Determination of emission factors of nitrous oxide from fluidized bed sewage sludge incinerators by long-term continuous monitoring

被引:10
作者
Suzuki, Y [1 ]
Ochi, S
Kawashima, Y
Hiraide, R
机构
[1] Natl Inst Adv Ind Sci & Technol, Tsukuba, Ibaraki 3058569, Japan
[2] Publ Works Res Inst, Tsukuba, Ibaraki 3058516, Japan
[3] Natl Inst Infrastruct Management, Tsukuba, Ibaraki 3050804, Japan
关键词
nitrous oxide; sewage sludge; emission factors; continuous monitoring; fluidized bed incinerators;
D O I
10.1252/jcej.36.458
中图分类号
TQ [化学工业];
学科分类号
0817 ;
摘要
This paper describes the results of field measurements of nitrous oxide (N2O) emissions from fluidized bed sewage sludge incinerators. N2O was monitored continuously at six incinerators for 7-14 days. To study possible seasonal differences in N2O emissions, measurements were done at two incinerators in both summer and winter. N2O emissions varied with time, with large fluctuations in all incinerators. This result suggests that N2O emission factors determined by a grab sampling or short-term monitoring are not reliable. The average emission factors obtained were 1,520-6,400 g-N2O/t-dry sludge, which is much higher than the values of 800-1,500 g-N2O/t-dry sludge published in "Good Practice Guidance and Uncertainty Management in National Greenhouse Gas Inventories" by the IPCC. N2O emissions were mostly determined by the highest freeboard temperature of the incinerator. N2O emissions were drastically lower at higher values of highest freeboard temperature. The relation of N2O emissions to the highest freeboard temperatures was nearly the same in all incinerators. This suggests that one can estimate the N2O emission factor of an incinerator by analyzing the freeboard temperatures for several weeks. Seasonal differences in N2O emissions from a small-capacity incinerator seemed to be due to the change in freeboard temperature. A large-capacity incinerator had the same N2O emissions in the summer and winter, because the change in freeboard temperature was small. Incinerators having larger incineration capacities tended to have higher N2O emission factors. This means that large capacity incinerators are operated with relatively low freeboard temperature.
引用
收藏
页码:458 / 463
页数:6
相关论文
共 10 条
[1]  
Amand L.-E., 1989, P 1989 10 INT C FLUI, V1, P49
[2]  
*ENV AG UK, 1998, ENV AG TECHN GUID NO
[3]  
HOUGHTON JT, 1990, CLIMATE CHANGE IPCC, P30
[4]  
*JAP SEW WORKS ASS, 2001, SEW WORKS JAP 2001, P56
[5]  
Johnke B., 1999, EMISSIONS WASTE INCI
[6]   MECHANISMS OF NITROUS-OXIDE FORMATION IN COAL FLAMES [J].
KRAMLICH, JC ;
COLE, JA ;
MCCARTHY, JM ;
LANIER, WS ;
MCSORLEY, JA .
COMBUSTION AND FLAME, 1989, 77 (3-4) :375-384
[7]  
*MIN ENV JAP, 2002, BUDG GREEN HOUS GAS
[8]  
PENMAN J, 2001, GOOD PRACTICE GUIDAN, P30
[9]  
TAKEISHI K, 1996, 147 PUBL WORKS RES I, P27
[10]  
YASUDA K, 1993, REPORT KANAGAWA ENV, V16, P49