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Energy wasted

The overall requirement is 1.0—2.0 s for low energy waste compared to typical design standards of 2.0 s for RCRA ha2ardous waste units. The most important, ie, rate limiting steps are droplet evaporation and chemical reaction. The calculated time requirements for these steps are only approximations and subject to error. For example, formation of a skin on the evaporating droplet may inhibit evaporation compared to the theory, whereas secondary atomization may accelerate it. Errors in estimates of the activation energy can significantly alter the chemical reaction rate constant, and the pre-exponential factor from equation 36 is only approximate. Also, interactions with free-radical species may accelerate the rate of chemical reaction over that estimated solely as a result of thermal excitation therefore, measurements of the time requirements are desirable. [Pg.56]

Machining is expensive - in energy, wasted material and time. Forming routes which minimise or avoid machining result in considerable economies. [Pg.154]

The heat exehanger temperature differenee wastes i6.4 Btu of work. Aiso, there is an estimated 4.49 Btu of flash energy wasted when the 200 psi iiquid is flashed to atmospherie pressure. These two drains on the theoretieai work, amounting to 20.89 Btu, are dedueted ieaving... [Pg.49]

Another feature of many (though not all) lasers is a cooling system to dissipate energy wasted m the form of heat. Although some are much more efficient than others, all lasers waste significant amounts of energy. For example, a CO, laser (the most popu-... [Pg.703]

Rumen methanogenesis is a necessary but energy-wasteful process as it corresponds to a significant loss of biological dietary energy (6-12% of intake) in the form of CH4. [Pg.249]

Similarly, the reaction of photoexcited 9,10-dicyanoanthracene (DCA) with a benzylstannane yields the contact ion pair in which the cation radical undergoes rapid mesolytic cleavage of the C—Sn bond to afford benzyl radical and tributyltin cation (which then adds to DCA- )77 (Scheme 14). When such unimolecular processes are faster than the energy-wasting back electron transfer (/cbet) within the contact ion pair, the D/A reactions occur rapidly despite unfavorable driving forces for electron transfer. [Pg.229]

The thermal and photochemical activations of EDA complexes by electron transfer are both enhanced when the radical ions D+- or A--(either paired or free) undergo a facile first-order (unimolecular) transformation such as fragmentation, rearrangement, bond-formation, etc., which pulls the redox equilibrium and thus renders the competition from the energy-wasting back electron transfer less effective (compare Scheme 5). Critical to the quantitative evaluation of the reaction dynamics is the understanding that the typical [D+% A--] intermediates, as described in... [Pg.264]

The protective method has also been employed with 3-ketoesters. In this case, the goal is to avoid keto-enol photoisomerization that is an efficient energy-wasting channel. Scheme 74 shows that direct photorearrangement of aryl benzoyl acetates (298) to the ort/jo-hydroxydibenzoylmethanes (299) is poor, whereas irradiation of the related acetal derivatives gives higher yields [208]. The resulting ort/ o-hydroxydibenzoylmethanes are precursors for the synthesis of flavones. Related flavonoids can be obtained in similar yields by PFR of aryl dihydrocinna-mates [209]. [Pg.109]

Energy, waste and the environment - a geochemical perspective introduction... [Pg.1]

From. Giere, R. Stilee, P. (eds) 2004. Energy, Waste, and the Environment a Geochemical Perspective. Geological Society, London, Special Publications, 236, 1-5. [Pg.1]


See other pages where Energy wasted is mentioned: [Pg.12]    [Pg.249]    [Pg.390]    [Pg.94]    [Pg.313]    [Pg.134]    [Pg.19]    [Pg.97]    [Pg.126]    [Pg.2]    [Pg.95]    [Pg.95]    [Pg.136]    [Pg.327]    [Pg.344]    [Pg.464]    [Pg.711]    [Pg.719]    [Pg.264]    [Pg.16]    [Pg.224]    [Pg.175]    [Pg.370]    [Pg.165]    [Pg.169]    [Pg.30]    [Pg.684]    [Pg.214]    [Pg.216]    [Pg.222]    [Pg.289]    [Pg.428]    [Pg.636]    [Pg.230]    [Pg.289]    [Pg.90]    [Pg.83]    [Pg.239]    [Pg.3]    [Pg.5]   
See also in sourсe #XX -- [ Pg.803 , Pg.804 , Pg.824 , Pg.834 ]

See also in sourсe #XX -- [ Pg.850 ]

See also in sourсe #XX -- [ Pg.778 , Pg.779 , Pg.801 , Pg.810 ]




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Biomass energy waste

Corrosion environment of waste-to-energy boilers

Energy content, biomass wood wastes

Energy from waste conversion

Energy from waste conversion process

Energy potential, biomass municipal solid wastes

Energy production waste

Energy recovery from waste gasification

Energy recovery from waste solvent

Energy recovery from wastes

Energy recovery mining waste

Energy recovery waste tyres

Energy recovery waste-heat boilers

Energy recovery, waste handling

Energy sources municipal solid wastes

Energy waste

Energy wasting back reactions

From Plastic Waste to Feedstocks and Energy by Means of Fluidized-bed Pyrolysis

Gaseous wastes energy recovery from

High energy level waste

Liquid wastes energy recovery from

Municipal Solid Waste Incinerators (with Energy Recovery)

Nuclear energy waste

Nuclear energy waste from

Organic waste energy

Plastic wastes energy recovery

Polyethylene Recycling - Waste-to-Energy

Prospects, Challenges, and Opportunities for Energy Recovery from Wastes

Solid wastes energy recovery from

WASTE-TO-ENERGY

Waste biomass energy content

Waste biomass energy contribution

Waste biomass energy potential

Waste energy Applied Science

Waste management energy recovery from

Waste to energy conversion

Waste tyres energy source

Waste-to-energy facilities

Waste-to-energy incineration

Waste-to-energy plants

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