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Effect on Emission

Would you expect to find the same chemical composition of the hydrocarbons from the exhaust of a gasoline-powered automobile as that of gasoline in the vehicle s tank Why What would be the effect on emissions from a gasoline-powered vehicle if it was designed to be operated on leaded fuel and an unleaded fuel was used ... [Pg.530]

What would be the effect on emissions from a gasoline-powered vehicle if it was designed to be operated on unleaded fuel and a leaded fuel was used ... [Pg.530]

Jones, G., Jackson, W.R., Choi, C.Y., and Bergmark, W.R. (1985) Solvent effects on emission yields and lifetime for coumarin laser dyes. Requirements for the rotatory decay mechanism.. Phys. Cbem. 89, 294. [Pg.1080]

Shifts in absorption spectra due to the effect of substitution or a change in environment (e.g. solvent) will be discussed in Chapter 3, together with the effects on emission spectra. Note that a shift to longer wavelengths is called a bathochromic shift (informally referred to as a red-shift). A shift to shorter wavelengths is called a hypsochromic shift (informally referred to as a blue-shift). An increase in the molar absorption coefficient is called the hyperchromic effect, whereas the opposite is the hypochromic effect. [Pg.32]

Tab. 3.3. Heavy atom effect on emissive properties of naphthalene (from Wehry, 1990)... Tab. 3.3. Heavy atom effect on emissive properties of naphthalene (from Wehry, 1990)...
Decree Implementation Heat Balance Effects on Emissions.271... [Pg.404]

This illustrative study, using the new approach to CDPF emissions modelling, shows that PGM distribution can have a significant effect on emissions. In later work, with improved kinetics that more closely describe the real-world system performance, it has been shown that very great cost savings can be achieved by correctly zoning the CDPF (York et al., 2008). [Pg.97]

We should point out that the temperature effects on emission intensity and photocurrent are completely reversible. Although this result suggests that electrode stability obtains over the duration of the experiments, the properties measured may not be very sensitive to variations in surface or near-surface composition. There is now considerable evidence, in fact, that surface reorganization processes do occur in CdS- and CdSe- based PECs in polychalcogenide electrolytes (17, 21-26). In particular, the occurrence of such an exchange reaction for CdS Te in polyselenide electrolyte would yield CdSe to whose lower band gap... [Pg.300]

Methylcyclopentadienyl manganese tricarbonyl (MMT) is an additive in many commercial unleaded gasolines, and thus its potential effect on catalyst performance is an important consideration. It was reported by Faggan et al. 8) that MMT at a recommended level of 0.125 g Mn/gal shows no adverse effect on emissions, when compared to unleaded gasoline, in tests on cars operated on the 50,000-mile EPA certification schedule. These findings have been confirmed by a number of unpublished test reports from several industrial laboratories. In fact, it is indicated that some of the manganese deposits can aid catalytically in the removal of CO, and possibly to some extent also of hydrocarbons. The consequence of such a catalytic effect of Mn has still to be explored. [Pg.351]

The HAZOP study was instrumental in determining the need for an adequate alarm system on each of the specified controllers. If liquid levels within the column are not well controlled, then either flooding (too much liquid) or plate by-passing bythegas (too little liquid) will occur. Both situations lead to a substantial reduction in absorption efficiency with large increases in emission levels. The other important control parameter was shown to be the temperature. If the temperature in the cooling-coil section rises, then there is an appreciable reduction in absorption. Control of temperature is important in the upper sections of the column because it is here that the greatest effect on emission levels occurs. [Pg.178]

The principal concern when using tires for fuel is the effect on emissions. Pollutants of particular concern include criteria pollutants, particulates, metals, and unburned organics. [Pg.139]

Environmental demands and are as follows (a) improved fuel economy (reduced viscosities, reduced friction, special viscosity improvers), (b) reduced oil consumption (unconventional base oils, improved seal compatibility), (c) extended oil life (improved thermo-oxidative stability), (d) extended engine life (improved detergents and antiwear additives), (e) beneficial effects on emission/after treatment hardware (new additives), (f) technological and environmental sensitivity (no halogens, limited metal types/concentrations, new organic compounds), (g) recyclability (limitations the polycyclic aromatic hydrocarbons content and high chlorine levels (Havet et al., 2001 Waara et al., 2001). [Pg.269]

We now further examine the effects of coal type and pollution control device on plant emissions. Table III gives individual values from each of 18 studies for the important elements S, As, and Se. As expected from the results in Table II, coal type has some effect on emissions of these elements, but the presence of a scrubber vs. an electrostatic precipitator (ESP) has a far greater influence. Except for the anomalous Radian(2) plant, and despite some overlap between the two groups, scrubber-equipped plants generally emit far more As, Se and, especially, S than do plants with ESPs. The total particulate mass emitted by plants with scrubbers ( 25 mg/m3 sulfate 4 mg/m3) is comparable to that emitted by plants with ESPs ( 47 mg/m3 sulfate 0.5 mg/m3), so scrubber-equipped plants release much more primary sulfate than do plants with ESPs. Scrubbers are designed to remove gas-phase S02 They accomplish this partly by converting SO2 to sulfate droplets or particles, some of which escape from the plant. [Pg.308]

To provide an illustration of the type of ouputs provided by these models, Figure 1 presents results based on the examination of alternative coal plant lifetimes for facilities operated by the electric utility industry. Figure 1 shows a comparison of assuned 40 and 60 year utility plant lifetimes on emissions to 2030. As can be seen, these assumptions have no effect on emissions from non-utility sectors, but have a tremendous effect on both the pattern and the magnitude of total emissions. [Pg.369]

Because the physical description is correct and consistent, the method allows for arbitrary division of a system into different subsystems, which may be described either on the quantum-mechanical (QM) or the molecular mechanics (MM) level, without significant loss of accuracy. This allows for performing fully MM molecular simulations (Monte Carlo, molecular dynamics), which can subsequently be followed by performing QM/MM calculations on a selected number of representative snapshots from these simulations. These QM/MM calculations then give directly the solvent effects on emission or absorption spectra, molecular properties, organic reactions, etc... [Pg.39]

Structural and medium effects on emission spectra and lifetimes of [Re(L) (CO)3(N,N)]m complexes are extensively discussed in [1], Here, it was proposed to use energy-gap law maps, that is, dependences of the logarithms of excited-state lifetimes on the emission energy in series of structurally related complexes, to obtain information on the character of the emissive states. Quantitative analysis of the shapes of emission bands of [Rc(I.)(CO)3(N,N) affords information on structural differences between the ground- and emitting triplet states (Sect. 6) and can thus be used to further characterize the lowest excited states. Hereafter, we will... [Pg.85]

In addition to their effects on emission energy, the diimines and dithiolates also influence the emission lifetime and quantum yield of the Pt(diimine) (dithiolate) chromophore. The complexes display lifetimes ranging from 1 ns to > 1 ps and <3>eill ranging from < 10 5 up to 6.4 x 10-3, indicating such an influence on the kinetics of excited-state decay (see Table II). The tdt complexes have lifetimes that are significantly longer than those measured previously for... [Pg.343]

Emissions from gasoline and diesel engines are commonly classified into three categories volatile organic compounds, toxics and nitrogen oxides. The composition of exhaust gas from a vehicle is dependent on its fuel properties and the vehicle s emission control technology. Table 4.1 summarizes the primary fuel properties of interest and their qualitative effects on emissions. [Pg.75]

With respect to combustion, the research focus will be on improvement of the models regarding tars and their effect on emissions of CO. soot and unburned hydrocarbons (UHC). Part of that research will be the testing of a combustor integrated in an entire 500 kWth small scale gas turbine set-up. [Pg.486]


See other pages where Effect on Emission is mentioned: [Pg.84]    [Pg.383]    [Pg.373]    [Pg.271]    [Pg.95]    [Pg.175]    [Pg.26]    [Pg.50]    [Pg.245]    [Pg.342]    [Pg.76]    [Pg.130]    [Pg.135]    [Pg.8]    [Pg.81]    [Pg.545]    [Pg.2143]    [Pg.28]   


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Effects of intermolecular photophysical processes on fluorescence emission

Solvent effects on emission

Temperature effects on emission

The effect of temperature on emission processes

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