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| United States Patent | 4805623 |
| Link to this page | http://www.wikipatents.com/4805623.html |
| Inventor(s) | Jobsis; Frans F. (Efland, NC) |
| Abstract | A spectrophotometric method is described of quantitatively determining the
concentration of a dilute component in either a clear or a strongly
light-scattering environment containing same in unknown concentration
together with a reference component of known concentration, by a series of
contemporaneous radiation-directing and measurement steps of radiation of
selected varying wavelengths. Specific applications are disclosed
involving the in situ, in vivo, non-invasive spectrophotometric
determination of blood-borne as well as tissue species, e.g., hemoglobin,
and oxyhemoglobin, and intra-cellular enzyme cytochrome c oxidase, in
human body parts such as fingers, hands, toes, feet, earlobes, etc., as
well as organs such as the brain, skeletal muscle, liver, etc. |
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Title Information  |
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Drawing from US Patent 4805623 |
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Spectrophotometric method for quantitatively determining the
concentration of a dilute component in a light- or other
radiation-scattering environment |
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| Publication Date |
February 21, 1989 |
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| Filing Date |
September 4, 1987 |
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Title Information  |
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References  |
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U.S. References |
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| | Reference | Relevancy | Comments | Reference | Relevancy | Comments | 3790797
|      Your vote accepted [0 after 0 votes] | | 4714080 Edgar, Jr. 600/330 Dec,1987 |      Your vote accepted [0 after 0 votes] | | 4707603 Miemela 250/339.08 Nov,1987 |      Your vote accepted [0 after 0 votes] | | 4697593 Evans 600/343 Oct,1987 |      Your vote accepted [0 after 0 votes] | | 4655225 Dahne 600/316 Apr,1987 |      Your vote accepted [0 after 0 votes] | | 4651741 Passafaro 600/328 Mar,1987 |      Your vote accepted [0 after 0 votes] | | 4629322 Pollard 356/300 Dec,1986 |      Your vote accepted [0 after 0 votes] | | 4623248 Sperinde 356/41 Nov,1986 |      Your vote accepted [0 after 0 votes] | | 4509522 Manuccia 600/326 Apr,1985 |      Your vote accepted [0 after 0 votes] | | 4467812 Stoller 600/475 Aug,1984 |      Your vote accepted [0 after 0 votes] | | 4446871 Imura 600/323 May,1984 |      Your vote accepted [0 after 0 votes] | | 4427889 Muller 250/339.11 Jan,1984 |      Your vote accepted [0 after 0 votes] | | 4407290 Wilber 600/330 Oct,1983 |      Your vote accepted [0 after 0 votes] | | 4299487 Sengoku 356/320 Nov,1981 |      Your vote accepted [0 after 0 votes] | | 4281645 Jobsis 600/324 Aug,1981 |      Your vote accepted [0 after 0 votes] | | 4223680 Jobsis 600/324 Sep,1980 |      Your vote accepted [0 after 0 votes] | | 4167331 Nielsen 356/39 Sep,1979 |      Your vote accepted [0 after 0 votes] | | 4166454 Meijer 600/479 Sep,1979 |      Your vote accepted [0 after 0 votes] | | 4114604 Shaw 600/339 Sep,1978 |      Your vote accepted [0 after 0 votes] | | 4086915 Kofsky 600/330 May,1978 |      Your vote accepted [0 after 0 votes] | | 3825342 Lubbers 356/41 Jul,1974 |      Your vote accepted [0 after 0 votes] | | | | | |
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| Market Size |
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| Reasonable Royalty |
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Market Review  |
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Technical Review  |
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Claims  |
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What is claimed is:
1. A spectrophotometric method of quantitatively determining the
concentration of a dilute component in an environment containing the
dilute component of known identity but of unknown concentration in
combination with a reference component of known concentration, by a series
of successive, substantially contemporaneous measurements of transmitted
and/or reflected radiation at selected wavelengths, comprising:
(a) determining the apparent effective pathlength in said environment;
(b) directing at said environment incident electromagnetic radiation of a
first wavelength in a selected spectral region at which the dilute and/or
reference component(s) exhibit absorption for the electromagnetic
radiation;
(c) measuring the first wavelength radiation transmitted and/or reflected
by the environment;
(d) directing at the environment incident electromagnetic radiation of at
least one other wavelength in the selected spectral region at which the
dilute and/or reference component(s) exhibit absorption of different
relative intensities than for the first wavelength incident radiation;
(e) measuring the other wavelength radiation transmitted and/or reflected
by the environment;
(f) determining extinction coefficient values for the dilute component at
said first and other wavelengths in said environment; and
(g) based on the apparent effective pathlength determined for the
environment, the extinction coefficient values for the dilute component at
said first, and other wavelengths, and the measured absorbed and/or
reflected radiation at said wavelengths, determining the relative amount
of the dilute component to the amount of the reference component, as the
concentration of the dilute component in the environment.
2. A method according to claim 1, wherein said apparent effective
pathlength of said environment is determined by the steps comprising:
(i) measuring the absorbance of said reference component at different
selected wavelengths in said selected spectral region;
(ii) calculating the differential absorbance from the measured absorbance
values;
(iii) determining the extinction coefficient values for said reference
component at the different selected wavelengths of step (i);
(iv) calculating the differential extinction coefficient from the
determined extinction coefficient values for said reference component; and
(v) dividing the differential absorbance by the differential extinction
coefficient to yield the apparent effective pathlength of said
environment.
3. A method according to claim 1, wherein said determination of step (f) is
effected by establishing simultaneous modified Beer-Lambert equations for
each of said absorption/scattering measurement steps, and solving said
equations for the concentrations of said dilute component and said
reference component is said environment.
4. A method according to claim 1, wherein a second dilute component of
unknown concentration is contained in said environment, and wherein
electromagnetic radiation of a third wavelength in said selected spectral
region is directed at said environment at which said second dilute
component exhibits an absorption for the electromagnetic radiation, and
the third wavelength radiation transmitted and/or reflected by the
environment is measured, and employed to determine the relative amount of
the second dilute component to the amount of the reference component.
5. A method according to claim 4, wherein three simultaneous modified
Beer-Lambert equations are established for the concentration of the dilute
components and reference component in said environment.
6. A method according to claim 1, wherein said environment effects
scattering of said electromagnetic radiation which is independent of
wavelength of said radiation, and wherein the transmitted and/or reflected
radiation is measured at a single additional wavelength.
7. A method according to claim 1, wherein said environment effects
scattering of said electromagnetic radiation to an extent which is of
sloped linear relationship to wavelength, and wherein the transmitted
and/or reflected radiation is measured at an additional two wavelengths.
8. A method according to claim 1, wherein said environment effects
wavelength scattering of said electromagnetic radiation which is a
non-linear function of wavelength, and wherein the transmitted and/or
reflected radiation is measured at an additional at least three
wavelengths.
9. A method according to claim 1, wherein said environment is a corporeal
environment.
10. A method according to claim 9, wherein said environment is selected
from the group consisting of corporeal tissue and corporeal organs.
11. A method according to claim 9, wherein the dilute component is selected
from the group consisting of tissue components and blood-borne species.
12. A method according to claim 9, wherein the dilute component is selected
from the group consisting of enzymes, metabolites, substrates, waste
products and poisons.
13. A method according to claim 9, wherein the dilute component is selected
form the group consisting of glucose, hemoglobin, oxyhemoglobin, and
cytochrome a,a.sub.3.
14. A method according to claim 9, wherein said corporeal environment
comprises a body portion selected from the group consisting of heads,
fingers, hands, toes, feet, and earlobes.
15. A method according to claim 9, wherein said reference component is
water.
16. A method according to claim 1, wherein said environment comprises an
externally added indicator solution as a reference component.
17. A method according to claim 14, wherein said environment is a corporeal
corpse body moiety, and said indicator is an aqueous solution of
indocyanine green dye.
18. A method according to claim 1, wherein a first dilute component and
reference component exhibit absorption for the electromagnetic radiation
in said selected spectral region and a second dilute component does not
exhibit absorption for the electromagnetic radiation in said spectral
region, and wherein the first and second dilute components exhibit
absorption for electromagnetic radiation in a second spectral region
closely proximate to said selected spectral region and in which the
reference component does not exhibit absorption for the electromagnetic
radiation, comprising determining the relative amount of the first dilute
component to the amount of the reference component in said selected
spectral region as the concentration of the first dilute component in the
environment, and utilizing the first dilute component whose concentration
is thus determined, as a reference component for the second dilute
component in said second spectral region.
19. A method according to claim 1, wherein said electromagnetic radiation
is infrared radiation having a wavelength in the range of from about 700
to about 1400 nanometers.
20. A method according to claim 1, wherein subsequent to determination of
the concentration of the dilute component in the environment, the
environment is monitored for changes in said concentration.
21. Apparatus for spectrophotometrically quantitatively determining the
concentration of a dilute component in an environment containing the
dilute component of known identity but of unknown concentration in
combination with a reference component of known concentration, comprising:
(a) means for producing electromagnetic radiation of known wavelengths and
directing said radiation into the environment to be characterized for the
dilute component;
(b) means for detecting electromagnetic radiation emanating from and/or
reflected from the environment and producing therefrom an electrical
signal corresponding thereto;
(c) means for receiving said electrical signal and producing therefrom
electrical signals corresponding to said different wavelengths;
(d) means receiving and operatively responsive to said electrical signals
corresponding to said different wavelengths, to establish absorbance
equations responsive to said electrical signals corresponding to said
different wavelengths, wherein absorbance at each of the wavelengths is
expressed as a function of the relative intensities of the absorption
contributions of the dilute and reference components and the
concentrations of the dilute and reference components, and for calculating
the amounts of the dilute and reference components by solution of said
absorbance equations; and
(e) means for displaying the calculated concentrations of said dilute and
reference components.
22. A spectrophotometric method of quantitatively determining the
concentration of a dilute component in an environment containing the
dilute component of known identity but of unknown concentration in
combination with a reference component of known concentration, comprising:
(a) directing at the environment incident electromagnetic radiation at a
number of wavelengths in a selected spectral region at which the dilute
and/or reference components exhibit absorption for the electromagnetic
radiation, the number of said wavelengths being determined by the number
of dilute and reference components in the environment, and the scattering
characteristics of the environment;
(b) determining the absorbance by the environment of the electromagnetic
radiation at the various wavelengths and the relative intensities of the
absorption contributions of the dilute and reference componets and
scattering losses from the environment at each of said wavelengths;
(c) at each of said wavelengths, establishing absorption equations of the
form:
##EQU6##
wherein: Abs.sub.w is the absorbance by the environment, containing the
dilute and reference components, of the incident electromagnetic radiation
of wavelength w; x.sub.i is the relative intensity of the absorption
contribution of the associated dilute component A.sub.i, and wherein terms
of the form x.sub.i A.sub.i are set forth for each of the dilute
components; n is the number of dilute components; z is the relative
intensity of the absorption contribution of the reference component; R is
the concentration of the reference component; and S is the normalized
scattering of the environment at wavelength w; thereby establishing for
each of said wavelengths an absorbance equation, to yield a set of
simultaneous equations whose number equals the number of dilute and
reference components and the number of wavelengths required to
characterize the scattering of the environment;
(d) deriving algorithms by matrix solution of said simultaneous equations,
said algorithms being of the form:
##EQU7##
wherein: [c] is the concentration of the specific dilute or reference
component; a.sub.i is a determined numerical constant; m is the number of
said wavelength determinations; Abs.sub.w.sbsb.i is the absorbance at
wavelength w; thereby establishing the concentration of each of the dilute
and reference components in the environment.
23. A method according to claim 22, wherein subsequent to determination of
the concentration of each of the dilute and reference components in the
environment, the environment is monitored to determine changes in said
concentrations. |
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Claims  |
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Description  |
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BACKGROUND OF THE INVENTION
1. Field of the Invention
This invention generally relates to a spectrophotometric method of
quantitatively determining the concentration of a dilute component in a
light- or other radiation-scattering environment containing the dilute
component in combination with a reference component of known
concentration.
2. Description of the Related Art
In many fields of technology there is a need for quantitative determination
of dilute component concentrations in environments where the dilute
component is in combination with a reference component of known
concentration. Examples of illustrative environments of such type include
enzymes, proteins, and metabolites in corporeal fluids; acidic fumes or
gaseous components (e.g., hydrogen sulfide and sulfuric acid, nitric acid,
carbon monoxide, etc.) in the atmosphere; salt concentrations in sea water
undergoing desalination; ozone in ozone-enriched air utilized in waste
water ozonation systems, etc.
In particular, there has been a specific need in the medical and health
care fields for a non-invasive, continuous, atraumatic, in vivo, in situ
determination of amounts of critical metabolic indicators in body fluids
or tissues of human patients. Examples of such body fluids include the
blood and fluids associated with the lymphatic and neurological systems of
the body. Further specific examples involving the human circulatory system
include the monitoring of glucose and of oxygenated/de-oxygenated,
arterial/venous colored hemoglobin in the blood stream. In addition,
monitoring in localized tissue, such as brain and muscle, of certain
enzyme species such as the cytochrome c oxidase enzyme (unofficially
better known as cytochrome a, a.sub.3) or metabolic substrates (such as
glucose) or products (such as carbon dioxide) is becoming an increasingly
urgent practical application of spectrophotometric technology.
Spectrophotometric methods have been proposed in the art to monitor
metabolites in corporeal fluids. Such methods involve the impingement of
radiation, typically in the visible or near-infrared region, onto the
exterior body portion of the subject for transdermal and interior tissue
penetration of the radiation, which is monitored as to its reflectance or
transmission, at a wavelength condition at which the metabolite or other
monitored component is selectively absorptive for the radiation. This
technique is mainly limited to yielding a qualitative determination from
the measured output radiation (reflected or transmitted) of the
qualitative character of the metabolism. At best a semi-quantitative
result can be obtained in a so-called trend monitoring mode where
concentration changes can be monitored in terms of an original baseline
condition of unknown concentration.
Solute concentrations in dilute fluid media can be theoretically quantified
by the Beer-Lambert law, i.e.,
log (I.sub.o /I)=d.times.E.times.c
wherein:
I.sub.0 =intensity of source radiation impinged on the sample;
I=intensity of radiation transmitted through the sample;
E=absorption (extinction) coefficient of the solute species at the
wavelength of the source radiation impinged on the sample;
d=optical distance (travel pathlength of the radiation transmitted through
the sample); and
c=concentration of the solute (dilute component) in the solution sample.
Although the foregoing Beer-Lambert Law equation permits a ready
determination of solute concentration to be made in in vitro or other
non-corporeal discrete sample systems utilized for conventional
spectrophotometric assays, such direct, quantitative measurement is not
possible in the intact body, even though the influent radiation is
penetrative of the body elements of the corporeal system, e.g., bones,
musculature, organs, and the like, since the scattering of radiation
during its passage through the corporeal system is extensive and highly
variable in character. Such scattering not only adds an unknown loss of
radiation to the required information regarding specific absorption but by
multiple scattering it also lengthens to an unknown degree the path length
of those photons eventually emerging from the body element. As a result,
it has not been possible to determine in an in vivo situation what the
effective path length, d, of the impinged radiation actually is, prior to
measurement of the transmitted or reflected radiation derived therefrom.
In consequence, the absolute quantitation of solute concentrations in
corporeal systems has been severely adversely limited.
Faced with the alternatives of invasive and traumatic sampling of the
corporeal fluids of interest, or spectrophotometric methods which realize
only qualitative or at best semi-quantitative measurement of changes in
tissue or body fluid solute concentrations, there is a substantial
perceived need in the art for a non-invasive, in vivo method of
quantitatively determining the concentration in corporeal solution of a
solute in a body fluid solvent.
A similar need exists in numerous other fields in which absolute
concentrations of dilute component species in fluid media would materially
assist the characterization of the fluid system. An example is atmospheric
monitoring of "acid rain", i.e., airborne acidic contaminants which have
in recent years proliferated and been determined to cause widespread
biospheric damage, including the defoliation of forest stocks and
spoliation of natural bodies of water and other aqueous environments. It
is anticipated that in coming years with the increasing severity of the
acid rain problem, correspondingly greater scientific and legislative
efforts will be focused on the monitoring of acid rain with a view to
controlling and minimizing its adverse impacts. Determinations in the
naturally existing medium such as turbid water and hazy or cloudy
atmosphere will be a great boon for direct, effective and rapid monitoring
of these environments.
In numerous other industrial and natural systems there is a need to
quantitatively monitor solute species in an indirect manner not involving
the time, effort, and cost of discrete sample collection, purification and
analysis.
U.S. Pat. No. 4,281,645 to F. F. Jobsis describes a spectrophotometric
system for monitoring cellular oxidative metabolism by non-invasively
measuring in vivo changes in the steady state oxidation-reduction of
cellular cytochromes together with changes in blood volume, the oxidation
state of hemoglobin and the rate of blood flow in the brain, heart,
kidneys, other organs, limbs, or other parts of a human or animal body.
The methodology described in the Jobsis patent involves transmitting
near-infrared radiation in at least two different and periodically
recurring wavelengths through the corporeal environment, and detecting and
measuring the radiation intensity which emerges at another, distant point
or on the opposite side of the body, for the monitoring of biochemical
reactions, utilizing an approximation of the Beer-Lambert law. One of such
wavelengths selected for the measurement is in a range for which oxidized
cytochrome a, a.sub.3, is selectively highly absorptive. One or more
reference signals are provided at corresponding wavelengths outside the
peak of the cytochrome absorption band but preferably in close proximity
to the measuring wavelength. The difference or ratio between the measuring
and reference signals is determined and non-specific changes in the
intensity of transmitted radiation not attributable to absorption by the
cytochrome species are eliminated. Thus, the system of this patent
produces an output signal representing the difference in or ratio of
absorption of the measuring and reference wavelengths by the organ or
other corporeal portion of the body as a function of the state of the
metabolic activity in vivo, which may be converted to a signal providing a
substantially continuous measure of such activity. A related
spectrophotometric reflectance technique is disclosed in U.S. Pat. No.
4,223,680 to F. F. Jobsis.
U.S. Pat. No. 4,655,225 to C. Dahne et al discloses a spectrophotometric
system for non-invasive determination of glucose concentration in body
tissue. The system involves irradiation of the exterior body portion with
an optical light whose transmittance or reflectance is collected at
selected band wavelength values for the glucose absorption spectrum and at
a selected band wavelength value for the absorption spectrum of background
tissue containing no or insignificant amounts of glucose. The measuring
and reference radiation collected is then converted into electrical
signals and utilized to determine glucose concentrations.
It is an object of the present invention to provide an improved method and
apparatus for indirectly quantitatively, spectrophotometrically
determining the amounts of a dilute component by using a reference
component in the environment of interest.
It is another object of the invention to provide such a method for
non-invasive, in vivo quantitative determination of the concentration of a
dilute solute component in a corporeal solvent environment.
Other objects and advantages of the present invention will be more fully
apparent from the ensuing disclosure and appended claims.
SUMMARY OF THE INVENTION
The present invention relates to a method of determining the true
concentration (e.g., in terms of grams or moles of a dilute component per
volume of a reference component) in environmental media in which the
optical pathlength is ill-defined due to the extensive occurence of
scattering of incident radiation, such as in very long distance
atmospheric monitoring as well as in more intensely light scattering media
during transillumination as well as diffuse reflectance modes of
spectrophotometry.
As used herein, the term "environment" refers to a selected spatial region
in which the directed and measured radiation is transmitted and/or
reflected along substantially the same path.
The crux of the invention is to measure the transmitted and/or reflected
radiation for both the dilute component of unknown concentration and the
reference component of known concentration with which it is associated.
Multiple scattering spoils the optical pathlength parameter in the
Beer-Lambert equation and does so to different degrees depending on the
wavelength. It is, therefore, necessary to measure the dilute and
reference components in closely the same spectral region. Measuring the
intensity of the light absorption and/or reflectance by the two types of
molecules, dilute component and reference component, in the environment
and applying the extinction coefficients of each provides the opportunity
to relate them to one another in terms of relative amounts, which is
recognized as being the essential character of concentration. Thus, by
absorption (and/or reflectance) measurements and with knowledge of the
extinction coefficients, the amount of dilute component in the light path
and the amount of reference component it is associated with, determined
similarly at other near-by wavelength(s), may be employed to calculate the
concentration of the dilute component relative to the reference component.
In a system in which the reference component is present in known
concentration, the apparent pathlength may be determined by absorption
measurements taken in the environment of unknown pathlength in the same
electromagnetic spectral region. The difference between the resulting
absorption values is calculated as the differential absorbance in the
environment whose pathlength is to be determined. The tabulated or
previously determined extinction coefficient values of the pure reference
component at such wavelengths are then employed to calculate the
differential extinction coefficient, as the difference between the
respective extinction coefficient values. When the differential absorbance
is then divided by the differential extinction coefficient, the result is
the apparent effective pathlength of the environment. When the
electromagnetic radiation emitter and detector spacing distance is
measured, the pathlengthening factor for the system is determined as the
ratio of the apparent effective pathlength to the actual
emitter-to-detector spacing distance.
In another selected, specific aspect, the invention relates to a
spectrophotometric method of quantitatively determining the concentration
of a dilute component in an environment containing the dilute component of
known identity but of unknown concentration in combination with a
reference component of known concentration, by a series of successive,
substantially contemporaneous measurements of transmitted and/or reflected
radiation at selected wavelengths, comprising:
(a) determining the apparent effective pathlength in said environment;
(b) directing at the environment incident electromagnetic radiation of a
first wavelength in a selected spectral region at which the dilute and/or
reference component(s) exhibit absorption for the electromagnetic
radiation;
(c) measuring the first wavelength radiation transmitted and/or reflected
by the environment;
(d) directing at the environment incident electromagnetic radiation of at
least one other wavelength in the selected spectral region at which the
dilute and/or reference component(s) exhibit absorption of different
relative intensities than for the first wavelength incident radiation,
whereby absorption is exhibited in said selected spectral region
comprising said first and at least one other wavelength by both the dilute
and the reference component(s);
(e) measuring the other wavelength radiation transmitted or reflected by
the envinroment; and
(f) determining extinction coefficient values for the dilute component at
said first and other wavelengths in said environment; and
(g) based on the apparent effective pathlength determined for the
environment, extinction coefficient values for the dilute component at
said first and other wavelengths, and the measured absorbed and/or
reflected radiation at said wavelengths, determining the relative amount
of the dilute component to the amount of the reference component, as the
concentration of the dilute component in the environment.
In another aspect of the method broadly described above, the determination
of step (f) is effected by establishing simultaneous modified Beer-Lambert
equations for each of the radiation absorption and/or reflectance
measurement steps, and solving the equations for the concentrations of the
dilute component and the reference component in the environment.
A further aspect of the invention relates to a spectrophotometric method of
quantitatively determining the concentration of a dilute component in an
environment containing the dilute component of known identity but of
unknown concentration in combination with a reference component of known
concentration, comprising:
(a) directing at the environment incident electromagnetic radiation at a
number of wavelengths in a selected spectral region at which the dilute
and/or reference components exhibit absorption for the electromagnetic
radiation, the number of such wavelengths being determined by the number
of dilute and reference components in the environment, and the scattering
characteristics of the environment;
(b) determining the absorbance of the environment of the electromagnetic
radiation at the various wavelengths and the relative intensities of the
absorption contributions of the dilute and reference components and
scattering losses from the environment at each of such wavelengths;
(c) at each of such wavelengths, establishing absorption equations of the
form:
##EQU1##
wherein: Abs.sub.w is the absorbance by the environment, containing the
dilute and reference components, of the incident electromagnetic radiation
of wavelength w; x.sub.i is the relative intensity of the absorption
contribution of the associated dilute component A.sub.i, and wherein terms
of the form x.sub.i A.sub.i are set forth for each of the dilute
components; n is the number of dilute components; z is the relative
intensity of the absorption contribution of the reference component; R is
the concentration of the reference component; and S is the normalized
scattering of the environment at wavelength w, thereby establishing for
each of such wavelengths an absorbance equation, to yield a set of
simultaneous equations whose number equals the number of dilute and
reference components and the number of wavelengths required to
characterize the scattering of the environment;
(d) deriving algorithms by matrix solution of the aforementioned
simultaneous equations, said algorithms being of the form:
##EQU2##
wherein: [c] is the concentration of the specific dilute or reference
component, a.sub.i is a determined numerical constant; m is the number of
said wavelength determinations; | | |