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Emissions from

Global emissions = emissions from on-site utilities... [Pg.291]

I- emissions from central power generation corresponding with the amount of electricity imported... [Pg.291]

There always is a relation between fuel composition and that of hydrocarbon emissions to the atmosphere, whether it concerns hydrocarbon emissions from evaporative losses from the fuel system, or from exhaust gases. This is the reason that environmental protection regulations include monitoring the composition of motor and heating fuels. We will describe here the regulations already in existence and the work currently underway in this area with its possible effects on refining. [Pg.258]

This rule is justified by the need to limit the benzene emissions from evaporation (Tims, 1983) Figure 5.25 shows that emissions increase linearly with the benzene content of the fuel. It is noteworthy that current legislation limits the measured evaporation to 2 g per test conducted in accordance with a standard procedure (Sealed Housing for Evaporative Determination, or SHED). Yet for a fuel containing 5% benzene, an evaporation of 0.7 g benzene /test is observed. [Pg.258]

Influence of the chemical composition of the fuel on pollutant emissions from vehicles in the US (auto/oil program). [Pg.260]

Me Arragher, J.S. and al. (1990), The effects of temperature and fuel volatility on evaporative emissions from european cars . /. Mech. Eng., No. 394/028, London. [Pg.458]

Tims, J.M. (1983), Benzene emissions from passenger cars . CONCAWE, report No. 12/83, La Haye. [Pg.460]

Signature Recognition of Acoustic Emission from FRP Structures. [Pg.37]

Photoexcited fluorescence from spread monolayers may be studied [158,159] if the substance has both a strong absorption band and a high emission yield as in the case for chlorophyll [159]. Gaines and co-workers [160] have reported on the emission from monolayers of Ru(bipyridine)3, one of the pyridine ligands having attached C g aliphatic chains. Ruorescence depolarization provides information about the restriction of rotational diffusion of molecules in a monolayer [161], Combining pressure-area... [Pg.127]

Fig. VIII 4. Field ion emission from clean tungsten. (From Ref. 64.)... Fig. VIII 4. Field ion emission from clean tungsten. (From Ref. 64.)...
IRE Infrared emission [110] Infrared emission from a metal surface is affected in angular distribution by adsorbed species Orientation of adsorbed molecules... [Pg.314]

Mobility of this second kind is illustrated in Fig. XVIII-14, which shows NO molecules diffusing around on terraces with intervals of being trapped at steps. Surface diffusion can be seen in field emission microscopy (FEM) and can be measured by observing the growth rate of patches or fluctuations in emission from a small area [136,138] (see Section V111-2C), field ion microscopy [138], Auger and work function measurements, and laser-induced desorption... [Pg.709]

The first mfonnation on the HE vibrational distribution was obtained in two landmark studies by Pimentel [39] and Polanyi [24] in 1969 both studies showed extensive vibrational excitation of the HE product. Pimental found that tire F + H2 reaction could pump an infrared chemical laser, i.e. the vibrational distribution was inverted, with the HF(u = 2) population higher than that for the HF(u = 1) level. A more complete picture was obtained by Polanyi by measuring and spectrally analysing tlie spontaneous emission from vibrationally excited HE produced by the reaction. This infrared chemiluminescence experiment yielded relative populations of 0.29, 1 and 0.47 for the HF(u =1,2 and 3)... [Pg.876]

Ultraviolet photoelectron spectroscopy (UPS) results have provided detailed infomiation about CO adsorption on many surfaces. Figure A3.10.24 shows UPS results for CO adsorption on Pd(l 10) [58] that are representative of molecular CO adsorption on platinum surfaces. The difference result in (c) between the clean surface and the CO-covered surface shows a strong negative feature just below the Femii level ( p), and two positive features at 8 and 11 eV below E. The negative feature is due to suppression of emission from the metal d states as a result of an anti-resonance phenomenon. The positive features can be attributed to the 4a molecular orbital of CO and the overlap of tire 5a and 1 k molecular orbitals. The observation of features due to CO molecular orbitals clearly indicates that CO molecularly adsorbs. The overlap of the 5a and 1 ti levels is caused by a stabilization of the 5 a molecular orbital as a consequence of fomiing the surface-CO chemisorption bond. [Pg.951]

While a laser beam can be used for traditional absorption spectroscopy by measuring / and 7q, the strength of laser spectroscopy lies in more specialized experiments which often do not lend themselves to such measurements. Other techniques are connnonly used to detect the absorption of light from the laser beam. A coimnon one is to observe fluorescence excited by the laser. The total fluorescence produced is nonnally proportional to the amount of light absorbed. It can be used as a measurement of concentration to detect species present in extremely small amounts. Or a measurement of the fluorescence intensity as the laser frequency is scaimed can give an absorption spectrum. This may allow much higher resolution than is easily obtained with a traditional absorption spectrometer. In other experiments the fluorescence may be dispersed and its spectrum detennined with a traditional spectrometer. In suitable cases this could be the emission from a single electronic-vibrational-rotational level of a molecule and the experimenter can study how the spectrum varies with level. [Pg.1123]

For molecules we can use Bom-Oppenlieimer wavefimctions and talk about emission from one vibronic level to another. Equation (B1.1.5T equation tb 1.1.6) and equation tb 1.1.7) can be used just as they were for absorption. If we have an emission from vibronic state iih to the lower state a, the rate constant for emission would be given by... [Pg.1131]

Typical singlet lifetimes are measured in nanoseconds while triplet lifetimes of organic molecules in rigid solutions are usually measured in milliseconds or even seconds. In liquid media where drfifiision is rapid the triplet states are usually quenched, often by tire nearly iibiqitoiis molecular oxygen. Because of that, phosphorescence is seldom observed in liquid solutions. In the spectroscopy of molecules the tenn fluorescence is now usually used to refer to emission from an excited singlet state and phosphorescence to emission from a triplet state, regardless of the actual lifetimes. [Pg.1143]

Rather different circumstances are encountered when considering THz remote sensing of extraterrestrial sources. The major source of THz opacity in the Earth s atmosphere is water vapour, and from either high, dry mountain sites or from space there are windows in which the background becomes very small. Incoherent instruments which detect the faint emission from astronomical sources can therefore be considerably more sensitive than their laboratory... [Pg.1235]

Maranowski K D, Gossard A C, Unterrainer K and Gornik E 1996 Far-infrared emission from parabolioally graded quantum wells Appl. Rhys. Lett. 69 3522-4... [Pg.1260]

Fessenden R W and Verma N C 1976 Time resolved electron spin resonance spectroscopy. III. Electron spin resonance emission from the hydrated electron. Possible evidence for reaction to the triplet state J. Am. Chem. Soc. 98 243-4... [Pg.1619]

Shelton FI 1957 Thermionic emission from a planar tantalum crystal Phys. Rev. 107 1553-7... [Pg.1898]

Micic O I ef a/1996 Highly efficient band-edge emission from InP quantum dots Appi. Phys. Lett. 68 3150... [Pg.2917]

The control of carbon dioxide emission from burning fossil fuels in power plants or other industries has been suggested as being possible with different methods, of which sequestration (i.e., collecting CO2 and injecting it to the depth of the seas) has been much talked about recently. Besides of the obvious cost and technical difficulties, this would only store, not dispose of, CO2 (although natural processes in the seas eventually can form carbonates, albeit only over very long periods of time). [Pg.217]

Typical examples of gaseous samples include automobile exhaust, emissions from industrial smokestacks, atmospheric gases, and compressed gases. Also included with gaseous samples are solid aerosol particulates. [Pg.195]

The focus of this section is the emission of ultraviolet and visible radiation following thermal or electrical excitation of atoms. Atomic emission spectroscopy has a long history. Qualitative applications based on the color of flames were used in the smelting of ores as early as 1550 and were more fully developed around 1830 with the observation of atomic spectra generated by flame emission and spark emission.Quantitative applications based on the atomic emission from electrical sparks were developed by Norman Lockyer (1836-1920) in the early 1870s, and quantitative applications based on flame emission were pioneered by IT. G. Lunde-gardh in 1930. Atomic emission based on emission from a plasma was introduced in 1964. [Pg.434]

Minimizing Spectral Interferences The most important spectral interference is a continuous source of background emission from the flame or plasma and emission bands from molecular species. This background emission is particularly severe for flames in which the temperature is insufficient to break down refractory compounds, such as oxides and hydroxides. Background corrections for flame emission are made by scanning over the emission line and drawing a baseline (Figure 10.51). Because the temperature of a plasma is... [Pg.437]

Other Detectors Two additional detectors are similar in design to a flame ionization detector. In the flame photometric detector optical emission from phosphorus and sulfur provides a detector selective for compounds containing these elements. The thermionic detector responds to compounds containing nitrogen or phosphorus. [Pg.570]

Short-lived gamma-ray Emission from impurities... [Pg.645]


See other pages where Emissions from is mentioned: [Pg.291]    [Pg.292]    [Pg.292]    [Pg.418]    [Pg.1103]    [Pg.1168]    [Pg.1235]    [Pg.1240]    [Pg.1312]    [Pg.1756]    [Pg.2060]    [Pg.2061]    [Pg.2073]    [Pg.2488]    [Pg.2489]    [Pg.2728]    [Pg.2973]    [Pg.426]    [Pg.433]    [Pg.438]    [Pg.645]    [Pg.33]    [Pg.33]   


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Abundance analysis from emission lines

Acetylene emission from vibrationally excited

Airborne lead arising from industrial emissions

Atmospheric Emissions from Plastics Industry

Auger electron-emission yields from

Automobile emissions ozone pollution from

Average dust emission from steel finishing

Barium isotopes, emissions from

Beta emission from carbon

Beta emission from lead

Beta emission from unstable isotopes

Biogenic sulfur emissions from ocean

Biomass burning emissions from

Blackbody emission from

Bromide emission from

Cadmium emissions from landfills

Caesium emission from

Calcium emission from

Calculation of absorptivities from emissivities

Carbon dioxide emission from car

Carbon emissions during hydrogen production from

Carbon monoxide from automotive emissions

Carbon vibrationally excited, emission from

Case study Reducing emissions to the air from a fertiliser plant

Catalytic Removal of NOX Species from Auto-exhaust and Power Plant Emissions

Challenges in Control of Emission from Automotive Exhaust

Chloride emission from

Cold emission of electrons from metals

Combustion plants, emissions from

Complexes emission spectra from transition

Control of lead emissions from motor vehicles

Copper emission from

Crystals laser emission from

Defect Emission from LPPPs

Defect Emission from PDAFs

Distributions emission from particles

Economic damage from pollutant emissions

Electric discharge emission from

Electron Emission from Quasimolecules

Electron emission current from metals

Electron emission from liquids

Electron emission from metals, photoinduced

Electron emission from nonpolar organic liquids

Emission and comsummption data from example plants

Emission and consumption data from ESBR plants (per tonne of product)

Emission and consumption data from the continuous PA6 production process

Emission and consumption data from the textile yam process

Emission and consumption data per tonne of product from EPS plants

Emission and consumption data per tonne of product from GPPS plants

Emission current from metals

Emission data for the exhaust gas from fettling, using various dedusting techniques

Emission data from EP-cleaned HPDC off-gas

Emission data from an example S-PVC plant

Emission from Charge Transfer States

Emission from Charge-Separated States

Emission from Combustion Products

Emission from Excited States

Emission from Gaseous Flames

Emission from Leaks

Emission from Polypeptides and Proteins

Emission from acetone

Emission from biacetyl

Emission from discharge

Emission from enclosed vapor degreasers

Emission from ocean

Emission from reactors

Emission from sinter plants

Emission from trapped carriers

Emission from volcanoes

Emission from “forbidden” transitions

Emission levels reported from 16 plants within the EU

Emission lines from nebulae

Emission of alkyl radicals from disordered selenium surface

Emission of heavy metals from coal-burning power plants

Emission resulting from excited

Emission resulting from excited states

Emission spectra from transition

Emission spectra from transition metal complexes

Emissions () of selected compounds from vegetable-based cold-box core systems

Emissions control from stationary

Emissions control from stationary sources

Emissions from China

Emissions from Ethane Cracking

Emissions from MSW

Emissions from Naphtha and LSWR Cracking

Emissions from Processing

Emissions from Propane Dehydrogenation

Emissions from Recycled Products

Emissions from Ricefields

Emissions from Russia

Emissions from United States

Emissions from chimney

Emissions from coastal salt marshes

Emissions from combustion sources

Emissions from diesel engine exhaust

Emissions from embedded sources

Emissions from environmental tobacco smoke

Emissions from finishing and product storage sections

Emissions from fossil fuel combustion

Emissions from fuel oil

Emissions from industrial chemical plants

Emissions from land

Emissions from lead paints

Emissions from municipal incinerators

Emissions from plane source

Emissions from point source

Emissions from power plants

Emissions from processes

Emissions from processes control

Emissions from processes control methods

Emissions from pulse combustor

Emissions from solvent spill

Emissions from storage tank

Emissions from vegetation

Emissions from wetlands

Emissions from wood smoke

Emissions of VOCs from varnishes and paints

Emissions to water from the S-PVC plant

Engines, gasoline powered emissions from

Estimating Emissions from Sources

Excimer emission from crystals

Exciton Emission from Alkali Halides

Field Emission from Carbon Nanotubes

Field Emission from Diamond Films

Field Emission from Different Si-Based Nanostructures

Flame soot emission from

Forest fires emissions from

Formaldehyde emission from building materials

Formaldehyde emission from particleboard

Fossil fuel emissions from

Fossil-fuels carbon emissions from

Fugitive emissions from

Gamma emission, from nucleus

Gaseous and Particulate Emissions from Forest Fires

Gaseous emissions, from pulse

Gasoline lead emissions from

Glycols emission from materials

Heat sources, emission from

Heavy metal emissions, from incineration

Hydrogen light emission from

Indium emission from

Infrared emission, from vibrationally excited

Infrared emission, from vibrationally excited species

Infrared emissions from dust disks

Intensity of emission from

Iodide emission from

Iodine isotopes emissions from

Ionization energies determination from emission

Lead-acid batteries emissions from

Lead-based paint emissions from

Light Emission from Flames

Light Emission from Mercury Gas Discharge

Light Emission from Nanostructures

Light emission from semiconducting

Light emission from semiconducting optical properties

Light emission from semiconducting polymers

Light emission, from chemically generated

Light emission, from chemically generated fluorescent molecule

Mercury emissions from coal-fired power plants

Metal emission spectra from transition

Metal oxides laser emission from

Metals, acoustic emission from

Methane emissions from different sources recalculated for carbon equivalent

Molecules emission from

N emissions from

Neptunium isotopes, emissions from

Neutral emission from

Neutral emission from fracture

New Opportunity for HC-SCR Technology to Control NOX Emission from Advanced Internal Combustion Engines

Nitrogen emissions from aircraft

Nitrogen recombination, emission from

Nitrous oxide emission from soils

Nitrous oxide emissions, from soil denitrification

Optical emission from plasma

Ozone emissions from printers

Ozone from auto emissions

Phenanthrene delayed emission from

Phosphorus emission from

Photo induced electron emission from metals

Photoelectron spectroscopy electron emission from core

Photoelectron spectroscopy electron emission from valence

Photon emission from solids

Polarised Light Emission from OLEDs

Pollution from automobile emission

Polonium alpha emission from

Potassium emission from

Power stations mercury emission from

Prevention of dust emissions from drying

Prevention of emissions from VCM unloading facilities

Processes Governing Ammonia Emissions from Rice

Processes Governing Methane Emissions from Rice

Production and Emissions from Natural Wetlands

Pulse typical emissions from

Radioisotopes radiation emission from

Radionuclides emissions from

Rate of emission from

Reduction of Infrared Emission from Combustion Products

Removal from emissions

Rubidium emission from

Semiconductor lasers emission from

Shock waves, emission from

Silver emission from

Sodium atom light emission from

Sodium emission from

Source from gaseous emissions

Spectra emission from multielement

Strontium isotopes, emissions from

Sulfur Recovery from Refinery Process Emissions

Sulfur emission from rain-forest trees

Sulphur molecule , emission from

Surface treatment emission from

Survey of air emissions from different ferrous foundry stages

Technology, nitrogen oxides emissions control from stationary sources

Temperature emission from wood

Thallium emission from

The Emission of Auger Electrons from Ionized Atoms

The Jahn-Teller Effect from Emission Spectra

Thermal Emission from Atmospheres and Surfaces

Thermal emission from electron bubbles

Total carbon emissions from various process steps, using aromatic- and vegetable-based solvents

Tryptophan Phosphorescence Emission from Proteins

Understanding Emissions from Indoor Sources

Upper atmosphere, emission from

Upper emission from

VCM emissions from German S-PVC reference plants

VOC emissions from emulsion paints

White Light Emission from Organic LEDs

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