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Brown coal combustion

Brown Coal Power Plant Scrubber residues. Solidification, sta- Brown coal combustion residues... [Pg.202]

It seems promising to extend these investigations to other PAH emissions such as hard coal, heating oil, and brown coal combustion to find specific markers for the various emission sources ... [Pg.112]

The total annual output of fly ash in Poland is about 20 million tons (in 2008 over 26 miUion tons) of fly ash fiom the black coal combustion and about 9 million tons of fly ash from the brown coal combustion respectively. The production of fly ash cements started in XX c. in late sixties. The annual fly ash consumption attains 1400 thousands tones. The three types of fly ash generated in the pulverized fuel combustion (frequently determined as conventional ones) can be distinguished (Table 7.3) those from the black coaf from the brown coal in Turoszbw coal-field as well as from the Konin and Belchatow coal-field. [Pg.556]

Component Fly ash from black coal combustion from power plant Fly ash from brown coal combustion from power plant ... [Pg.557]

This classification is not perfect, unlike the other classifications for example the calcareous fly ash is not distinguished regarding the differences of anhydrite content (SO3). As it results from the analysis presented in Table 7.3, the fly ash from Belchatow could be even used in the production of CEM n/B-V cement, after CaO transformation into the calcium hydroxide, while the fly ash from Konin only in a limited range, because of the SO3 content. The transition of CaO to Ca(OH)2 is necessary, because in the PN-EN 197-1 standard the reactive CaO content in fly ash is restricted to 10%. The aforementioned classification rates Polish fly ash from the hard coal combustion to the siliceous ash and that from the brown coal combustion in Turoszow coal-field— to the aluminous ones respectively. [Pg.557]

Glass in the fly ash from the brown coal combustion is much more differentiated... [Pg.561]

It is important to pinpoint the PAH source even in an environment where more than one pollutant source is evident. The following source-specific compounds have been used cyclopenta(cd)pyrene for automobile exhaust benzo(6)naphtho(2,l-d)thio-phene for hard coal combustion picene derivatives for brown coal combustion, and l-methyl-7-isopro-pylphenanthrene (retene) for wood combustion. [Pg.3781]

Because of the wide variation in composition and properties of brown coal (see Table 3), efficient combustion of these fuels caimot be accomphshed by a single system. The moisture content limits combustion efficiency because some chemical energy is required to convert Hquid water to steam in the flue gases. The steam then increases the dew point of the gases, requiring higher temperatures to avoid condensation in the stack. For fuels up to 25% moisture content, 80% efficiency can be achieved. As the moisture content increases to 60%, the efficiency decreases to 70% and efficiency continues to decline about another 1% for each additional 1% moisture to 70%. [Pg.156]

The moisture content of peat or brown coal that is briquetted for fuel must be reduced to about 15% for satisfactory briquetting. Mechanical or natural means are used because of the cost of thermal drying. Moisture is sometimes desirable. About 8% is necessary for prevention of combustible loss from a chain-grate stoker. [Pg.222]

This formulation is proposed as a complete treatment, comprising powdered and crystalline combustion catalysts and slag modifiers. It is designed for pulverized fuel (PF), brown coal, lignite, peat moss, and bark, and for application with cyclone burners, chain grates, underfed, and spreader stokers. [Pg.687]

The action of organic solvents on natural polymers combustible minerals (coal and brown coal or peat) is intensively studied for a long time due to following reasons. Firstly, this is one of the successful method of studying the structure of combustible materials and the second is their technological application for obtaining of a so-called montan-wax or low-molecular liquid extracts which can be transformed into synthetic liquid fuel due to hydration process. Moreover, an interaction of a coal with the solvents is a basis of the coals liquation processes and coals transformation into liquid fuel. [Pg.52]

Sahu, S., Brown, S. A. Lee, R. J. 2002. Thaumasite formation in stabilized coal combustion byproducts. Cement and Concrete Composites, 24, 385-391. [Pg.657]

The addition of lime to control acid drainage from mining wastes typically produces calcium arsenates (Pichler, Hendry and Hall, 2001). Bothe and Brown (1999) further concluded that lime precipitates As(V) as a number of hydroxyl and hydrated calcium arsenates (Ca4(OH)2(AsC>4)2 4H2O, CaslAsCLLOH (arsenate apatite), and/or Ca3(AsC>4)2 3H2O) rather than anhydrous tricalcium orthoarsenate (Ca3(As04)2). Calcium arsenates also occur in coal combustion byproducts (Chapter 7). In the flue gas treatment systems of coal combustion facilities, volatile arsenic can readily react with calcium to form the arsenates on the surfaces of flyash and injected lime (Seames and Wendt, 2000 Yudovich and Ketris, 2005, 175). [Pg.110]

Figure 12 Theoretical and experimental NO emissions at coal combustion that were calculated by model (90)—(95) (curve 7) and presented in the work by Gorban (2001,2006) equilibrium (1), maximum (2) actual (3-6) fluidized bed combustion (3), low-temperature combustion of brown coals (4), high-temperature combustion of hard coals (5), averaged for coal-fired boilers (6) A— prompt NO, B— fuel NO, C— thermal NO. Figure 12 Theoretical and experimental NO emissions at coal combustion that were calculated by model (90)—(95) (curve 7) and presented in the work by Gorban (2001,2006) equilibrium (1), maximum (2) actual (3-6) fluidized bed combustion (3), low-temperature combustion of brown coals (4), high-temperature combustion of hard coals (5), averaged for coal-fired boilers (6) A— prompt NO, B— fuel NO, C— thermal NO.
It has been recognized for many years that exposure of coal to air can significantly alter the processing characteristics of the coal. This effect is more pronounced in lower rank coals and in fact some brown coals will undergo spontaneous combustion at or near ambient temperatures. [Pg.92]

The chemical characteristics of Latrobe Valley brown coals have been extensively studied over the last twenty-five years, primarily in relation to the effect of coal quality on combustion for power generation. More recently a research project was initiated with the objective of determining the characteristics and suitability of the State s brown coal resources for uses other than power generation, primarily conversion to liquid fuels. [Pg.3]

Aluminium and Precipitator Ash. In some Victorian brown coals significant quantities of acid-soluble aluminium are found. This is believed to be present as aluminium hydroxide which is dispersed throughout the water phase of the coal. During combustion of this coal, the refractory aluminium oxide formed takes the shape of the relics of the plant material present in the coal, thus forming an extremely low density ash (approximately 100 kg/m ). Whilst the collection of these particles by electrostatic precipitation is possible, the problem of reentrainment on rapping has necessitated the use of larger sized units than would otherwise be required. It is therefore important to determine the acid soluble aluminium fraction in the coal to determine if precipitation of fly ash is likely to be a problem. [Pg.14]

Chemical composition of waste plastic cracking products depends on shares of the individual polymers (PE, PP, PS) in the feed and process parameters. This fact decides the technological application of the final products. Important products of the cracking process, both petroleum fractions and waste plastics, are coke residues. Coke residue yield increases considerably, up to 10 wt%, in cracking of municipal and industrial waste plastics since they contain various inorganic impurities and additives. It can be applied as solid fuel, like brown coal. In the fluid cracking the solid residue is continuously removed from the process by combustion in a regenerator section. [Pg.112]

The cyclone combustion chamber. Here the air is injected tangentially into a usually cylindrical chamber and exhausts through a centrally located exit hole at one end. The cyclone combustors are usually used to bum eflBciently diflBcult-buming materials such as high-ash-content and brown coals, anthracite, high-sulFur-content oils, damp vegetable refuse, poor-quahty-low-calorific-value fuels, etc. [Pg.95]

The test rig at IVD (50 kWth) and the Delft PDU (1.5 MWth) were operated successfully with respect to pressurised gasification, high temperature gas cleanup and combustion of biomass (wood and Miscanthus) and brown coal derived LCV gas. [Pg.486]

Further research work is necessary to extensively determine the influence of the biomass fuel type used and synergistic effects of brown coal/coal as additive to biomass with respect to Carbon conversion, tar formation and NO, precursor formation. Also, gasification modeling is further optimised and validated with these and more experimental data to describe the basic processes of drying, devolatilisation, partial combustion and gasification. [Pg.486]

Mcschgbiz A, Kakaras E Krumbeck M. (1995), Combined Combustion of Biomass and Brown Coal in a Pulverized Fuel and Fluidized Bed Combustion Plant, 3" European Conference on Industrial Furnaces and Boilers, LisbonTPortugal. [Pg.798]

After the reserves of high quality coal have been exhausted, it will be necessary to use brown coals with more impurities. Extremely high-ash coals with high alkaline contents must be used in some countries even though the performance of such fuels could not be controlled with the combustion technologies available in the past. [Pg.394]

Schneider (9 ) with brown coals of different origin in a drop tube furnace similar to that used by Field clearly showed the influence of different mineral substances on ash deposition. Sand particles (Figure 2) maintained their former shape in combustion or showed changes only at their edges while other ash constituents fused together into dark brown or glassy-clear spheres. [Pg.397]

Pilot scale combustion techniques were also used to estimate the performance of brown coals. The Field tube is limited for estimating performance of brown coals and was supplemented by a cyclone combustor. The cyclone combustor allows combustion of the larger particles with longer residence times typical of brown-coal-fired boilers. [Pg.407]

M.V. Lomonosov was one of the first scientists to introduce a reasonable scientific concept of the origin of petroleum. In his mid-eighteenth century work on terrestrial layers , this Russian scientist wrote It is expelled from underground with heat, prepared from stone coal and brown coal, this black oily material... And this is a birth of a different grade of combustible liquid and dry hard matter. This is the essence of stone oil, liquid pitch, petroleum, and similar materi-... [Pg.13]


See other pages where Brown coal combustion is mentioned: [Pg.534]    [Pg.234]    [Pg.534]    [Pg.234]    [Pg.1]    [Pg.155]    [Pg.96]    [Pg.115]    [Pg.1]    [Pg.713]    [Pg.401]    [Pg.48]    [Pg.4]    [Pg.13]    [Pg.21]    [Pg.69]    [Pg.243]    [Pg.396]    [Pg.307]    [Pg.425]    [Pg.305]    [Pg.798]    [Pg.510]    [Pg.512]   
See also in sourсe #XX -- [ Pg.101 ]




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