NOx control through reburning1

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Abstract

Reburning is a process whereby a hydrocarbon fuel is injected immediately downstream of the combustion zone to establish a fuel-rich zone in order to convert nitric oxide to HCN. The reburning fuel can be gaseous (e.g., natural gas), solid (e.g., coal char or wood) or liquid (e.g., residual oil). Typically, the amount of reburning fuel used is 10–30% of the total fuel. This technology is practiced commercially with nitric oxide reduction levels of 35–65%, depending on the type and scale of the boiler or combustion, the primary and reburning fuels and other variables. Current research and development are suggesting several advanced reburning concepts including injection of ammonia or urea aft of the reburning fuel injection. Nitric oxide reductions of over 90% are anticipated. In this mini-review, a review of reburning technologies, measurements and mechanisms is presented. Predictive methods for reburning are also discussed. Recent work on reburning, including development of a global reburning reaction rate, is summarized, and results of application of a comprehensive combustion model to reburning measurements are summarized.

Introduction

Nitrogen oxides (NOx) have been recognized as acid rain precursors that impose a significant threat to the environment. Coal combustion is a major anthropogenic source of NOx. In coal combustion, NOx originates mostly from nitrogen bound in the coal matrix, namely, fuel-NOx[1]. Molecular nitrogen in air typically contributes less than 10% of overall NOx emissions from coal combustion[2]. Several technologies have been demonstrated to reduce NOx emissions during fossil fuel combustion, as summarized by Boardman and Smoot[3]and others. During the past decade, work on NOx formation and control has been substantial, including gas-phase and coal-phase NOx formation modeling and measurement, demonstration of very low NOx burner technologies, and prediction and measurement of NOx control through reburning. International work in NOx formation and control has been particularly extensive during this decade, as noted in reviews by Miller and Bowman[4], Hayhurst and Lawrence[5], Bowman[6], and Kramlich and Linak[7]. Among the most recent developments for reducing NOx emissions from coal systems are the reburning technologies, wherein gaseous, liquid or solid hydrocarbon fuels are injected downstream of the main combustion zone with NO and produce HCN3, 8, 9. Advanced reburning is an even more recent technology whereby ammonia, urea or similar substances are injected aft of hydrocarbon injection for reburning to further reduce NOx species[10]. Reburning and advanced reburning technologies are commercially available retrofit technologies, capable of providing 50%–85% NOx reduction beyond other combustion modifications. This paper provides a review of reburning work, including work at ACERC in the area of reburning.

No published review of reburning was located. However, a review chapter on reburning is reported to be forthcoming in a new encyclopedia[11]. To meet the requirements of the Clean Air Act Amendments of 1990 (CAA) within budget limitations and scheduling constraints, electric utilities have considered a variety of novel approaches to reduce NOx emissions from powerplants. Categories of NOx control options include burner replacement, combustion modifications, fuel staging, fuel reburning, steam or water injection, selective catalytic reduction (SCR), and selective non-catalytic reduction (SNCR)[12]. The efficiencies and limitations of various methods have been summarized by Boardman and Smoot[3]. Reburning technology is not fully understood theoretically, but it is a successful and commercially available retrofit technology, capable of providing 50%–70% NOx reduction beyond other combustion modifications[13]. Advanced reburning technologies are reportedly capable of greater reductions.

The reduction of NO by hydrocarbons was observed nearly half a century ago by Patry and Engel[14], and subsequently by Drummond[15]. This concept, and the term reburning, were first proposed by Wendt et al.[16]who noticed that, with the injection of CH4 just downstream of the primary flame zone, up to 50% of NO was reduced, as shown in Fig. 1. Myerson[17]proposed that the overall reactions for NO reduction by methane (and other hydrocarbons) could be written as:2NO+2CH4=2HCN+2H2O+H2+88kcal6NO+2CH4=2CO+4H2O+3N2+428kcal

Since this earlier work, much recent work has been completed in several countries. This work has included commercial demonstration, detailed laboratory measurement, and demonstration of improved and advanced reburning technologies. Also, work on understanding the kinetics of reburning and on predicting reburning effectiveness during turbulent fuel combustion has been studied. What follows is a brief review of this recent work, including work in process.

Section snippets

Technologies

Reburning was apparently first demonstrated as a practical NOx reduction method in Japan where the concept of reburning was first applied to a full-scale boiler by Mitsubishi in the early 1980s, more than 50% reduction of NO being achieved[18]. Babcock–Hitachi K.K. has also applied the technology successfully to numerous wall-fired utility boilers in Japan[19]. Because of these successful examples and the high efficiency of the reburning technology on the reduction of NOx emissions, many

Measurements

Some experimental results with gas-based reburning in the U.S. are discussed below. Marion, et al.[36]have shown that greater than 50% NOx reduction was achieved with gas reburning in ABB–CE's Boiler Simulation Facility, which allows for carefully controlled experiments at a sufficient scale to replicate the reburning process in full-scale units. Wendt and Mereb[37]have completed a number of laboratory-scale, gas-based reburning tests which consist of numerous premixed-flame cases and a few

Mechanisms and rates

Wendt[42]has recently published a review of mechanisms governing the formation and destruction of NOx. NO reduction through the reburning-NO mechanism usually includes the interactions of HCN and NO species, as described in the elementary reaction steps of reburning noted by Wendt et al.[16]. Under fuel-rich conditions, the formation of HCN relies strongly on the concentration of hydrocarbon species,CHi+NOHCN+…which then decays through NCO→NH→N, as shown in , , , and ultimately reaches N2 via

Predictive methods

While several predictive models for formation of NO through modeling of thermal and fuel processes have been developed (e.g., Boardman and Smoot[3]), until recently there has been little published work on destruction of NO through reburning processes. Several approaches to predict reburning-NO are being considered and models are now becoming available.

Mereb and Wendt[8]simplified the detailed kinetic mechanism of Glarborg et al.[80]for natural gas reburning, and then developed an engineering

Reburning model applications

Chen[72]used PCGC-2 to initially evaluate the NOx submodel with the global reburning reaction. Two laboratory-scale reburning cases from Mereb and Wendt[8]were simulated. The predicted NO profiles were consistent with the measured results.

NOx predictions including the reburning reaction (Eq. (22)) have also been made with a comprehensive combustion model, PCGC-3, which incorporated the NOx submodel of Fig. 9[93]. PCGC-3 is a generalized, comprehensive, three-dimensional, steady-state combustion

Summary

Reburning, the process whereby gaseous, liquid or solid hydrocarbon is injected downstream of the combustion zone to reduce NO to HCN, is a commercialized technology. First tested in about 1950 and named in 1973, it has been commercially demonstrated in very large-scale utility boilers. It has also been demonstrated in four of the Clean Coal Technology programs. Typically, 10–30% of the total fuel is used as the reburn fuel.

Reburning with natural gas, without other NOx control technologies, can

Acknowledgements

Some of this research and preparation of this review paper were sponsored by the Advanced Combustion Engineering Research Center. Funds for this center are received from the National Science Foundation (Engineering Education and Centers Division), the State of Utah (Centers of Excellence), 37 industrial participants, and five federal agencies. The authors express their gratitude to all of the above, the University of Utah, Dr Dale Tree, Mechanical Engineering at BYU, Dr William Bartok,

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    1

    This mini-review paper was presented, together with a series of other review papers, at the Tenth Annual Technical Conference of the Advanced Combustion Engineering Research Center, held in Salt Lake City, Utah, in March 1997.

    2

    Professor, Chemical Engineering; Director, ACERC.

    3

    Research Associate; Head, Combustion Computations Laboratory.

    4

    Graduate Research Assistant, Chemical Engineering.

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