Skip to main content
Much less attention has been paid to bubbling fluidized bed combustion, BFBC, partly because of scaling-up problems. However, small BFBC units have many advantages for applications such as the use of biomass, wood waste, and different... more
Much less attention has been paid to bubbling fluidized bed combustion, BFBC, partly because of scaling-up problems. However, small BFBC units have many advantages for applications such as the use of biomass, wood waste, and different locally produced combustibles. Recent work focused on gaseous and liquid fuels, of various chemical characters. BFBC combustion efficiency can be high, with the flue gases cleaner than the usual with conventional burners. During flameless combustion of CH4 at over 900°C, CO, CxHy, and NO2 were produced only at the trace level of about 1 ppm. NO was under 15 ppm and did not increase when the temperature was raised to 1070°C. With the laboratory size BFBC, the flue gas concentrations of CO, CxHy, NO, and NO2 were similar as with CH4 fuel. With chlorine present as a result of CCl4 addition at below 950°C, CO emissions increased, and NO was unaffected.
Research Interests:
There is no full thermodynamic equilibrium in FBC reactors and catalytic effects are possible. Such phenomena were observed in the presence of halogens and halides (other than fluorine and fluorides) and as for flames, were interpreted in... more
There is no full thermodynamic equilibrium in FBC reactors and catalytic effects are possible. Such phenomena were observed in the presence of halogens and halides (other than fluorine and fluorides) and as for flames, were interpreted in terms of catalytic cycles. This led to the development of the iodine method for studying processes dependent on above equilibrium free radical concentrations in FBC systems and several groups have made use of it. When gaseous hydrocarbons or combustible vapours, premixed with air, are burned in a bubbling bed, other kinetic effects appear, such as NO and NO2 formation. Fuels burning at 800–950oC, cannot give much thermal NO. The temperatures are too low and times short and [NO] falls with increasing O2, with little temperature dependence. An alternative to the thermal mechanism is the “prompt” one, with NO primary and NO2 secondary. The NO2 forms at lower temperatures, at high [CO], which is explained in terms of relative rates of chain branching, ...
The paper presents the results from studies on co-combustion of dry, “high” calorific value wastes with/without supplementary fuels. Two fluidisation techniques were employed, circulating and bubbling, in facilities of three sizes; a... more
The paper presents the results from studies on co-combustion of dry, “high” calorific value wastes with/without supplementary fuels. Two fluidisation techniques were employed, circulating and bubbling, in facilities of three sizes; a bench scale circulating fluidized bed combustor (CFBC) designed to burn coal and two were bubbling fluidised bed reactors (BFBC): ~100 kWth with a ceramic-lined combustion chamber and outer insulation of the freeboard and 1MWth insulated reactor burning wastes. Tests have been carried out in the CFBC reactor using coal or pelletised Refuse Derived Fuels (RDF) separately or mixed together. Municipal Segregated Wastes (MSW) alone and mixed with Wood Waste (WW) were burned in the BFBC reactors. In the BFBC experiments, continuous records were obtained of temperature and flue gas concentrations of O2, CO, SO2, NO, NO2 and VOC. With the CFBC unit, continuous measurements of temperature, bed pressure at different heights and concentrations of O2, CO, SO2, NO,...
ABSTRACT In 1980s change in meat and bone meal production technology led to the spread of BSE and massive culling of beef cattle in many countries. Adding meat and bone meal to animal feed was banned, but animal carcasses still have to be... more
ABSTRACT In 1980s change in meat and bone meal production technology led to the spread of BSE and massive culling of beef cattle in many countries. Adding meat and bone meal to animal feed was banned, but animal carcasses still have to be disposed of. In this work the operational parameters and efficiency of a utilisation process for raw meat wastes and emissions of CO, NOx, SO2 and VOC were studied. A 5 kW thfluidised bed combustor was used and tests were repeated in a 150 kW th (KFD-s14u) boiler, with combustion of meat wastes (biomal). With combustion, the heat generated can be recovered, the meat waste is completely burned, bone pieces mineralised and fragmented and flue gas composition is similar to that with coal alone. The potential of the technology for raw meat waste utilisation has been demonstrated on a technical scale, with waste throughput of 180 kg/h*m2 (with respect to distributor area) and factors limiting the combustion efficiency have been determined. An installation (up to 3 MW thermal) has been designed for the utilisation of 500 kg/h of raw meat waste in co-combustion with coal. The installation should fulfil the requirements with respect to waste utilisation efficiency and thermal energy production.
It is always better to prevent the formation of PAH than remove them from the flue gases. Burning polymer waste in a fluidized bed, with plenty of oxygen and efficient mixing could be promising. Polymer pellets were burned in a bed of... more
It is always better to prevent the formation of PAH than remove them from the flue gases. Burning polymer waste in a fluidized bed, with plenty of oxygen and efficient mixing could be promising. Polymer pellets were burned in a bed of glass making sand, fluidized with a mixture of air and propane. The pellets were dropped into the reactor operating under steady conditions and the effect on O2 consumption, CO2 and CO production, total hydrocarbon, and NOx emissions was monitored. The combustion of a pellet depends on the thermal decomposition of the polymer and burning of the volatile decomposition products. The pyrolysis was fast and a local streak of fuel-rich gases appeared. The efficient oxidation of these depends on the local availability of O2 and the efficiency of mixing. With larger pellets, the importance of the initial "background" increased. At higher temperatures the rate of the oxidation of the intermediates increases, but their rate of production also increases which outweighs the benefit of higher reaction rates. Original is an abstract.
Working with a small, bubbling laboratory scale fluidised bed combustor for many years, helped to gain some insights into the fundamental physicochemical processes taking place in fluidised bed combustors in general, irrespective of size.... more
Working with a small, bubbling laboratory scale fluidised bed combustor for many years, helped to gain some insights into the fundamental physicochemical processes taking place in fluidised bed combustors in general, irrespective of size. For example, it has been demonstrated that during coal combustion as a rule the gases leaving the bed cannot be assumed to be at full thermal equilibrium and that when gases are burned the associated acoustic and visual phenomena can be explained in terms of bubbles of the combustible ...
ABSTRACT Fluidised bed combustion (FBC) is a technology which can use waste materials and low quality fuels along with coal. Mixed with wastes, coal can burn more efficiently. The present study aimed at the co-combustion of refuse derived... more
ABSTRACT Fluidised bed combustion (FBC) is a technology which can use waste materials and low quality fuels along with coal. Mixed with wastes, coal can burn more efficiently. The present study aimed at the co-combustion of refuse derived fuels (RDF) with coal in a bench scale circulating fluidised bed combustor (CFBC). Tests were carried out at different ratios of RDF/coal at temperatures from 830 to 960 degrees C. Compared with coal alone, RDF - coal mixtures gave a more uniform temperature distribution in the combustor and the emissions were lower when burning. Improved efficiency and stability of co-combustion were attributed to the higher volatile matter content in RDF. However, the advantages could be lessened if a too high secondary air ratio was used. NOx and SO2 emissions were due to the presence of S ( mainly in the coal) and fuel N ( more than S) in both fuels. The SO2 concentration decreased with increasing RDF rich in Ca in the fuel. It was shown that CFBC units could burn RDF efficiently and cleanly.
ABSTRACT The process of selective non-catalytic reduction of NO, SNCR, is important for limiting emissions of nitrogen oxides from coal-fired power plants. Such a process has been studied for many years, both in the laboratory and under... more
ABSTRACT The process of selective non-catalytic reduction of NO, SNCR, is important for limiting emissions of nitrogen oxides from coal-fired power plants. Such a process has been studied for many years, both in the laboratory and under practical conditions. This work was an attempt at elucidating some of the problems associated with the method when used under circulating fluidized bed (CFB) conditions and in particular, the formation of the N2O by-product. The NO + NH3 reaction has been studied in the laboratory, over quartz sand in a heated fixed bed flow reactor. In comparison with a combustion environment, the composition of the gas phase was drastically simplified and limited to NO and NH3, in nitrogen as the carrier gas, with O2 added in some experiments. The product gases were analyzed for NO, N2O and NH3. The effects the following parameters were studied: temperature inside the reactor between 850 and 1250 K, height of the sand bed, NH3/NO molar ratio over the range 0.54–2.0 and the addition of 1 or 2% of O2 in volume. Baseline tests with an empty reactor were also made. With no sand in the reactor, the results were both qualitatively and quantitatively different. The sand helped to increase the efficiency of NO reduction, particularly at lower temperatures, but N2O formation also appeared to be strongly enhanced, except at the highest temperatures. Higher molar NH3/NO ratios favored NO reduction and N2O production, both with and without sand. The reduction of NO did not appear to require the presence of O2, but the introduction of 1% or 2% of O2 gave some benefit. The results confirmed that under practical conditions more attention should be paid to the role of the bed solids in the SNCR process.
A laboratory size quartz reactor has been used to burn methane, LPG (liquid petroleum gas) and aromatic hydrocarbon vapors in a bubbling fluidized bed. Most measurements and observations were made for lean mixtures of fuel and air with... more
A laboratory size quartz reactor has been used to burn methane, LPG (liquid petroleum gas) and aromatic hydrocarbon vapors in a bubbling fluidized bed. Most measurements and observations were made for lean mixtures of fuel and air with quartz sand in the bed, but in some experiments NO, NO2, or CCl4 were introduced with the fuel, the stoichiometry was varied or the bed material changed. The quantities monitored were the bed temperature at two levels and the freeboard concentrations of O2, CO2, CO, NO, NO2, and in some runs, ...
The combustion of fuel-lean mixtures of methane+ air in a strongly bubbling fluidized bed of quartz sand has been studied in the laboratory. Video color images of the burning bed, at 25 frames/s, were examined and used to obtain images in... more
The combustion of fuel-lean mixtures of methane+ air in a strongly bubbling fluidized bed of quartz sand has been studied in the laboratory. Video color images of the burning bed, at 25 frames/s, were examined and used to obtain images in three color bands, red, green, and blue. A mathematical procedure was then employed to analyze the color images further, to discriminate between continuous radiation from the hot sand and discrete emission, mostly in the blue wavelength region, from bubbles exploding inside the bubbling bed or at its ...
The migration of selected heavy metals has been analysed when sewage sludge from a municipal waste water treatment plant was burned in a bubbling fluidised bed. It has been shown that manganese, lead, arsenic, mercury and cadmium, as... more
The migration of selected heavy metals has been analysed when sewage sludge from a municipal waste water treatment plant was burned in a bubbling fluidised bed. It has been shown that manganese, lead, arsenic, mercury and cadmium, as opposed to chromium, nickel and copper, leave the reactor mainly via the gas phase. To reduce the emissions of heavy metals to the atmosphere associated with the thermal utilization of sewage sludge requires more effective flue gases cleaning than is possible with filters.
Results are presented, obtained when sewage sludge was burned in a purpose-designed industrial installation, comprising a 1.5 MW bubbling fluidised bed combustor. Dried sewage sludge was used in the tests. The combustion process was... more
Results are presented, obtained when sewage sludge was burned in a purpose-designed industrial installation, comprising a 1.5 MW bubbling fluidised bed combustor. Dried sewage sludge was used in the tests. The combustion process was stable, and since the moisture content of the dried sludge was low, no auxiliary fuel was required. Analysis of the flue gases has shown that the concentrations of SO2 and NOx are somewhat elevated, on account of rather high combined S and N content in the sludge. The results have ...
Much of air pollution is due to burning of fossil fuels, but some purpose-produced biofuels and biowastes can be burned very cleanly. Historic towns should maintain high standards of air purity, but deriving all heat and power from... more
Much of air pollution is due to burning of fossil fuels, but some purpose-produced biofuels and biowastes can be burned very cleanly. Historic towns should maintain high standards of air purity, but deriving all heat and power from burning of biomass cannot be feasible, but using some biowastes can help locally, with savings on energy transport and flue gas cleaning systems. It can also contribute to reducing greenhouse emissions. This has been demonstrated, eg, at Niepołomice where several types of waste have been effectively and ...
The paper presents the results from a study of the combustion of wastes of animal origin-feathers and meat and bone meal in a 1.5 MW bubbling fluidised bed reactor. The process of thermal utili-sation is stable and short-term fluctuations... more
The paper presents the results from a study of the combustion of wastes of animal origin-feathers and meat and bone meal in a 1.5 MW bubbling fluidised bed reactor. The process of thermal utili-sation is stable and short-term fluctuations on the composition of the wastes are not a problem, since the operational parameters of the combustor are constantly monitored and controlled. The process does not require conventional supporting fuel and the level of CO in the flue gases is com-parable to that observed with some low quality ...
A 100 kW atmospheric, bubbling fluidised bed reactor was used to study the combustion of wood waste, sewage sludge and a mixture of sewage sludge and meat-and-bone meal. Steady operation of the combustor was possible, even if the fuel was... more
A 100 kW atmospheric, bubbling fluidised bed reactor was used to study the combustion of wood waste, sewage sludge and a mixture of sewage sludge and meat-and-bone meal. Steady operation of the combustor was possible, even if the fuel was abruptly changed. With sewage sludge, the flue gas concentrations of SO2 and NOx were relatively high, as the sludge fuel contained much higher concentrations of combined S and N than eg wood waste. Co-combustion of sewage sludge and meat-and-bone meal presented no ...
Some of the very damp sludge can be partly replaced by the second waste fuel, irrespective of its physical state (solid, liquid or gaseous). Candidate supporting fuels are, e.g., the biomass by-products of the maintenance of vegetation... more
Some of the very damp sludge can be partly replaced by the second waste fuel, irrespective of its physical state (solid, liquid or gaseous). Candidate supporting fuels are, e.g., the biomass by-products of the maintenance of vegetation within the city (street trees, parks, etc.), partly segregated municipal solid waste (MSW), or even animal waste. A pilot installation, 1 Mw, was designed, with some of the heat produced employed in the gas cleaning system and for heating the premises used by the technical staff and for providing hot water. The combustor is equipped with feed systems for the sewage sludge and for the supporting fuels. An automatic process control system was developed. The effect of bed temperature and air excess on the flue gas composition and the degree of mineralisation of the sewage sludge was assessed. The flue gas concentrations monitored were: O2, CO, NO, NO2, and SO2 (using ECOM®-SG Plus instrument, with electrochemical sensors), VOCs (JUM® working on the FID principle). The mean flue gas concentrations of CO and VOC were 200 ppm and 124 mg/cu m respectively. The presence of SO2 and NOx was due to the presence of combined sulfur and nitrogen in the fuel, most likely in organic form. This is an abstract of a paper presented at the 30th International Symposium on Combustion (Chicago, IL 7/25-30/2004).
Research Interests: