PATENTSCOPE sera indisponible quelques heures pour des raisons de maintenance le mardi 19.11.2019 à 16:00 CET
Recherche dans les collections de brevets nationales et internationales
Certains contenus de cette application ne sont pas disponibles pour le moment.
Si cette situation persiste, veuillez nous contacter àObservations et contact
1. (WO1986004140) PROCEDE ET APPAREIL POUR ANALYSER DES SUSPENSIONS GAZEUSES CONTENANT DES PARTICULES
Note: Texte fondé sur des processus automatiques de reconnaissance optique de caractères. Seule la version PDF a une valeur juridique

METHOD AND APPARATUS FOR ANALYZING
PARTICLE-CONTAINING GASEOUS SUSPENSIONS

BACKGROUND OF THE INVENTION
Many processes require, or would at least benefit from, on-line monitoring of the chemical composition and/or other parameters of gaseous suspensions involved. Such in-situ analysis entails a number of significant advantages over other techniques (e.g., the analysis of conversion products) , particularly in that all of the problems associated with sampling and sample handling are inherently eliminated; it also permits dynamic monitoring of chemical and/or physical changes that occur during the course of combustion, pyrolysis, and other types of reactions.
As far as is known, very few (if any) of the forms of instrumentation heretofore available are useful or satisfactory for the on-line analysis of particle streams (as used herein, reference to "particles" is to be understood to include liquids and solids, as well as mixed phases) . In particular, it is not believed that any such instrumentation is capable of resolving size, temperature, number density and/or quantitative chemical composition for particle-containing gaseous streams, especially in a reactive environment.
It is of course well known to utilize electromagnetic radiation for a variety of analytical purposes, as evidenced by the body of prior art patents issued in the United States. For example, in Bertrand Patent No. 2,333,762 an analytical technique is disclosed in which the intensity of radiation is used to determine the solid content of a gaseous medium. A temperature measurement system, operating upon absorbed and emitted radiation, is described in Tandler et al No. 2,844,032, and in Patent No. 2,878,388 Bergson discloses a system for analyzing gases by measuring the absorption of radiant energy.
Seelbinder No. 3,724,951 and Riggs No. 3,743,430 both involve techniques for making aerosol opacity determinations, based upon transmitted radiation, and Snowman No. 3,588,496 teaches radiation absorption analysis apparatus for identifying samples of gases, aerosols and liquids. Each of the following patents uses irradiation scattering as a basis for detecting and/or analyzing aerosols or smokes: Hilsum No.
3,317,730, Charlson et al No. 3,700,333, Lepper, Jr. No. 3,787,122, and Mueller No. 3,882,477. In Patent No. 4,017,193, Loiterman describes apparatus for measuring the transmittance of a gaseous medium carrying particulate matter through a conduit, and Suga No. 4,021,713 discloses apparatus for the sequential measurement of radiation transmitted through smoke.
Neugroschel No. 3,703,337 discloses an analytical processor capable of handling at least two characteristics of the specimen, simultaneously measuring and converting them for digital print out. Vanesse No. 4,095,899 concerns a technique for performing Fourier spectroscopy. In Cashdollar et al No. 4,142,417, an infrared pyrometer is used to determine radiation emitted from a gas and/or particle, with tempertures being determined by correlation of the radiation data to black-body radiation curves.
Kraushaar et al No. 4,304,491 discloses the use of a spectrometer to detect both dispersed and undispersed . irradiation for IR imaging.
Cells and associated devices, used for spectroscopic analysis of samples, are described in Gaglione No. 3,478,206, Sole et al No. 3,631,237 and itte No. 3,730,630. Surface temperature measuring apparatus is taught by Brandli et al in No. 3,924,469, and a photometer/detector/amplifier arrangement, for use in automatic analysis apparatus, is shown in Atwood et al No. 4,014,612.
In Stein No. 4,440,510, a system is disclosed for pyrometric gas temperature measurement, carried out by adjusting and comparing the physical temperature of a black-body with the radiation temperature thereof measured through the gas. A spectrometric method for determining the size of metal particles in oils is taught in Kauffman et al No. 4,448,887, and a method and apparatus for determining size distribution of particles, by fitting a selected parameter distribution function to sealer representations of data obtained, is disclosed in Hobbs et al No. 4,453,226.

Finally, in an article entitled "Fire Flame Radiation" (Combustion and Flame 52: 127-135, 1983) , Vervisch and Coppalle discuss the use of normalized emission measurements for determining the temperature of flames containing soot.
Despite the foregoing, a need remains for means by which analyses of the sort described above can be carried out conveniently and effectively.
Accordingly, it is a primary object of the present invention to provide a novel method and apparatus by which gaseous suspensions of liquid and/or solid particles can readily be analyzed for any of a variety of physical and chemical properties.
More specific objects are to provide such a method and apparatus by which such a suspension can be analyzed either in-situ, in a reactive environment, or as a supplied sample, for determinations of particle size, temperature, number density, spectral emittance, and/or composition, in a manner that is very fast, convenient, and effective.
SUMMARY OF THE INVENTION
It has now been found that certain of the foregoing and related objects of the invention are readily attained by the provision of apparatus comprising, in combination, interferometer means, radiation collecting means, radiation source means, and electronic data processing means for analyzing collected radiation. The interferometer means is operatively positionable, with respect to the suspension to be analyzed, for encoding radiation projected thereinto and emanating therefrom, and the collecting means is similarly positionable, with respect to the suspension and the interferometer means, for collecting coded radiation from the suspension; the collecting means is also adapted to discriminate, in cooperation with the data processing means, radiation transmitted through the suspension from radiation emanating therefrom. An electromagnetic radiation beam is provided by the source means, so as to be projected through the interferometer means for coding and thereafter for transmission through the suspension.
It should be noted that, as used herein, reference to radiation "emanating" from the suspension or containment means is intended to be exclusive of radiation which is transmitted by or through the suspension or the particles thereof, but inclusive of any radiation that is emitted by the particle and/or scattered by interaction therewith. Also, "transmitted" radiation is that which passes directly through the substance, without being diverted (such as by refraction, diffraction or scattering by another mechanism) from its original rectilinear path.
In preferred embodiments of the apparatus, the collecting means will comprise a first collector operatively positionable for collecting radiation transmitted through the suspension, and a second collector separate from the first, operatively positionable for collecting the radiation emanating from the suspension. Generally, the apparatus will be adapted for use with containment means having a sidewall defining a chamber for the gaseous suspension. The sidewall of the containment means will in turn have at least one port providing optical access into the chamber, with the "second" collector, and the source means and/or the "first" collector, being disposed on the apparatus for positioning so as to function through the port.
In most instances, however, the apparatus will be adapted for use with containment means having a pair of optical access ports aligned transversely on opposite sides of its sidewall. The source means and "first" collector of such apparatus will be in effective optical alignment, and spaced from one another to accommodate the containment means therebetween, thereby permitting projection of the beam from the source means through the aligned access ports to the "first" collector. The apparatus will desirably include means defining an aperture of variable size, from which passes the transmitted radiation for collection by the "first" collector; this will enhance the usefulness of the apparatus for making particle size determinations.
For some applications, the apparatus will additionally include a cell, cooperatively providing the above-described containment means as an integral component of the apparatus, together with associated eans for injection of the gaseous suspension. In a specific embodiment, the cell has a generally cylindrical sidewall and end walls cooperatively defining the chamber thereof. The sidewall has a pair of optical access ports positioned diametrically thereon, and the end walls have means defining inlet and outlet channels therethrough, which channels are aligned substantially on the longitudinal axis of the cell for the injection and removal of particles, respectively. Such a cell will also have means by which the temperature of the inside surface of the sidewall, and the temperature of the inlet and outlet channel-defining means, can be independently controlled.
In other preferred embodiments of the apparatus, the "second" collector will be effectively disposed along the path of radiation between the source means and the interfermometer , and the apparatus will additionally include diverter means for establishing a radiation path between the gaseous suspension and either the source means, the "second" collector, or both. The diverter means may be operative to either permit passage of radiation from the source means to the suspension, or to block such passage of radiation while simultaneously directing radiation from the suspension to the "second" collecting means. As a result, measurements of radiation transmitted through and emanating from the suspension, respectively, can be selectively made.

Most desirably, the diverter means will be adapted to simultaneously permit passage of radiation from the source means to the suspension while also directing radiation therefrom to the "second" collecting means. To do so, the diverter means may have a first portion which is transparent to the radiation from the source means, and a second portion which is opaque thereto and is reflective of radiation emanating from the suspension, and is directed theretoward. Thus-, the diverter means will permit the transmitted and emanating radiation to be simultaneously measured, using the "first" and "second" collecting means, respectively.
In the particularly preferred embodiments, the apparatus will comprise a Fourier-transform spectrometer, adapted to develop a spectrum **-representative of the intensity of the collected radiation as a function of wavenumber. For that purpose, the data processing means of the spectrometer will be programmed to compare the representative spectrum to preestablished spectra indicative of a parameter for which the gaseous suspension is being analyzed, so as to fit the representative spectrum thereto and thereby determine the parameter. More specifically, the spectrometer will employ radiation source means operating in the infrared wavelengths regions, and the data processing means will beneficially be programmed to effect the comparisons involved by application of at least one of the following generalized formulas:

E *=
[ksBB(Tg) +k BB(T ) +NA*BB(T ) +N QsBB(Tw) ]*
[l-exp(-(ks+kg+NAQeχt)L) ]
+ + NAQ
s g ext
and
(1-/) = l-exp[-(kg + kg + NAQeχt)L].

As used therein (and in other expressions throughout this specification) , "E" represents any collected radiation emanating from the gaseous suspension and not transmitted therethrough; "• " represents the ratio of any collected radiation that is transmitted through the suspension, divided by radiation that would be transmitted -in the absence thereof (i.e., transmittance) ; "kw" and "k*y " are the extinction coefficients for any soot present and the gas phases, respectively, of the suspension; "BB(Ts) " , "BB(Tg) ",

"BB( p)", and "BB(Tw)" are the black-body spectra appropriate to the temperature of any soot present, the gas, the particles, and the medium surrounding the suspension, respectively; "N" is the number density of the particles in the suspension; "A" is the geometric cross-sectional area of the particles; "L" is the effective path length through the gaseous suspension; ny is the spectral emmittance of the particles; "Q " is the ratio of the radiation scattering cross section to -10-the geometric cross section of the particles; and "Q ext is the ratio of the extinction cross section to the geometric cross section of the particles, and is equal to Q + Qahs* τtle term πQa s" i-s us&d to represent the ratio of the absorption cross section to the geometric cross section of the particles, and it should be appreciated that each of the foregoing quantities, other than N, A and L, is wavenumber dependent.
The foregoing generalized formula for "E" is a special case of a more basic equation, in which special case the sample is homogeneous and all quantities are therefore independent of position through the sample volume. The data processing means of the apparatus may, however, be programmed to effect comparison of the representative spectrum using the following basic equation, by which contributions from theoretical slices of width "dl", at positions "1" through the suspension, are integrated for values of "1" from zero to "L" to determine the radiation emanating from a non-homogeneous sample:

E = J [{kgBB(Ts) + kgBB(Tg) + NA$BB(Tp) +

NAQSBB(TW)} exp(-y)]dl,

wherein "y" is the integral: 1 (k + k + NAQ . )dl
o

It will be appreciated that equations other than the foregoing generalized formula for E may also be derived from the basic equation, and used in the apparatus and method of the invention, for other special cases in which particular conditions may exist or be assumed to exist as a practical matter, as will be discussed more fully hereinbelow.
Other objects of the invention are attained by the provision of apparatus particularly adapted for the analysis of a gaseous suspension to determine compositional parameters of the particles contained therein, utilizing refracted components of radiation. Such apparatus will comprise containment means having a sidewall defining a chamber for the flow of a gaseous suspension of particles along a path therethrough, with at least one port being provided in the sidewall to afford optical access to the path. Source means used for providing electromagnetic radiation in the apparatus will be adapted to direct the radiation inwardly from substantially all peripheral points about the path, and the apparatus will have means for collecting radiation emanating from the containment means. To enable the compositional analysis to be made, the containment means, the source means, and the collecting means will be so adapted that components of radiation from the source means that have been refracted or otherwise diverted from their original paths, due to interaction with the particles of the suspension, can be substantially discriminated from radiation that has not been so diverted. Preferably, such apparatus will additionally include second source means, for providing an electromagnetic radiation beam, and second radiation collecting means, the second source means and second collecting means being disposed in effective optical alignment with one another, and being adapted to measure radiation transmitted by the particles of the suspension during passage through the containment means.
Generally, the apparatus will also include electronic data processing means for analyzing the radiation collected by the "first" and "second1- collect-ing means, and for also controlling operation of the "second" source means.
In particularly preferred embodiments of the apparatus, the sidewall of the containment means will substantially surround the flow path, and will have an energy radiating surface thereon to provide the first-mentioned source means, which surface will usually be heated for that purpose. The configuration of the wall surface, and the positions thereof and of the collecting means with respect to the access port(s), will substantially limit the radiation from the radiating surface impinging upon the collecting means to that which has been so diverted, thereby effectively providing the radiation discrimination capability of the apparatus. Most desirably, the radiating surface will be of generally circular cross-sectional configuration in planes transverse to the flow path axis, and the sidewall defining it will have a second optical access port therein aligned transversely with the "one" port on the opposite side of the flow path. The "second" port will provide a non-radiating area on the surface, and thereby cooperate to provide the discrimination capability of the apparatus. An interferometer or other coding means, radiation diverter means, and other specific features described above may also be incorporated into the apparatus of this embodiment.
Additional objects of the invention are attained by the provisions of analytical methods, broadly defined to comprise the steps of: a. causing electromagnetic radiation from at least one source to impinge upon a gaseous suspension of liquid and/or solid particles to be analyzed; b. collecting spectral radiation from the so-irradiated suspension; c. developing a spectrum representative of the intensity of the collected radiation as a function of wavenumber; and d. comparing the representative spectrum to preestablished spectra indicative of the parameter for which the suspension is being analyzed, and fitting the representative spectrum thereto to determine the parameter, the comparison being made by application of the equations and formulas set forth and defined herein.
In some cases, the method will include the step of passing the gaseous suspension through a chamber at a flow rate of about 1 to 100 meters per second, with the suspension being irradiated during such passage, and a stream of gas may be passed into the chamber simultaneously with, and as a sheath about, the particle suspension. Normally, the irradiation used will be a beam of infrared wavelengths, preferably brought to a focal volume or zone within the chamber with the gaseous suspension being passed substantially therethrough the focal volume. For certain purposes, it will be advantageous for the particles of the suspension to be in the form of a monodispersed stream, and in the most preferred embodiments of the method the step of analyzing the radiation will comprise Fourier-transform spectroscopic measurement thereof.
In more specific aspects of the method, radiation transmitted through the irradiated suspension, as measured by transmittance / , is discriminated from radiation "E" emanating therefrom, with spectra representative of the intensity of the radiation / and E so collected and discriminated being developed as functions of wavenumber. Preferably, the comparison of the representative and preestablished spectra, for determining the desired parameter, will be made by application of the generalized formulas given above, or by application of the basic equation referred to, or other equations derived therefrom, depending upon the nature of the sample.
In the method, the particles of the suspension may be at a temperature "TD" which is to be determined, the representative spectrum used for comparison being that of normalized emission "En", wherein En„ = B/ {1-Ϋ) . When irradiation is carried out with the gaseous suspension contained in a chamber, the surrounding medium will be the wall surface defining the chamber, and the comparison of spectra will be made based upon the following equation, derived on the basis that Qext equals 1, and k and k both equal zero:
En = £BB(Tp) + (l-£) BB(TW).
In other instances, the temperature of the particles and the temperature of the medium surrounding the suspension will be known, and ' the parameter for analysis will be emittance " " , the representative spectrum used again being normalized emission. If particle temperature "T " is substantially higher than the surrounding medium temperature "T " , the comparison will be made based upon the equation: £ = E /BB(T ) . If, on the other hand, the surrounding medium comprises the surface of a wall, the temperature of which is substantially higher than that of the particle, the comparison will be made based upon the equation:
= 1 - [E 11 /BB(TW)]. In the latter instance, the method may include the further step of estimating the wavenumber-dependent linear absorbtion coefficient characteristic " ^" of the composition. This may be done by measuring the value of E , determining a value for the average transmission "T-*" for the inside of the particles of the suspension by application of the equation: Υ" - En • c -,ha-,r-.a _c-,*t._er-. ii „zi-n „g-, t.h«e g -,r-.o-.s-.s-,

geometry of the particles of the suspension, in terms of a characterizing dimension "D", selecting a suitable preestablished curve expressing (-In T") as a function of k^D, based upon that characterization, and estimating the value of ^ from the selected curve.
In an embodiment of the method that is specifically adapted for quantitative compositional analysis, electromagnetic radiation will be caused to impinge at off-axis angles upon the particles of the suspension during passage through a chamber, such angles consisting essentially of angles that are oblique to the optical access port thereof. The collected radiation is substantially limited, by virtue of the off-axis impingement, to rays coming from the source that are refracted or otherwise diverted by the particles. A spectrum representative of the path and amplitude of the collected radiation is developed, as a function of wavenumber, and is compared and fitted to preestablished spectra indicative of the compositional parameter for which the suspension is being analyzed, to determine the same.
Generally, the cavity used in performing such a method will be defined by a wall substantially surrounding the gaseous suspension, the surface of which will be maintained at a temperature substantially higher than the temperature of the particles, thereby providing an off-axis, infrared radiation source. Typically, the wall surface will be at a temperature that is about 500 Centigrade degrees or more above that of the particles, and the suspension will desirably be maintained, prior to entry into the cavity, at a temperature suitable to ensure that they will be substantially at room temperature therewithin; the flow rate of the suspension through the chamber should be sufficiently high to avoid substantial heating of the particles by the radiant energy. As an alternative to using a hot surrounding wall surface, a high intensity radiation source (such as laser beam optics) may be moved to incrementally displaced circumferential positions about the path of the suspension, to provide an off-axis beam at a multiplicity of angular relationships.
In especially preferred embodiments of the method for compositional analysis, a beam of electromagnetic radiation from a second source will also be caused to impinge upon the particles, with the collecting step being carried out by collecting and discriminating the diverted rays from the components of the second-source beam that are transmitted through the particles. The representative spectrum used for comparison will again be that of normalized emission, with the comparison being made by application of the designated formulae or equations. In such a case, the transmitted radiation components and the diverted rays may be collected sequentially, under conditions of constant particle flow rate and density, or they may preferably be collected simultaneously. This embodiment of the method may also include the further step of estimating the wavenumber-dependent linear absorbtion coefficient characteristic "k^" of the composition, in the manner described above.
Finally, the method may be employed for the analysis of the size of particles in a gaseous suspension, by causing a beam of electromagnetic radiation to impinge upon the suspension, and selectively collecting radiation transmitted therethrough. A spectrum representative of the intensity of the collected radiation, as a function of wavenumber, is developed, and is compared and fitted to preestablished spectra indicative of particle size. The representative spectrum is that of (1-7') , and the comparison is made based upon the formula:
(1-f) = l-exp[-(ks + kg + NAQeχt)L],
wherein f is the transmittance or fraction of radiation transmitted, and is equal to the (wavenumber-dependent) ratio of measured intensities, with and without particles in the impinging beam (i.e., I/I ) .
Preferably, the gaseous suspension will be contained in a chamber, and the aperture size of the optical access port, beyond the zone of impingement of the beam upon the particles, will be varied to maximize the dependency of the intensity of collected radiation upon the wavenu bers of the radiation of the impinging beam. In this manner, the curve of the representative spectrum will be optimized for fitting to the curves of preestablished spectra.
BRIEF DESCRIPTION OF THE DRAWINGS
Figure 1 is a schematic representation of a spectrometriσ system embodying the present invention;
Figure 2 is a schematic representation of a sampling cell appropriate for use in the system of Figure 1;
Figure 3 is a schematic representation showing the geometry of emission and transmission measurements, taken along the axis -of the cell; and
Figures 4-20 are curves of data representative of various relationships significant to the invention.
DETAILED DESCRIPTION OF THE ILLUSTRATED AND PREFERRED EMBODIMENTS
Turning now in detail to Figure 1 of the appended drawings, as indicated above the measurement of particle properties is preferably performed, using
Fourier-transform infrared spectrometer (FT-IR) apparatus, generally designated by the numeral 10 therein, fitted with special optics and programmed to carry out the unique analysis methodology of the invention. More specifically, the FT-IR apparatus shown schematically in Figure 1 can be any of several commercially available instruments (e.g., the NICOLET

7199 system) , and will include an infrared source 12

(e.g., a globar) , a Michelson interferometer, generally designated by the numeral 14, a sample compartment 16, a radiation collector or detector 18, and a computer 20, suitably interconnected (by means not shown) for instrument control and data processing and analysis; it will normally also incorporate a laser beam source 22 and detector 23, for timing purposes. Generally, the spectrometer will be capable of spectral resolution between 0.5 to 8 wavenumbers and of operating at any appropriate scan frequency and any frequency range, although 400-10,000 wavenumbers is preferred. In addition to providing suitable mirrors 24, 26, 28, 30, 32 and 34 at appropriate locations within the system, a second detector 36, a reflective diverter 38, and a sample cell, generally designated by the numeral 40, are incorporated in the illustrated embodiment.
By way of broad description, assuming a measurement of transmitted radiation is to be made for a gaseous suspension passing through the chamber 42 of the cell 40, the IR beam from source 12 is reflected by mirror 26 into the interferometer 14 for encoding. From the interferometer, it is reflected by focusing mirror 28 through port 44 in one side of the cell wall 46, and is brought to a focal volume "f" therewithin. Those components of the beam that are transmitted by the suspension pass through the second port 48 (laterally aligned with the first) in the wall 46, and are reflected by mirrors 32, 34 into the detector 18, which will be selectively adapted to collect the encoded radiation. Although not illustrated, it should be pointed out that the port 48, which lies beyond the focal zone f (or the zone of particle/beam interaction, if an unfocused beam is employed) with respect to the source 12, may have associated means for varying the size of its aperture, so as to permit adjustments to be made to achieve optimal sensitivity for particle size measurement.
Radiation emanating from the cell 40 can be collected by the detector 36, being reflected by mirror 28 through the interferometer 14 and encoded for that purpose. To do so, the diverter 38 is positioned (as shown) in the path of the beam reflected from the mirror 26, and will serve to reflect it to the mirror 24 and to the detector 36 therefrom; as will be appreciated, in the embodiment shown the diverter 38 will be displaced (such as by pivoting) from the path of the beam generated by source 12, to permit the above-described transmission measurement to be made.
The two measurements (i.e., of transmitted and emanating radiation) can be made sequentially with the arrangement illustrated by rapidly shifting the position of the diverter 38, as indicated. Alternatively, the measurements can be effected simultaneously, and this will normally be the preferred mode of operation. Simultaneous measurements can be made by use of a diverter having two zones of different optical properties disposed in the radiation path, one zone being constructed to pass the beam from the source 12, and the other being made to reflect radiation emanating from the cell 40, which is directed thereto by the mirrors 28 and 26.
Other arrangements and apparatus features can of course also be employed. For example, since it is desirable in most instances to utilize suspensions in which the particles are homogeneously dispersed, suitable means for providing such suspensions doing so may be included. The apparatus may employ a system of flipping mirrors for projecting the radiation to a common detector location (which may itself comprise a single collector, if appropriately constructed and coupled with suitable analytical data processing logic to perform the desired functions) . It is also possible to use only a single optical access port with an aligned reflector, in which case the beam will enter and exit from the same aperture and provide a double-length transmittance measurement through the sample. Moreover, although infrared spectrometry is described and is preferred, other radiation frequencies may be substituted.
It should be appreciated that apparatus such as that of Figure 1 can be employed, as well, to analyze gaseous suspensions at locations external to the system; e.g., for the in-situ monitoring of a chemical reaction in progress. In those instances the cell 40 would not be used, its functions instead being performed by the on-site containment means (e.g., the reaction vessel), which would of course have suitable ports for optical access, and the mirrors 28, 32 would be positioned (as necessary) to accommodate the reaction vessel therebetween. It is also possible to employ the apparatus for analysis of unconfined volumes (e.g., of a gaseous combustion mixture flowing from a smokestack or over a container) , in which case the medium surrounding the suspension would be the ambient, 'rather than a cell or reactor wall.
Generally, the function of the sampling cell 40 will be to either conduct gas suspended particles through the beam from the source 12, or to provide a second source of radiation emanating from locations about the gaseous stream (e.g., the wall surface 42); as is evidenced by Figure 1, moreover, the cell may serve both functions. Because the port 48, which is aligned with port 44 on the optical path, provides an unheated area on the surface 42, it will effectively represent a gap in the radiation source surrounding the particle flow path, and will thereby limit the components collected from that source to those which are refracted or otherwise scattered by the particles into the optics of detector 36. Obviously, the same effect could be achieved by other means in the absence of a port, such as by cooling the corresponding, on-axis area of the wall. If a transmission beam were projected through port 48 toward port 44, that fraction of its rays which was not scattered out of the optical path would of course be directed toward the same detector; however, the coding effects provided by the apparatus permit them to be discriminated, so as to not contribute to the refracted radiation measurement. In the particular arrangement of Figure 1, such coding permits the detector 18 to discriminate and collect the rays from the source 12 which are transmitted through the particles, and permits the detector 36 to do the same with regard to the radiation emanating from the cell 40.

In any event, the geometry of the cell should be such that no appreciable attentuation of the IR beam occurs in traversing it from port 44 to port 48 unless particles are present, generally within a volume of focus thereof. Similarly, it should be so designed that no appreciable radiation from the second radiation source (e.g., surface 42) reaches detector 36 in the absence of particles in such a zone of the optical path.

A preferred embodiment of the sampling cell 40 is schematically illustrated in Figure 2. It consists of a body 48 having an internal cavity 42 of circular cross section, defined by the inside surface of wall 46. Means (not shown) is provided for controlling the temperature of the wall surface (normally, the heated section will be separate from the remainder of the wall 46, to minimize heat loss and energy requirements) , and ports 44, 48 are aligned diametrically on the opposite sides of the wall 46 and provide optical access to the cavity 42; the ports are closed by transparent windows 50. Passages in the top and bottom walls 52, 54, respectively, of the body 48 are aligned on the longitudinal axis of the wall 46, and are constructed to provide particle injection and collection features for the cell.
More specifically, the injection feature is provided by two coaxial tubular conduits, the inner conduit being temperature controlled (by means not shown) and providing a channel 56 for the gaseous suspension of particles to be injected into the cell, and the outer conduit providing a channel 58, of annular cross section, for delivery of a gas which is to form a sheath about the suspension. The collection feature is provided by an insert 60 (which is also temperature controlled by means not shown) having a funnel-like conduit 62 formed therethrough.
As can be seen, the optical path of the spectrometer beam traverses the ports 44, 48, and is brought to a focal zone at "f", within the cavity 42. The particles 64 are injected through the conduit 56 (in monodispersed form, in the illustrated embodiment) , into the focal volume of the beam for interaction therewith.

and are thereafter removed from the cell through the conduit 62.
The design of the illustrated cell serves to minimize any path for radiation to enter the emission detector 36 in the absence of a sample stream. It wi.ll be appreciated that the fluid mechanics will be so designed so that the sample stream will pass through the cavity virtually without loss and without appreciable alteration of its temperature, by internal cavity radiation, when the temperature controlled walls are hot (relative, to the particles). Moreover, under those conditions the gas velocity must be sufficiently high to avoid particle heating; flow velocities of 1 - 100 meters/second will generally be employed, and residence times will typically range from fractions of a millisecond to about one-tenth second.
The carrier gas used can be of any desired composition; nitrogen and argon will be beneficial in providing a non-reactive environment which will not interfere in the IR spectra. On the other hand, the use of "tracer" gases which exhibit IR absorption, such as carbon monoxide, will allow for gas temperature diagnostics. The sheath gas can be nitrogen, argon, or other non-absorbing gas. The suspended particles can, as explained above, be solids, including very finely divided substances such as soot, or liquid droplets; optimally, the particles will be less than 300 micrometers in diameter, and they can be either monodispersed or polydispersed in the gas phase.
The Measurements
Generally, the analysis methodology will consist of obtaining transmittance spectra, emission spectra, or both, which preferably (particularly for the sake of speed and accuracy) will be taken simultaneously, and under conditions ensuring homogeneity of the particle concentration in the gas phase. These spectra are obtained and analyzed with an FT-IR spectrometer under computer control, using special computer software functionally described herein to determine desired parameters and properties of the particles.
For purposes of calibration, spectra are obtained in the absence of a sample stream. Normally, calibration will be , required only at infrequent intervals, depending of course upon the stability of the optical system and detectors.
Emission Measurements
The emission measurements require that a wavenumber dependent instrument response function, F^ , be determined for each resolution used. This is done by obtaining a spectrum "R " (using a detector such as 36 in Figure 1) , from a reference black-body placed at the focal point "f". R^ is corrected by subtracting the background with no source present, and is divided by the black-body curve "BBfTβ)" appropriate to the temperature -28-of the reference; thus, the response function is determined in accordance with the formula:
F = ^ /BB(TR)
It should be appreciated that all of the above quantities are wavenumber dependent, and that the measured spectral response curve will be obtained with a collector such as the so-called "MCT", "InSb" or "TGS" detectors. Instrument response functions and background spectra were observed to be stable over several weeks, provided that cell conditions remained constant.
A sample emission spectrum "E" is then obtained by dividing (using the computer associated with the spectrometer) the observed spectrum "0" at the detector, with particles present in the focus "f" and corrected for background, by the instrument response function F (the subscript π,1* is omitted for convenience) . It has been found that emission measurements, with appropriate background and instrument response corrections, were made with good signal-to-noise ratios, in as little as 200 milliseconds. Examples of such data are shown in Figures 5-8 (in which radiance is plotted against wavenumber) for a number of cases where the particles are of different composition and at different temperatures with respect to the wall.
Absorption Measurements
Measurements of absorption, or transmittance, are made in the normal way. The spectrum from a globar source [see Bohren, C. F. and Huffman, D. R. , "Absorption and Scattering of Light by Small Particles", John Wiley and Sons, New York, NY (1983)] passing through the empty cell is measured to determine intensity "I " at each wavenumber, and the same measurement is made with the particles in the cell to give the intensity "I". As indicated above, the transmittance n*f " is defined as the fraction of the radiation transmitted ( Υ - I/I ) , which term is also used herein to refer to the transmitted percentage. The absorbance "A" is given by A = -log-. Q 7" - and the fraction percentage of radiation absorbed and scattered is given by (1-f) .
Examples of the transmission, plotted as {1-7) as a function of wavenumber, are presented in Figs. 9 and 10. Figures 9a and 9b are for carbon and copper particles. Particles can of course block radiation by absorption and by scattering (i.e., reflection, refraction and diffraction) . For particles of diameter greater than several micrometers, and for wavelengths of present interest (e. g., 1.6 to 25 micrometers), it has been predicted and observed, in accordance herewith, that almost none of the incident radiation is transmitted directly through the particle along its original rectilinear path. This is true even for particles that are completely or partially transparent in the infrared range, such as potassium chloride (Figure 10a) and fuel oil (lOd) , as long as the refractive index of the substance differs from unity. In addition, diffraction and interference can produce a wavelength-dependent reduction of the transmitted intensity by a factor that is as much as twice the projected area of the particle (see Hottel, H. C. and A. F. , "Radiative Transfer", McGraw-Hill Company, New York, (1976) and van de Hulst, H. C, "Light Scattering by Small Particles":, Dover Publications, NY, (1981).] in addition to the Bohren and Huffman reference noted above) .
With regard to Figures 9a and 9b, it is expected that particles such as carbon and copper block radiation over their projected surface area at relatively short wavelengths (large wavenumbers) , with diffraction effects decreasing the transmission at longer wavelength values. For large particles, therefore, (1-71 at short wavelengths is taken as a measure of the fraction of the viewing area which is blocked by the projected area thereof. For soot particles, of diameter 0.1 micrometer (Figure 9c) , the level of absorption is highly dependent upon wavelength, decreasing at longer values.
An FT-IR spectrometer is ideally suited for making transmission measurements in a hot cell, since the detector will only record radiation which has been modulated b the Michelson interferometer and will therefore reject radiation originating at the hot cell walls. Of course, such a spectrometer also offers the advantages of high sensitivity, high resolution, and rapid scan in all applications, and is therefore the preferred apparatus herein, and the apparatus of first choice in the practice of the instant method.
Normalized Emission
In analyzing the data from the measurements made, the determination of radiation extinction by the particles, relative to their blocking area, is of primary interest. This is done by use of "normalized" emission "En", equal to H/ {1-p . Examples of normalized emission for several cases of interest are presented in Figures 11 to 14 (plots of radiance versus wavenumber) . As can be seen, the spectra vary substantially with the composition of the particles and their temperature relative to the cell wall.
The Analyses*
Analysis of Size and Density
To determine the size and concentration (number density) of the particles in the suspension analyzed, transmittance spectra are employed, examples of which, plotted as (1-/), are presented in Figures 9 and 10. In the case of particles which block less than 20 percent of the transmitted light, the quantity (1-Ϋ) is approximately equal to the quantity Qext NAL, and can readily be evaluated in accordance herewith; when blockage is greater than 20 percent, valuable information can still be obtained, but the analysis is -32-considerably more complex. For a spectrometer acceptance angle of θ , and particles with perimeter "P" such that (P/> (sinø) is equal to or less than 3, diffraction and interference can produce a wavelength-dependent reduction of the transmitted intensity which is as much as twice the fractional projected area. An example of this phenomenon, which is well understood, is illustrated in Figure 9b, which shows enhanced scattering at long wavelengths. For purposes of the present analysis, the FT-IR spectrometer used had an acceptance angle of 0.25 radian.
While the full Mie scattering theory is available to treat the effect of diffraction, the simpler Rayleigh expression has been employed herein, which has been shown to be accurate for the larger P/ ratios (see Gumbrecht, R. O. and Sliepceviσh, C. N. , J. Phys. Chem. 57, 90 (1953) .] For Figures 9a and 9b, it is expected that the particles block radiation over their projected surface area at relatively short wavelengths (large wavenumbers) with diffraction effects decreasing the transmittance further at longer wavelengths. Therefore, for large particles the expression "(1-70" at short wavelengths is a measure of the fraction of the viewing area which is blocked by the particles, while the shape of (1-71 is a measure of the particle size. Figure 15 illustrates the calculated shapes of three different sizes.

By way of specific example, the diameters of particles monodispersed in a gas stream, traversing a cell in a system such as illustrated in Figure 1, is obtained by a least squares fitting routine, which compares (l-T") to theoretical . curves. Least squares fitting is a technique which seeks, such as through successive approximations, to minimize the value of the square of the difference between the actual and the computed values for a particular selected parameter. This operation may be conducted iteratively until an acceptable minimization occurs, whereupon those particular values of the parameters are outputted, as ' providing the best fit.
Comparing the theoretical predictions to the curves of Figures 9 and 10 gives the following average particle sizes for the several substances: carbon spheres (Figure 9a) 80 micrometers; copper (Figure 9b) 32 micrometers; potassium chloride (Figure 10a) 80 micrometers; lignite

(Figure 10b) 56 micrometers; and fuel droplets (Figure lOd) greater than 100 micrometers. These values are in reasonable agreement with the corresponding values of 115, 44, 95, 60 and 180, respectively, as determined by sieving or photomicroscopy. Because the latter techniques indicate the largest dimensions of the particles, rather than average values, determination by

( 1- T) plotting would be expected to give smaller particle size indications, as it does.

For mixed sizes, the observed spectrum is least squares fit to the theoretical prediction for a log-normal (or other) distribution. Range and accuracy can be improved by obtaining additional data for smaller acceptance angles Θ , which can be changed by using a variable aperture between the focus "f" and the detector 18. For example, decreasing Q by a factor of 3 will increase the maximum measurable size to approximately 300 micrometers.
In any event, the fitting routine will provide a determination of Qeχt and the average particle diameter (assuming a spherical shape) from which the particle area "A" can be calculated. Then the quantity "N x L" (concentration times" path length) is determined from the known quantitites, according to the derived approximation equation set forth above.
An important factor in analyzing the size distribution for particles has been found to be the value of the extinction of radiation caused by the particles, relative to their blocking area. Extinction of radiation is schematically illustrated in Figure 16, wherein "Qext" (which, in the preferred embodiments of the invention, depends on the entrance aperture of the FT-IR optics) , is plotted against "X" for particles with wavelength-independent optical constants, X being equal to P/\. In the Figure, the "blocking" region (Qext = 1) is on the left. For particles larger than about 100 micrometers, Q is equal to 1 over the whole wavelength region, depending on the value of the refractive index. For smaller particles, Q increases to a maximum value of 2, which effect is observed as an increase in absorption at long wavelengths (see Figures 9a and 9b) . Also indicated in the diagram is the scattering behavior of very small particles, for which X is less than 1. Small soot particles (see Figure 9c) and possibly ash particles (Figure 10c) lie in this range, for the wavelengths of interest for this technique; for such small particles the quantity "(1 - γ) n decreases at long wavelengths.
Analysis of Composition
Quantitative analysis of particulate composition is made using the normalized emission function; emission spectra alone can be employed for semi-qualitative analysis. The representative spectra are obtained when the particles are at low temperatures relative to the surrounding medium; ideally, the particle will be near room temperature or below, with the suspension contained in a chamber having a wall surface temperature of 500 Centigrade, or above.
In the simplest case, there will be no effect from gas or soot absorption or radiation; the particle will be assumed to be at a temperature low enough to neglect its emission, and to be large enough to neglect diffraction effects. Under these circumstances, BB(T )
XT will be approximately zero, Qeχt will equal the quantity

(Q + Qabs) and will have a value of about unity, and En will about equal Qs times the black-body specrum at the temperature of the wall; thus, the general equation for E , set forth above, will reduce to: E =
(1-Q . )BB(T ). In the simple case of potassium chloride, where Qaws is approximately zero (Figure 11a) , EiX equals BB(TW) , which agrees with the observed spectrum.
For samples where Qabs has a value other than zero, the compositional information is contained in the function E . For example, the absorption bands for coal and fuel oil can be seen in the emission spectra of Figures 5a and b, and the normalized emission spectra of Figures lib and lid. The value of Qaws must be related to the shape and optical properties of the particles.
The various effects which have been observed can be quantitatively explained on the basis of refraction of radiation, as schematically indicated in Figure 3, which shows the geometry for the emission and transmission measurements, looking down the axis of the cell 40 with a particle 64 at the focus "f" of the FT-IR beam. The emission spectrum consists of actual emission from the particles (ray "a") , plus radiation (ray"b") from the walls which is diffracted (or reflected) from virtually any angle that is oblique to the port 44 (i.e., off the axis between it and the particle) into the collection optics; ray "c" is a component of incident radiation (e.g., a transmission beam) which has been refracted out of the optical path, and scattered to virtually any angle relative thereto.
For Figures 5 and 11, the particles are cold, so only the radiation scattered (diffracted, refracted or reflected) into the collection optics contributes, and the magnitude of the signal will depend on the size of the particle, the index of refraction of the 'substance, and its absorptivity. For a sphere, exact calculations can be performed to determine absorptivity from E , given the diameter of the particles, the degree of scattering on the surface, and the index of refraction.

In the simple case of non-reflecting spheres of a substance having an index of refraction greater than 1.5, Qaj-_ is approximately equal to the quantity
(1-e —k 7_r*- D) , where k^ is the wavelength dependent absorption coefficient (absorbance) of the sample, and D is the diameter of the sphere, which may be known or computed from {1-Υ) as discussed above. Then, the following derived equation applies:

** - -md-Qabs) = -lπ(En/BB(Tw)
D D

Figure 17 presents a comparison of k, for a jet fuel composition, computed from the foregoing equation using the observed diameter of 180 micrometers, and measured -38-in a liquid cell, respectively; it can be seen that the agreement is excellent.
As indicated above, semi-quantitative spectra can be obtained using emission spectra alone, such as those shown in Figure 5. For that purpose, BB(TW) may be scaled to fit the highest regions of the emission spectra.
Analysis of Emittance
The spectral emittance of particles can be made either with .them cooler or hotter than the surrounding medium (the particles can be heated, for example, in a heated injector, an entrained flow reactor or a heated tube reactor associated with the analytical apparatus) . The simplest case is for large particles (Qext - D , where the particle temperature is greater than that of the envirous (T > T ) , and where soot and absorbing gases are absent (k = k = 0) . Under those conditions, E - BB(T ) and, conversely, = E /BB(T ) .
To determine ■ , measurements were made in a cell with a temperature controlled injector heating the particles to a known equlibrium temperature T .
Examples of En and BB(T ) for char and lignite particles of two size cuts, at different temperatures, are presented in Figure 12. The emittance varies with the degree of pyrolysis and particle size.
To obtain the emittance of cold particles, the simplest case is for large particles, where T. W. is much higher than T , once again in the absence of soot and absorbing gases, in which case the emittance will be equal to (1- [E /BB(T ) ] ) . To determiner, measurements are made in the cell with the wall heated to above 500 Centigrade, and with the particle injector cooled to room temperature or below. Examples of E Xi and BB(TW) for a lignite, potassium chloride, jet fuel and graphite are presented in Figure 11. As can be seen, the spectral emittance varies with the sample composition: for potassium chloride it is approximately zero; for graphite, it is almost 80 percent in agreement with expectations; for the lignite (Figure lid) , the emittance is similar to that determined from the hot lignite (Figure 12d) .
Analysis of Temperature
Temperatures can be obtained for the components of the sample stream even when different components (gas, soot, particles) are not at the same temperature, a. particle temperature
Considering initially the case in which soot and gas contributions can be neglected (k = k = 0) , and diffraction effects are small (Qext is approximately 1) , particulate temperature can be determined from black-body curves, through application of the equation:

En = £ BB(TP) + (1-f*•) BB (Tw) . A particularly simple case occurs when the surrounding wall is much colder than the particle, in which case E is approximately equal to BB(T ), and T can be determined directly by
hr xr
comparing E to computed black-body curves, as in

Figures 12 and 14; E falls on the black-body curve in regions where £ -= 1. Another simple case occurs when the particle and wall are in equlibrium, in which case

En - BB( p), as shown in Figure 13.
For other cases, the equation expressing E in terms of the black-body curve for the wall, provided above, must be solved using an iterative fitting procedure. This requires knowing 6 for at least two wavelengths,
b. particle distributions
One difficulty with a shape-based determination of temperature is that a distribution of particle temperatures can give an emission spectrum which appears to be a good black-body shape corresponding to an intermediate temperature. The amplitude, however, is always found to be lower than that of an isothermal distribution at that intermediate temperature, as illustrated in Figure 18.
Figure 18a compares the spectrum for a 50/50 mix of radiators at 1100° and 1700° Kelvin, with an isothermal case at 1400° K (the "average" temperature) ; there is clearly a difference. The shape of the 50/50 mix curve however can be matched to 0.77 times the black-body curve at 1575° K/ as shown in Figure 18b; therefore, the amplitude of the 50/50 mix does not match the full 1575° black-body curve, and it has been found that the larger the temperature spread, the larger the discrepancy. This illustrates the importance of normalized emission in the particle case. With a good knowledge of , quantitative information about the average temperature of the particles, and the temperature spread, can be inferred by comparing normalized emission shape and amplitude to black-body curves.
Although normalized emission spectra are obtained only in instances in which transmission can be measured, a similar measurement can be made for emission from an optically thick combusting sample. In that case, a calibration can be made on a sample of known single temperature which fills the spectrometer aperture, and amplitudes would again have significance,
c. temperatures of components in mixed phase systems
In monitoring the properties of reacting mixed phase systems, it is desirable to obtain the temperature of individual phases. For example, in coal combustion the spectra contain continuum contributions from both soot and particulates, as well as band contributions from the gases. To determine relative contributions of each phase to absorbance, and the particle, soot and gas phase temperatures, the last two values are assumed to be the same, and the contribution of BB(T W) is ignored in the interpretation of the spectra (as will be clear from the context, the subscripts "s", "p", and "g" refer to soot, the particles, and the gas, respectively) .
The temperature determinations from the continuum region are made at the three wavenumber regions, chosen . . because they lie outside of gas emission lines. For λ less that five micrometers, Qeχt is expected to be unity for particles of diameter greater than about 16
micrometers (see Figure 16) ; Q χt is taken to be unity for this analysis. In addition, it is assumed that the values of are constant with time, and the appropriate value of £ will be substituted in the generalized equation for "E" set forth above, at the three
wavelength regions of interest. From the measured emission and transmission spectra, —lnT" and E are calculated.
With the above approximations, -In 7* (i.e., (k + NA) L) at the three wavenumber regions of interest is made up of a part that is linear as a function of wavenumer (k ) , and a part that is independent (NA) .
These two straight line contributions can be separated from the In/ data, giving the relative "amounts" of k and NA at each wavenumber region, as illustrated in
Figure 20.
With the approximations made, the normalized emission in the regions free of gas contributions is: E

= [ks BB(Ts) + NA BB( p)]/(ks + NA) , the ratio ks/NA being known from the transmittance, as discussed above.

By dividing the above equation by ks_ and simplifying, the expression becomes:
[Bn (1 + NA/ks) = BB(TS) + (NA/kg) £ BB(T )] i, the "i" denoting that the equation is for three (or more) wavenumber regions. The unknown quantities are the black-body amplitudes, which can be found by a least squares minimization using an iterative fitting routine, after postulating trial values of and T . The amplitudes of the black-body curves for all temperatures can be calculated from the black-body reference spectrum.
In the region of the spectra containing gas lines, the ratio of k to ( + NA) can be determined from the

-In/ curve. With this information, and with known

(from the continuum-only measurement discussed above) , the gas temperature can be determined from the normalized emission, using the generalized formulas, and the En relationship to emission and trasmittance spectra, previously set forth.
Where soot is present, the comparison of T and T from these two methods will provide an extra check on the data. A comparison of determined E , with a theoretical E made up of separate contributions from gas, soot and particles, is shown in Figure 20. The agreement with reasonable values for the temperatures of the separate phases, determined in Figure 19, is seen to be excellent.

d. particle temperatures from emission only
In obtaining particle temperatures, the use of normalized emission has two advantages: (1) the fit of amplitude, as well as of shape, affords improved precision and the potential for determination of particle temperature spreads; (2) it provides the ability to determine soot temperatures. However, some monitoring applications may preclude the determination of transmittance, which generally requires entrance and exit ports along a line-of-sight, and (extinction-path length) products sufficiently small so that at least 15 percent transmission is achieved. When there is a very small degree of transmission because of particle blocking, the spectra will tend to that of 6 • For cases without fine soot, a temperature measurement may be obtained from the shape of the ray emission; again, knowledge of c is required to make this determination more accurate.
For several spectra, a temperature of combusting coal particles has been derived from an "n-color" black-body fit of the raw emission. The n- original colors are the five wavelength regions designated on the raw emission spectra shown in Figure 8 where interference from gas emission is minimized.
On applying this method to the spectra of combusting species with higher gaseous emission, however, it became clear that only the three higher wavenumber regions could be considered to lie outside of overlapping gas lines. Char is presented in Figure 8a, lignite in Figure 8b, and bituminous coal in Figures 8c and d; the circled regions of the spectra correspond to the five wavelength regions chosen. Only the three higher wavenumber regions were used for the black-body fits, since the two lower ones appeared to have interference at high water levels.
The measurement is seen to agree well with those from the normalized emission technique, illustrated in Figure 14. Eliminating the requirements for transmission measurements will make the instant technique more flexible, and therefore more desirable in some situations.
Theory
The scattering, absorption, transmission and emission of electromagnetic radiation by and from particles depend both upon material properties, in the form of optical constants, and on morphology, which can be represented by scales of inhomogeneity relative to wavelength. The interaction of particles with a radiation field can be characterized by
wavenumber-dependent efficiency factors "Q", which express the effective cross sections for scattering or absorption, divided by the geometric cross section of the particles; thus, Qext = Qs + Qat>s- where the subscripts stand for extinction, scattering and -46-absorption, respectively. As used herein "Qsπ refers to radiation scattered out of the acceptance angle of the optics, and the other Q**s are similarly specific to the optical beam path.
In developing the basic equation and generalized formulas underlying the analytical techniques and apparatus of this invention, and from which the simplified equations employed for the several analyses are derived, a model was developed to quantitatively account for many features of the observed normalized emission spectra. One feature of the model relates to the geometry of the particles in the sample cell (as described above in connection with Figure 3) , from which it is concluded that the efficiency for scattering of radiation out of the beam path in a transmission experiment (e.g., ray "c") is equal to the efficiency for scattering wall radiation into the beam in an emission experiment (e.g., ray "b") , for particles within the focus volume.
To describe the emission, transmission, and scattering behavior of a multi-phase suspension (i.e., containing gas, particles and soot) , the model developed was based upon the assumption that: (1) gas and fine particulates (soot) are at one temperature within the analyzed volume; (2) particles larger than 0.3 micron are at one temperature, not necessarily that of the gas; (3) the molecular concentration of each constituent.

averaged over a volume containing many particles, is constant throughout the analyzed volume; and (4) the density of large particles is small, so that less than 0.2 of the radiation is blocked by them. Also, assuming that "L" is the effective path length through a sample located in a cell or reactor, with walls at temperature T surrounding the sample volume, the following expressions for the radiation "E" emanating from the cell, and for the radiation (expressed in terms of transmittance "- ") transmitted through the sample, respectively, were developed:

E =
[ksBB(Tg)+kgBB(Tg)+NA£BB(Tp)+NAQsBB(Tw)]- [1-exp (- (ks+kg+NAQeχt) L) ]
kes + kg + NAQΩeVxt.
and
(1-/) = l-exp[-(ks + kg + NAQeχfc)L],

the terms of which formulas are defined elsewhere herein. The analysis is readily extended, by use of the above-defined basic equation, or equations derived therefrom, to include ash, to include samples that are non-homogeneous along the path length "L", and to accommodate other deviations from the assumptions made and expressed herein; such analyses will of course be correspondingly more complex.
As noted above, the normalized emission has previously been used for both gaseous and soot flames.

in which cases E is simply the black-body curve appropriate to the temperature of the flame in both shape and amplitude. The present invention, however, involves the discovery of the significance of normalized emission for particle spectra, and the use thereof for analysis of the several parameters of the particle suspensions discussed herein. It involves, moreover, the discovery of techniques for utilizing the components of spectum of In/ = (kg + k + NA QeX|-)L, the use of En to obtain composition data for the particles, and of / to obtain particle size and density. Furthermore, it has been found that, in those cases in which Qext*--l the spectral variation of can be determined using normalized emission, together with a measurement of by an auxilliary technique; no other method is believed to exist for determining the spectral emittance of particles.
As discussed above, composition analysis is performed under conditions where the particles are cool and the wall is hot, and in the absence of absorbing gas or soot; where Qpxt =■ 1, the normalized emission is approximately equal to the expression: (1-Q b )BB(T ). The compositional information is contained in the Qabs term, which must be calculated from the properties of the particles.
Mie theory predicts the scattering of radiation of particles as a function of wavelength, particle size.

and optical constants. Certain aspects of the present invention utilize the fact that radiation from hot cell walls (or other surrounding medium at a temperature above that of the particles) passes through particles in the center and is diverted along other paths. By collecting the portion of such radiation that is directed towards an emission detector, the detected spectrum, missing energy at wavelengths in the absorption bands of- the particle it has passed through, can be used for analysis of composition.
To optimize this determination, however, it is necessary to predict, based upon the shape and optical constants of the particles, the relative magnitudes of Q and Qabs; this is done, in accordance herewith, by evaluating effective transmission "T"*" of radiation scattered therethrough. The plot of Figure 4 shows calculations of " for particles that can be categorized as having one of four basic configurations, or gross geometries; in the plot, "k^ " is the
wavelength-dependent absorption coefficient, and D is a characteristic dimension for the geometry.
More particularly, a thin film of thickness D will transmit radiation in accordance with Beer's Law, and consequently the expression: -In (T') = k,D will apply; for such particles, k will equal [-ln(En/BB(Tw) )/D] . For sperical particles having a range of surface roughnesses, the effective transmission is given by the equation:


wherein the factor "? r_\ " expresses the probability that any particular ray will travel a distance "d" before emerging from the particle. For perfectly scattering speriσal particles, the applicable equation is:



wherein D is the particle diameter.
To derive an expression for prismatic flakes (such as coal particles) , "D" was taken as the diameter of a sphere of the same volume as the flake, knowing the mesh size and the typical geometry of the sample. In Figure 4, data bars are extracted from normalized emission spectra of cold coal particles within a hot environment; regions within the E spectra for both 170 x 200 mesh Zap lignite and 400 x 500 mesh Zap lignite were selected for calculation of these data points. The quantity (-InT') is calculated to be [-In (EΠ/BB(T ))], corrected to account for a reflective component of five to ten percent. For the chosen regions of the spectra, k was determined from potassium bromide pellet spectra. The calculated values of -InT"* were found to be in good agreement with the measured values.

Thus it can be seen that the present invention provides a novel method, and novel apparatus for carrying it out, by which gaseous suspensions of liquid and/or solid particles can readily be analyzed for any of a variety of physical and chemical properties. The invention provides, more specifically, such a method and apparatus by which a gaseous suspension can be analyzed either in-situ, in a reactive environment, or as a supplied sample, for determinations of particle size, temperature, number density, spectral emittance and/or composition, and which is carried out in a manner that is relatively accurate and is very fast and convenient.