This work aims at demonstrating the feasibility of replacing Indonesian coal (INC) with hydrothermally treated municipal solid waste (MSWH) in cocombustion with high ash Indian coal (IC). The combustion efficiencies and emissions (CO, NO) of MSWH, INC and their blends with IC for a series of tests performed under a range of temperatures and air conditions were tested in a drop-tube reactor (DTR). The results showed the following. The combustion efficiency of IC was increased by blending both MSWH and INC and CO emission was reduced with increasing temperature. For NO emission, the blending of MSWH led to the increase of NO concentration whereas the effects of INC depended on the temperature. The combustion behaviors of IC-MSWH blend were comparable to those of the IC-INC blend indicating it is possible for MSWH to become a good substitute for INC supporting IC combustion. Moreover, the CO emission fell while the NO emission rose with increasing excess air for IC-MSWH blend at 900°C and the highest combustion efficiency was obtained at the excess air of 1.9. The existence of moisture in the cocombustion system of IC-MSWH blend could slightly improve the combustion efficiency, reduce CO, and increase NO. 1. Introduction With the development of human civilization, municipal solid waste (MSW) turns out to be a great threat to the environment. Traditional MSW disposal methods such as open dumping, landfill, or composting are becoming less and less attractive due to less land available around cities and also much more stringent environmental regulations. Thermal treatment as incineration will therefore play an important role as an effective MSW treatment which enjoys the advantages of outstanding reduction in waste volume, thermal destruction of toxic organic constituents, and so forth. However, it is hard to recycle adequate energy from the incineration of MSW with high moisture content, heterogeneous characteristics, and low energy content. Recently, hydrothermal treatment (HT) is regarded to be an effective waste to energy technology for converting MSW into solid fuels with low moisture content, uniform characteristics, and high bulk/energy density [1–5]. On the other hand, we are running out of high-rank coals for power generations so that the utilizations of low-rank coals are inevitable especially in developing countries. For example, Indian coal (IC) is one kind of coal with high ash content which leads to difficulty in ignition and maintenance of flame stabilization, and so forth. In reality, Indonesian coal (INC) is blended with IC in power plants in
References
[1]
M. Muthuraman, T. Namioka, and K. Yoshikawa, “A comparative study on co-combustion performance of municipal solid waste and Indonesian coal with high ash Indian coal: a thermogravimetric analysis,” Fuel Processing Technology, vol. 91, no. 5, pp. 550–558, 2010.
[2]
M. Goto, R. Obuchi, T. Hirose, T. Sakaki, and M. Shibata, “Hydrothermal conversion of municipal organic waste into resources,” Bioresource Technology, vol. 93, no. 3, pp. 279–284, 2004.
[3]
M. Muthuraman, T. Namioka, and K. Yoshikawa, “Characteristics of co-combustion and kinetic study on hydrothermally treated municipal solid waste with different rank coals: a thermogravimetric analysis,” Applied Energy, vol. 87, no. 1, pp. 141–148, 2010.
[4]
M. Muthuraman, T. Namioka, and K. Yoshikawa, “A comparison of co-combustion characteristics of coal with wood and hydrothermally treated municipal solid waste,” Bioresource Technology, vol. 101, no. 7, pp. 2477–2482, 2010.
[5]
S. Jomaa, A. Shanableh, W. Khalil, and B. Trebilco, “Hydrothermal decomposition and oxidation of the organic component of municipal and industrial waste products,” Advances in Environmental Research, vol. 7, no. 3, pp. 647–653, 2003.
[6]
S. Biswas, N. Choudhury, P. Sarkar et al., “Studies on the combustion behaviour of blends of Indian coals by TGA and Drop Tube Furnace,” Fuel Processing Technology, vol. 87, no. 3, pp. 191–199, 2006.
[7]
K. Le Manquais, C. Snape, I. McRobbie, J. Barker, and V. Pellegrin, “Comparison of the combustion reactivity of TGA and drop tube furnace chars from a bituminous coal,” Energy and Fuels, vol. 23, no. 9, pp. 4269–4277, 2009.
[8]
K. Suksankraisorn, S. Patumsawad, and B. Fungtammasan, “Co-firing of Thai lignite and municipal solid waste (MSW) in a fluidised bed: Effect of MSW moisture content,” Applied Thermal Engineering, vol. 30, no. 17-18, pp. 2693–2697, 2010.
[9]
H. Tsuji, H. Shirai, H. Matsuda, and P. Rajoo, “Emission characteristics of NOx and unburned carbon in fly ash on high-ash coal combustion,” Fuel, vol. 90, no. 2, pp. 850–853, 2011.
[10]
E. Desroches-Ducarne, E. Marty, G. Martin, and L. Delfosse, “Co-combustion of coal and municipal solid waste in a circulating fluidized bed,” Fuel, vol. 77, no. 12, pp. 1311–1315, 1998.
[11]
K. Suksankraisorn, S. Patumsawad, P. Vallikul, B. Fungtammasan, and A. Accary, “Co-combustion of municipal solid waste and Thai lignite in a fluidized bed,” Energy Conversion and Management, vol. 45, no. 6, pp. 947–962, 2004.
[12]
S. G. Li, A. Wu, S. Deng, and W. P. Pan, “Effect of co-combustion of chicken litter and coal on emissions in a laboratory-scale fluidized bed combustor,” Fuel Processing Technology, vol. 89, no. 1, pp. 7–12, 2008.
[13]
M. Ikeda, H. Makino, H. Morinaga, K. Higashiyama, and Y. Kozai, “Emission characteristics of NOx and unburned carbon in fly ash during combustion of blends of bituminous/sub-bituminous coals,” Fuel, vol. 82, no. 15–17, pp. 1851–1857, 2003.