Oil sludge, if unused, is one of the major industrial wastes requiring treatment from petroleum re®nery plants or the petrochemical industry. It contains a large amount of combustibles with high heating values. The treatment of waste oil sludge by burning has certain bene®ts; however, it cannot provide the useful resource ef®ciently. On the other hand, the conversion of oil sludge to lower molecular weight organic compounds by pyrolysis not only solves the disposal problem but also has the appeal of resource utilization. The major sources of oil sludge include the oil storage tank sludge, the biological sludge, the dissolve air¯otation (DAF) scum, the American Petroleum Institute (API) separator sludge and the chemical sludge. In this study, the oil sludge from the oil storage tank of a typical petroleum re®nery plant located in northern Taiwan is used as the raw material of pyrolysis. Its heating value of dry basis and low heating value of wet basis are about 10681 kcal kg À1 and 5870 kcal kg À1 , respectively. The removal of the moisture from oil sludge signi®cantly increases its heating value. The pyrolysis of oil sludge is conducted by the use of nitrogen as the carrier gas in the temperature range of 380±1073 K and at various constant heating rates of 5.2, 12.8 and 21.8 K min À1 . The pyrolytic reaction is signi®cant at 450±800 K and complex. For the sake of simplicity and engineering use, a onereaction kinetic model is proposed for the pyrolysis of oil sludge, and is found to satisfactorily ®t the experimental data. The activation energy, reaction order and frequency factor of the corresponding pyrolysis reaction in nitrogen for oil sludge are 78.22 kJ mol À1 , 2.92 and 9.48 Â 10 5 min À1 , respectively. For precise use, the two-and three-reaction models are proposed to describe the pyrolysis results. Among the three models proposed, the three-reaction model gives the best ®t. These results are very useful for the proper design of the pyrolysis system of the oil sludge under investigation.