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Biomass reactions

Rate of reaction per unit volume of reactor Rates of reaction of D and G materials Rate of substrate reaction Local rate of reaction of substrate per unit volume of sphere Rate of biomass reaction Rate of reaction per unit area of biocatalyst Maximal rate of reaction based on unit area of biocatalyst... [Pg.435]

In the ongoing project on secondary biomass reactions in fixed-bed gasifiers the following issues will be pursued in the near future ... [Pg.160]

The catalyst employed was not reduced prior to the biomass reaction due to the results obtained in previous works (5,22) in which it was concluded that the gases generated in the thermal decomposition of biomass at 700 C have the ability to reduce the Ni/AI catalyst prepared by coprecipitation and calcined at 750 C. [Pg.348]

Up to now, only a few physical parameters such as temperature, pressure, and agitation, or basic chemical parameters such as pH, dissolved oxygen and CO2, are controlled on-line on a routine basis. Other important parameters, such as concentration of biomass, reaction products, substrates, and inhibitors, are more difficult to measure on-line, since suitable systems for their measurements have to fulfil strict requirements of selectivity, reliability, robustness, suitable detection range, and easy maintenance. [Pg.257]

Contents of all sugar and Klason lignin are based on untreated oven-dried biomass. Reaction condition flow rate of ammonia (15 wt%)=5.0 ml/min... [Pg.529]

Strongly positive Benedict s tests. These three biomass resources also did not wet easily and their protein content may have interfered with the hydrogenation. Other experimental details are given in reference 14. Table IL Selected Biomass Reaction Data ... [Pg.310]

Arena (J9) devised more active and more hydrothermally stable mixed titania supports for Ru hydrogenation of glucose at 120 °C. Elliot has recently developed an even longer activity Ru/Ti02 (rutile) catalyst (20). Operation at lower temperature (100 °C) and with pH neutral conditions (for glucose) obviously helps to extend catalyst life compared to the conditions required for the raw biomass reactions herein. However, the rutile-supported ruthenium might be less prone to absorption and is scheduled for IDAHH tests. [Pg.315]

Renewable carbon resources is a misnomer the earth s carbon is in a perpetual state of flux. Carbon is not consumed such that it is no longer available in any form. Reversible and irreversible chemical reactions occur in such a manner that the carbon cycle makes all forms of carbon, including fossil resources, renewable. It is simply a matter of time that makes one carbon from more renewable than another. If it is presumed that replacement does in fact occur, natural processes eventually will replenish depleted petroleum or natural gas deposits in several million years. Eixed carbon-containing materials that renew themselves often enough to make them continuously available in large quantities are needed to maintain and supplement energy suppHes biomass is a principal source of such carbon. [Pg.9]

Steam also is blended with air in some gasification units to promote the overall process via the endothermic steam—carbon reaction to form carbon monoxide and hydrogen. This was common practice at the turn of the nineteenth century, when so-called producer gasifiers were employed to manufacture LHV gas from different types of biomass and wastes. The producer gas from biomass and wastes had heating values around 5.9 MJ /mr at... [Pg.24]

Another hydrogenation process utilizes internally generated hydrogen for hydroconversion in a single-stage, noncatalytic, fluidized-bed reactor (41). Biomass is converted in the reactor, which is operated at about 2.1 kPa, 800°C, and residence times of a few minutes with steam-oxygen injection. About 95% carbon conversion is anticipated to produce a medium heat value (MHV) gas which is subjected to the shift reaction, scmbbing, and methanation to form SNG. The cold gas thermal efficiencies are estimated to be about 60%. [Pg.25]

Direct hydrohquefaction of biomass or wastes can be achieved by direct hydrogenation of wood chips on treatment at 10,132 kPa and 340 to 350°C with water and Raney nickel catalyst (45). The wood is completely converted to an oily Hquid, methane, and other hydrocarbon gases. Batch reaction times of 4 hours give oil yields of about 35 wt % of the feed the oil contains about 12 wt % oxygen and has a heating value of about 37.2 MJ /kg (16,000 Btu/lb). Distillation yields a significant fraction that boils in the same range as diesel fuel and is completely miscible with it. [Pg.26]

Thermochemical Liquefaction. Most of the research done since 1970 on the direct thermochemical Hquefaction of biomass has been concentrated on the use of various pyrolytic techniques for the production of Hquid fuels and fuel components (96,112,125,166,167). Some of the techniques investigated are entrained-flow pyrolysis, vacuum pyrolysis, rapid and flash pyrolysis, ultrafast pyrolysis in vortex reactors, fluid-bed pyrolysis, low temperature pyrolysis at long reaction times, and updraft fixed-bed pyrolysis. Other research has been done to develop low cost, upgrading methods to convert the complex mixtures formed on pyrolysis of biomass to high quaHty transportation fuels, and to study Hquefaction at high pressures via solvolysis, steam—water treatment, catalytic hydrotreatment, and noncatalytic and catalytic treatment in aqueous systems. [Pg.47]

Adsorption of Metal Ions and Ligands. The sohd—solution interface is of greatest importance in regulating the concentration of aquatic solutes and pollutants. Suspended inorganic and organic particles and biomass, sediments, soils, and minerals, eg, in aquifers and infiltration systems, act as adsorbents. The reactions occurring at interfaces can be described with the help of surface-chemical theories (surface complex formation) (25). The adsorption of polar substances, eg, metal cations, M, anions. A, and weak acids, HA, on hydrous oxide, clay, or organically coated surfaces may be described in terms of surface-coordination reactions ... [Pg.218]

Lime-Sulfuric. Recovery of citric acid by calcium salt precipitation is shown in Figure 3. Although the chemistry is straightforward, the engineering principles, separation techniques, and unit operations employed result in a complex commercial process. The fermentation broth, which has been separated from the insoluble biomass, is treated with a calcium hydroxide (lime) slurry to precipitate calcium citrate. After sufficient reaction time, the calcium citrate slurry is filtered and the filter cake washed free of soluble impurities. The clean calcium citrate cake is reslurried and acidified with sulfuric acid, converting the calcium citrate to soluble citric acid and insoluble calcium sulfate. Both the calcium citrate and calcium sulfate reactions are generally performed in agitated reaction vessels made of 316 stainless steel and filtered on commercially available filtration equipment. [Pg.183]

Ethyl Tertiary-Butyl Ether. Similar to methanol in the MTBE reaction, ethanol can react with isobutylene to produce ETBE. Which alcohol is used to make the ether is highly dependent on the relative cost of the alcohols. To make ethanol more economically competitive with methanol, the federal tax credit for biomass-based ethanol used in fuel also appHes to ethanol used to make ETBE in the United States (24). [Pg.429]

Supercritical fluid solvents have been tested for reactive extractions of liquid and gaseous fuels from heavy oils, coal, oil shale, and biomass. In some cases the solvent participates in the reactions, as in the hydrolysis of coal and heavy oils with water. Related applications include conversion of cellulose to glucose in water, dehgnincation of wood with ammonia, and liquefaction of lignin in water. [Pg.2005]

The laboratory studies utilized small-scale (1-5-L) reactors. These are satisfactoiy because the reaction rates observed are independent of reac tor size. Several reac tors are operated in parallel on the waste, each at a different BSRT When steady state is reached after several weeks, data on the biomass level (X) in the system and the untreated waste level in the effluent (usually in terms of BOD or COD) are collected. These data can be plotted for equation forms that will yield linear plots on rec tangular coordinates. From the intercepts and the slope or the hnes, it is possible to determine values of the four pseudo constants. Table 25-42 presents some available data from the literature on these pseudo constants. Figure 25-53 illustrates the procedure for their determination from the laboratory studies discussed previously. [Pg.2219]


See other pages where Biomass reactions is mentioned: [Pg.14]    [Pg.358]    [Pg.86]    [Pg.577]    [Pg.637]    [Pg.314]    [Pg.80]    [Pg.643]    [Pg.14]    [Pg.358]    [Pg.86]    [Pg.577]    [Pg.637]    [Pg.314]    [Pg.80]    [Pg.643]    [Pg.75]    [Pg.21]    [Pg.21]    [Pg.22]    [Pg.24]    [Pg.25]    [Pg.26]    [Pg.29]    [Pg.46]    [Pg.46]    [Pg.426]    [Pg.275]    [Pg.314]    [Pg.473]    [Pg.238]    [Pg.215]    [Pg.2215]    [Pg.2215]   
See also in sourсe #XX -- [ Pg.320 ]




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