catalyst degradation (both stoves) are the probable causes. One noncatalytic Phase I stove (NCAT09) was monitored two seasons ago and can be compared to its previous performance. When burn rate is taken into account its performance appears unchanged from the earlier data. Based on comparison of 1989-90 cata- lytic stove data obtained with fresh cata- lysts, there was evidence of emission deg- radation (or unusually poor performance for other reasons) in 67% of the catalytic stoves monitored. Most of these were Phase I stoves, and catalyst deterioration is the suspected cause in most cases. Two Phase II noncatalytic stoves per- formed at about the same emission lev- els observed 2 years ago for Phase I noncatalytic stoves. The emissions from noncatalytic stoves are more sensitive to wood moisture and burn rate than are catalytic stoves. This sensitivity compli- cates the comparison of year-to-year data. After correcting for variations in these variables, the data showed no evidence of degradation. The Phase II catalytic stove was in its first heating season. Its performance was approximately the same as that of the Phase I catalytic stoves of the 1989-90 study, where care was taken to ensure that stoves and catalysts were in good condition. However, its PM emission fac- tor was about twice that of one of the Phase I stoves when new. Tediar® bags were used to store gas samples for later hydrocarbon analysis, but problems with sample integrity re- duced the accuracy of the data. The total hydrocarbon emission factors for cata- lytic and noncatalytic stoves were esti- mated at 16.8 and 14.0 g/kg, respec- tively, using the average of two exponen^ tial sample decay calculations. Based on some highly preliminary measurements, these numbers are probably 20% low due to the adsorption of hydrocarbons by the desiccant which was part of the sample train. The Method 25 analyses of the samples indicate that approximately 56% of the hydrocarbons were methane. This corre- sponds to methane emission factors of 10 and 8 g/kg for catalytic and noncata- lytic stoves, respectively. Further monitoring would help to de- velop a statistically sound database which can give definitive answers about stove degradation. This year's work indicates that catalyst durability is a problem. In- stove catalyst evaluations and bench tests would also be of help in future work. •kv.8. GOVERNMENT PRINTING OFFICE! WM - SSOJM7/IM240 ------- ------- D. Jaasma, C. Stem, andM. Champion are with Virginia Polytechnic Institute and State University, Blacksburg, VA 24061-0238. Robert C.McCrIHl8 is the EPA Project Off tear (see below). The complete report, entitled "FieldPerformance of Woodbuming Stoves in Crested Butts During the 1991-1992 Heating Season,"(Order No. PB94-161270; Cost: $27.00; 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 BULK RATE POSTAGE & FEES PAID EPA PERMIT No. G-35 EPA/600/SR-94AJ61 ------- |