Chemical sensing method and apparatus employing liquid-core optical fibers

Abstract: A permeable optical fiber waveguide 10 with a liquid core 12 is employed as a probe for the detection or measurement of a chemical specie of interest by filling the waveguide core region with a light transmitting reagent liquid 12' which undergoes a change in an optical characteristic thereof when exposed to the chemical specie and then inserting the filled waveguide 10 into an environment in which the chemical specie may be present. The chemical specie, if present, will permeate through the waveguide wall and react with or be absorbed in the core liquid.

Description: This invention relates to the optical detection of different chemical species and, particularly, to the identification and/or measurement of chemical substances of interest through detection of changes in the optical properties of a reagent/solvent caused by the reaction with or dissolution of the said chemical substance in the reagent/solvent. More specifically, the present invention is directed to optically detecting the presence, and/or concentration of species which are in the gas or vapor phase or are dissolved in a liquid matrix and, especially, to sensing changes in the optical properties of a confined light conducting medium resulting from exposure of the confining vessel to the sample matrix of interest. Accordingly, the general objects of the present invention are to provide novel and improved techniques of such character. The use of fiber optics in chemical analysis is known in the art. In the prior art, there are two main classes of fiber optic based sensors employed in such analysis. In a first type of prior art sensor, a relatively long length of optical fiber is employed as the sensing element and analysis light passed through the fiber interacts with the medium surrounding the fiber. This interaction occurs because the light used to internally illuminate the fiber, i.e., the analysis light, penetrates the external medium to a distance equivalent to 1/4 of its wavelength, i.e., to a distance much less than the radius of the fiber. Such sensors are called evanescent wave sensors. The main disadvantage incident to the use of evanescent sensors is limited sensitivity. (See for example, "Fiber Optic Optrodes for Chemical Sensing", Brenci and Baldini, in Proceedings, 8th International Conference on Optical Fiber Sensors, pages 313-319, 1992; and "Fiber-Optic pH Sensor Based on Evanescent Wave Absorption Spectroscopy", Ge et al, Analytical Chemistry, volume 65, pages 2335-2338, 1993.) In the second type of prior art fiber optic based chemical sensor, which has found more practical applications when compared to the above-mentioned type device, light launched into the proximal end of an optical fiber emerges at the distal end thereof to interact with a "target" substrate or solution that is affected by the chemical composition of the medium in which the target is present. The light interaction can be probed by observing changes in either light absorption or the emission properties of the target substrate/solution. In a fluorometric mode of operation, a light beam of a wavelength suitable to excite fluorescence is launched through the fiber and the emitted fluorescent light is collected by, for example, the same fiber and separated by a suitable optical arrangement such as a dichroic mirror. (See, e.g., "Enzyme-based Fiber Optic Zinc Biosensor", Thompson and Jones, Analytical Chemistry, volume 65, pages 730-734, 1993); and "Fiber Optic pH Sensor Based on Phase Fluorescence Lifetime", Thompson and Lakowicz, Analytical Chemistry, volume 65, pages 853-856, 1993). Alternatively, the emitted fluorescent light can be collected by a second fiber(s). (See, e.g., "Novel Techniques and Materials for Fiber Optic Chemical Sensing", Wolfbeis, in Optical Fiber Sensors, Springer Proceedings in Physics, Volume 44, pages 416-424, 1989). Absorptiometric measurements employing the above-discussed second . type of prior art sensor typically implement a bifurcated collection technique, i.e., a second fiber(s) is used to receive the light to be analyzed. Most commonly, in absorption-type sensors, a reflecting optical target containing an immobilized reagent which undergoes a spectral change upon interaction with an analyte of interest in the surrounding medium is located at the fiber tip. Light (monochromatic or broadband) launched through the fiber is reflected off this target and single or multiwavelength measurements are made on the reflected light. (See, e.g., "Potentiometric and Fiber Optic Sensors for pH Based on an Electropolymerized Cobalt Porphyrin"), Blair et al, Analytical Chemistry, volume 65, pages 2155-2158, 1993; "Fiber Optic Sensors for pH and Carbon Dioxide Using a Self Referencing Dye", Parker et al, Analytical Chemistry, volume 65, pages 2329-2334, 1993; and "Current Developments in Optical Biochemical Sensors", Narayanaswamy, Biosensors and Bloelectronlcs, Volume 6, pages 467-475, 1991). Such immobilized reagents can also be used for fluorescence measurements. (See, e.g.," Fluorocarbon-based Immobilization of a Fluoroionophore for Preparation of Fiber Optic Sensors", Blair et al, Analytical Chemistry, volume 65, pages 945-947.) The employment of an immobilized reagent, while attractive in theory, generally results in a sensor with a limited lifetime due to reagent loss from photodecomposition or leaching. To solve this problem, resort has been had to renewing the reagent and, particularly, to flowing the reagent through the sensor probe. (See, e.g., "Measurement of Seawater pCO 2 Using a Renewable - Reagent Fiber Optic Sensor with Colorimetric Detection", DeGrandpre, Analytical Chemistry, volume 65, pages 331-337, 1993). In the extant art embodying such flow-through sensors, the tip of the optical fiber is typically located at a first end of a cylindrical chamber, and a reflector is disposed at the opposite end of the chamber. Provision is made for the continuous introduction of a suitable reagent and its withdrawal via conduits which are in fluid communication with the chamber and, typically, oriented in parallel with the optical fiber. The chamber will in part be permeable to the analyte of interest. The analyte thus permeates through a chamber wall and reacts with the reagent thereby producing a change that can be optically monitored. The rate of reagent flow governs the attainable sensitivity, i.e., sensitivity increases with decreasing flow, while response time decreases with increasing flow. In the reflectance mode, as described above, the effective path length is twice the distance between the fiber tip and the oppositely disposed reflector. The sensor can also be configured with a transmitting fiber at one end of the chamber and an oppositely disposed receiving fiber whereby the path length essentially becomes the length of the chamber. In either case, limited pathlengths are generally attainable, due to severe light loss, and maximum achievable sensitivity is very limited. Collection of analytes into a reagent flowing through a permeable membrane is well known in the art. The collected analyte is typically measured colorimetrically or fluorometrically in a system external and separate from the collector with or without further reagent addition and reaction. If a sufficient membrane area is provided for analyte collection, parts per trillion levels of analytes can be detected in favorable cases. (See, e.g., "Determination of Gaseous Hydrogen Peroxide at Parts per Trillion Levels with a Nafion membrane Diffusion Scrubber and a Single-Une Flow-Injection System", Dasgupta et al, Analytica Chimica Acta, Volume 260, pages 57-64, 1992; and "Measurement of Atmospheric Ammonia", Dasgupta et al, Environmental Science and Technology, Volume 23, pages 1467-1474, 1989). The sensitivity of a renewable-reagent fiber optic sensor employing this mode of analyte collection would be expected by those skilled in the art to be very low because the length of the membrane that can be used is constrained by the light loss through the membrane. A renewable reagent liquid core waveguide chemical sensor which uses a membrane material as both the sampling and waveguiding component has been reported. (See, e.g., "Liquid Core Waveguides for Chemical Sensing", Hong and Burgess, Proceedings SPIE, Vol. 2293, pgs. 71 - 79, 1994). This paper proposes a liquid core waveguide comprised of then available permeable polymers, i.e., PTFE and FEP. Such waveguides, however, have very limited utility because their refractive indexes are greater than that of water, i.e., exceed 1.33, and because they are not optically clear and thus can conduct light for only a short distance. Further, while being somewhat permeable to gases, such polymers do not have sufficient permeability to function as a sensor probe with significant commercial applicability. In the use of such waveguides, it is necessary to incorporate ethylene glycol or some other non-aqueous solvent(s) in the liquid core, to raise the refractive index of the core above that of the containment tube, and this further limits utility. The paper discussed immediately above also discussed the use of Teflon A.F. as an internal coating on a porous polyethylene hollow support fiber, the thickness of the coating being on the order of 1 µm. The resulting tube was filled with an acid-base indicator and reportedly responded to relatively high concentrations of ammonia gas (statically deployed in the vapor space over a 0.01 M solution of ammonia in a 50 mL capacity closed vessel) with a seemingly rapid response time (ca. 1 min). Coating the inside of a thin-walled porous fiber with the "AF" solution to produce an ultrathin layer of the latter polymer to produce a reliable or reproducible waveguide is not a commercially practical solution because, as is well known, "Teflon", including the AF variety, has very poor surface adhesion to most materials unless special adhesion promoters are used (see, e.g., P. Dress and H. Franke, "A Cylindrical Liquid-Core Waveguide", Applied Physics, Part B, Volume 63, pages 12 - 19, 1996). Further, as is well known, such surface promoters can compromise the structural integrity of the porous tubing used as the support for the layer. Also, it is impossible to produce uniform thicknesses of a polymer coating in the manner reported over any reasonable length of a tube and, especially, to produce such a coating in a reproducible manner from one batch to another. Further, such thin coatings cannot, on a practical basis, be produced without periodic occurrence of pinholes and this would make it impossible to use such tubing in in-vivo physiological applications or in any situation involving significant external pressure, e.g., for a situation in which a sensor is to be immersed in the depths of the ocean. In the latter case, the high collapsibility of supporting porous membrane tubes when pressure is applied from the outside will also compromise the structural integrity of such a sensor. Importantly, the data provided by Hong and Burgess for the response speed of their "Teflon AF" coated tube teaches away from the use of a polymeric tube solely composed of "Teflon AF", rather than a bilayer structure involving a porous support structure and a "Teflon AF" adlayer. This is because the response time in the Hong-Burgess design is solely due to the permeation through the 1 µm thick "Teflon AF" layer, i.e, the transport in the support structure occurs through the free pore space in a microsecond time scale (the characteristic diffusion time of ammonia, a gas with a diffusion coefficient of 0.25 cm 2 /s, through a 55 µm deep (see Hong and Burgess, page 78) air-filled pore is only 120 msec. Accordingly, the ∼1 min response time for a device having a 1µm thick layer, as seen in Figure 9 of Hong and Burgess, is actually not fast but very slow when the thickness is taken into account. It is well known that the characteristic time (loosely, response time for transport) for diffusive or permeative transport across a polymer wall varies directly with the square of the thickness of the polymer wall and Inversely with the diffusion coefficient of the analyte of interest through the polymer. The diffusion coefficient remains constant for a given analyte and polymer and thus the response time Increases with the square of the thickness (see, e.g., Dasgupta, P.K., "A Diffusion Scrubber for the Collection of Atmospheric Gases", Atmospheric Environment, Volume 18, pages 1593 - 1599, 1984). Hong and Burgess's own data on PTFE membranes (page 78) show the same behavior. The response time for ammonia decreases by a factor of ∼4 as the membrane thickness is reduced by a factor of two (from 150 to 84 µm). Accordingly, if a polymer of ~1 µm thickness produces a response time ∼1 min (and this for ammonia, a relatively low molecular weight, small, fast diffusing molecule), the response time for a 75 µm thick tube would be expected to be 5,625 minutes, i.e., close to 4 days, if one were to follow the teachings of Hong and Burgess. A "Teflon AF" tube having a wall thickness significantly less than 75 µm would not have sufficient rigidity to be employed as a sensor probe. According to the present invention there is provided a method as claimed in claim 1 and apparatus as claimed in claim 25. The present invention overcomes the above-briefly discussed and other deficiencies and disadvantages of the prior art by providing, novel and improved optical analyses techniques. The present invention thus encompasses novel methods by which chemical substances of interest may be detected and/or measured using optical means. The present invention exploits two properties unique to a special kind of polymer membrane which has the following important properties: 1) the membrane structure is permeable to gases, vapors and certain chemical substances dissolved in a liquid matrix, 2) the membrane consists of a polymer material which is amorphous, optically clear and has a refractive index which is less than 1.33, and 3) the membrane can be formed into various self-supporting cylindrical shapes which, when filled with liquid, may function as an optical waveguide. The inside of the waveguide will be filled with a light conducting liquid. Also, any of a wide range of well known chemical solutions whose optical properties are modified when exposed to permeant gases or vapors can be dissolved in the waveguide filling fluid. In the practice of the invention to sense and measure chemical substances of interest, the exterior surface of the permeable waveguide is exposed to an environment in which the substance(s) may be present In the gas or vapor phase or may be dissolved or dispersed in a liquid. Light is "shown", by various means, in the interior of the polymer waveguide. The light leaving the waveguide is then "measured". Light measuring techniques such as optical absorption (colorimetry), luminescence, fluorescence and Raman spectra can be used as modalities with which to characterize the substance(s) to be detected and measured. The invention thus employs a unique permeable liquid core waveguide wherein an appropriate light transmitting reagent forms the waveguide core. This permeable waveguide is fabricated from an optically clear amorphous polymer material having a lower refractive index than the flowing or stationary light transmitting reagent core liquid. A preferred material for use as the containment tube of a reagent core waveguide for practice of the invention is the copolymer of 2,2'-bis-trifluoromethyl-4,5 difluoro-1,3 dioxole (PDD) with tetrafluoroethylene (TFE) (TEFLON AF 2400). The reagent core liquid inside the waveguide contains or consists of a chemical indicator that will change its optical characteristics when the waveguide sensor is exposed to the analyte, the analyte diffusing through the highly permeable tube wall(s). The optical changes may, in accordance with the invention, be detected by one of the following techniques: UV/Vis absorption, fluorescence, chemiluminescence, or Raman spectrometry. The design flexibility of a combined liquid core optical waveguide/gas or vapor sensor as described above for use in the practice of the invention allows a broad spectrum of uses, i.e., the sensor may be embodied in a probe having a length of a few millimeters to a few meters depending on the application and the sensitivity requirements. A short length waveguide is particularly well suited for applications that require a small sensor such as, for example, in-vivo biological sensors. The longer waveguide lengths will permit greater sensitivity or faster response times and may be particularly useful in environmental measurements. The sensitivity of a combined liquid core optical waveguide/gas or vapor sensor as described above may be enhanced by maximizing the collection of emitted light and/or the quantity of analyte to which the reagent is exposed per unit of time. Various embodiments of the present invention will now be described by way of example only, and with reference to the accompanying drawings in which: Figure 1 is a schematic illustration of a first embodiment of a flow-through sensor for use in the practice of the invention; Figure 2 is a schematic showing of a modified version of sensor of Figure 1; Figure 3 schematically shows the practice of a sensing technique in accordance with the invention. Figures 4A and 4B are respectively schematic top and side elevational views of apparatus in accordance with a second embodiment of the present invention; and Figure 5 schematically illustrates a third embodiment of the present invention, the apparatus of Figure 5 being operable in an analysis or control process. The invention employs a liquid core waveguide as the main body, i.e., the probe, of a sensor. Referring to Figure 1, a liquid core waveguide having properties which enable its use in the Invention is indicated generally at 10. Waveguide 10 comprises a substantially optically transparent liquid core region 12 surrounded by a material, i.e., a tube 14, having a lower refractive index (relevant to the wavelength range of light used) than the liquid material 12' comprising the core. Light will propagate inside the waveguide with negligible losses due to the total internal reflection at the surface of the lower refractive index material provided that the launching angle of the light into the core is within the acceptance angle of the material comprising tube 14. In practice, as schematically illustrated in Figure 1, the sensor probe is coupled to a light source 16 which illuminates the core liquid 12' via a solid optical fiber 18, or bundle of such fibers. Light exits the waveguide at the end opposite to fiber 18 and is collected by an optical fiber(s) 20. Optical fiber(s) 20 deliver the collected light to an analysis instrument 22. Figure 1 illustrates a "flow-through" technique wherein the core liquid 12', i.e., the indicator reagent, is delivered to the core region of the waveguide sensor via a supply conduit 24 and exits the core region via a discharge conduit 26. In a stationary, i.e., non-flowing, reagent embodiment, one of conduits 24 or 26 would be used to fill the core region of the waveguide with the reagent, after which the conduit would be capped, and the other conduit would be omitted. The wall material of tube 14 must meet certain basic requirements. Firstly, it has to be permeable to the analyte and it must have a refractive index that is lower than that of the reagent, i.e., the core liquid 12'. Secondly, it must be optically clear. Thirdly, it must be relatively rigid so that, if the use dictates, the probe will be self-supporting. A preferred waveguide defining material is TEFLON AF 2400 which is the copolymer of PDD with TFE. It has recently been learned how to extrude PDD-TFE in the form of tubing having a wall thickness of 75 µm. The tubing 14 has several important functions. Firstly, it forms a total reflection layer to entrap light, injected via fiber 18, inside the tube 14 so as to form a light waveguide. To form a liquid-core light waveguide, the tubing must define an outer layer with a refractive index which is lower than that of the liquid core. Since the copolymers of PDD with TFE have a refractive index in the range of 1.29 to 1.31, i.e., a refractive index which is lower than water and most organic solvents, almost any liquid can be used as the core liquid in a TEFLON AF 2400 tube. The waveguide action will significantly increase the signal-to-noise ratio of the analysis technique when compared to the prior art. This increase in sensitivity, in turn, allows the choice of a detection mode that will reduce the cost of detection. When UV/Vis absorption spectroscopy is used as the detection method, the waveguide action of the reagent-filled part of the sensor helps maintain high light throughput to the receiving fiber 20, making possible a long length and a large surface area for Influx of the analyte, in the manner to be described below, into the sensor. In the absence of large light losses, the slgnal-to-noise ratio is linearly related to the amount of analyte transported into the sensor. In the prior art, the light pathlength of the sensor has typically been only 1 mm long because of the Inherent dlfficulty in keeping he light throughput for a longer path. In the practice of the present invention, a one meter long waveguide can be easily used, resulting in a signal-to-noise ratio improvement of three orders of magnitude over a sensor with 1-mm length, with a proportionate improvement in the limit of detection. When fluorescence, Raman, or chemiluminescence spectroscopy is used as the detection technique in instrument 22, the waveguide will enhance the signal by the integrating light signal, i.e., the additive effect which occurs along the waveguide. As will be obvious to those skilled in the art, when chemiluminescence is the detection modality, light injection via fiber 18 is not required. The tubing 14 must also reduce interference caused by the effects of ambient light on the sensor. This result is accomplished because the optically clear, low refractive index tubing wall not only functions as a total reflection layer to keep the transmitted analysis light inside the waveguide, but it also substantially prevents ambient light from propagating through the lumen of the waveguide. Restated, any ambient light that is within the acceptance angle of the receiving fiber 20 will also be within the "total rejection angle" of the tubing 14. Therefore, although the tubing behaves like a mirror to internal light, it appears transparent to ambient light. Accordingly, ambient light is "rejected" while the internal guidance of analysis light and/or Internally generated light is enhanced. A further reason of the relative immunity of the liquid-core guide sensor of the invention to the deleterious effects of ambient light is its high throughput of internal light which makes penetration of a fixed amount of ambient light less important. The thin walled tube 14 must additionally function as an efficient analyte permeable membrane. Not only does the PDD-TFE copolymer display the lowest refractive index of any polymer, whereby it may function as a liquid core waveguide when filled with almost any clear liquid, it is also much more gas permeable than other fluoropolymers. Published data indicate that TEFLON AF 2400, for example, is 230 times more permeable to CO 2 , O 2 and H 2 than polytetrafluoroethylene (PTFE). In the case of CO 2 , the permeability of TEFLON AF 2400 to CO 2 is 3900 Barrer. Indeed, the permeability of PDD-TFE copolymers is comparable to that of polydimethylsiloxane (see, e.g., "Gas and Vapor Transport Properties of Amorphous Perfluorinated Copolymer Membranes Based on 2,2-bis trifluoromethyl-4, 5-difluoro-1,3-dioxole/tetrafluoroethylene", Pinnau and Toy, Journal of Membrane Science, Volume 109, pages 125-133, 1996). In Figure 1, the migration of gas or vapor from the ambient environment to the core liquid through the permeable wall of tube 14 is indicated by "g". The PDD-TFE tubing 14 also has sufficient rigidity to provide mechanical support for the associated components of the sensor. The analyte flux into the sensor is not only linearly dependent on available membrane area, it is also dependent inversely on the thickness of the membrane. Most gas permeable membrane tubes, because they have to be very thin to obtain sufficient flux, are lacking in rigidity and cannot be used as the structural support of the sensor. Thus, for a waveguide of any significant length, additional means of mechanical support would normally be necessary. The PDD-TFE copolymer displays high mechanical strength and rigidity. A narrow bore tube 14 with 75 µm thick walls is strong enough for most biological applications. As noted above, the wall of polymeric tubing 14 provides containment for the reagent/core liquid 12'. Transport of the analyte through the tube wall, as noted, occurs by permeation. The process of permeation is governed by a combination of solubility in the polymer and diffusion through the polymer. For ionic constituents in a solution or other high molecular weight substances, the vapor pressure is very low and there is negligible loss of the internal constituents through the sensor wall. The present invention can be practiced in several modes. For example, the reagent inside the waveguide can be used in either a flowing or stationary manner. For a stable reagent that can be used in an equilibrium fashion, for example when sensing pCO 2 using a carbonate-bicarbonate buffer with an additional pH indicator, when the sensor is to be disposable or where long term usability is not an important consideration, the indicator reagent can be permanently sealed inside the waveguide. Such non-flowing sensors may be stored inside a sealed package to prevent contamination of the reagent inside the waveguide from ambient air between fabrication and use. Where a stationary reagent core is used, the Figure 1 sensor may be modified to permit the indicator reagent to be replaced or refurbished by including sealable liquid in/out caps, through which the waveguide can be filled with a fresh reagent, on one or both of conduits 24 and 26. For indicators that are chemically or photolytically unstable, the reagent will be continuously refreshed by using the waveguide essentially as a flow cell as represented by Figure 1. For many applications, the optimum mode may be the use of a stationary liquid core for a desired measurement period, to cumulatively build the maximum analyte concentration possible, followed by flushing and recharging the core at the end of that measurement period to ready the sensor for a new measurement. The above-described liquid core waveguide can also be used in combination with another membrane that collects the analyte, followed by one or more sequential reagent additions and reactions. Those skilled in the art will perceive that plural analyte collection step could be sequentially carried out with the liquid core of the waveguide of Figure 1 forming the final reaction zone. A further mode of practice of the present invention, is to employ a solvent in which the gas specie of interest will dissolve in the core liquid of the permeable waveguide. Since the liquid core waveguide is a very sensitive detector, many permeated analytes can be detected directly by the spectral signature characteristic of the analyte gas itself, dissolved in a suitable liquid, without any reaction with an indicator reagent. For example, most of the volatile organic compounds have a strong absorbence band in the UV range. With a one meter long flow cell, such compounds can be detected at a concentration of ten (10) nanomolar. With the use of Raman spectroscopy as the detection mode, it Is possible to differentiate between a variety of analytes and simultaneously measure them, although there will be some sacrifice in sensitivity relative to UV/Vls absorbence detection. Figure 2 depicts an alternative sensor probe for use In practice of the present invention. The sensor of Figure 2 employs a gas and vapor permeable tube 32 as a liquid core optical waveguide 30. A suitable reagent is delivered Into tube 32 via a conduit 34 which is arranged to have Its discharge end located adjacent the distal end of waveguide 30. When the Figure 2 sensor is operated in the flow-through mode, the reagent will exit waveguide 30 via a discharge conduit 36. Analysis light is launched into the proximal end of the waveguide core region via an optical fiber(s) 38. Light transmitted down the waveguide core is reflected at the distal end thereof by a mirror 40. Fiber(s) 38 thus function as both the analysis light launching and collection modality. The manner in which this is accomplished may, for example, be as explained in the description of Figure 2 of U.S. Patent 5,444,807, which further discloses the use of a waveguide consisting of a material having a refractive index which is less than 1.33. Obviously, the pathlength for the light In the sensor of Figure 2 is essentially twice the length of tube 32. The following are illustrative examples of practice of the present invention. CO 2 Detection : CO 2 may be sensed by filling the waveguide with an aqueous carbonate-bicarbonate buffer solution containing a pH indicator that undergoes a spectral change around the pH of such a buffer solution. Suitable pH indicators are phenol red and bromthymol blue. Visible absorption spectroscopy is used for sensing. The concentration of CO 2 outside the sensor (whether it is dissolved CO 2 in water or ambient CO 2 in the gas phase) quickly reaches equilibrium with PCO 2 (partial pressure of CO 2 ) inside the sensor. The pH inside the sensor and hence the exact spectrum of the indicator depends on the pCO 2 level. All general considerations relevant to any other fiber optic based CO 2 sensors will apply (see, e.g., DeGrandpre, above). O 2 Detection: Oxygen may be sensed through utilization of both fluorometric and absorptiometric principles. Many fluorescent aromatic dye stuffs are known that are fluorescent and their fluorescence markedly decreases in the presence of oxygen due to Stem-Volmer Quenching. O 2 can be sensed using a solution of an oxygen-quenchable fluorescent dye inside the liquid waveguide. Inexpensive and highly sensitive absorptiometric oxygen sensing can be accomplished by filling the liquid core waveguide with a solution/suspension of leuco-methylene blue. This colorless dye substrate is readily oxidized by oxygen to form methylene blue which can be monitored by the emission from a red light emitting diode (LED). Other reagents such as ammoniacal cuprous chloride or chromous chloride (Chromium(II) chloride) which readily absorb oxygen to form highly colored products can also be used in the absorptiometric mode. CO Detection: It is known that an alkaline solution of silver p -sulfoaminobenzoate or a solution of potassium tetrachloropaladate(II) readily absorbs CO and respectively form silver or palladium in a colloidal form that can be monitored by optical absorption measurement around 400 nm. Such solutions can be readily used for making a liquid core waveguide sensor for CO. H 2 S Detection : Hydrogen sulfide is readily absorbed by an alkaline solution of sodium nitroprusside to from an intense purple color that can be monitored by emission from a green or yellow light emitting diode (LED) (see, e.g., "Nitroprusside and Methylene Blue Methods for Silicone Membrane Differentiated Flow-Injection Determination of Sulfide in Water and Wastewater", Kuban et al, Analytical Chemistry, Volume 64, pages 36-43, 1992). This can form the basis of a highly sensitive and selective method for the measurement of H 2 S in ambient air and wastewater with an LED and a liquid core waveguide. NO 2 Detection: Nitrogen Dioxide forms an intensely purple dye that can be monitored with a green LED upon reaction with Griess-Saltzman reagent (sulfanilic acid or sulfanilamide with 1-naphthylethylenediamine hydrochloride in a dilute acetic acid medium). Accordingly, by filling a liquid core waveguide with this reagent, NO 2 and/or nitrous acid may be selectively sensed. NO 2 can also be sensed in the lumionometric mode when a solution of luminol and sulfite is used in the waveguide, this reaction selectively producing chemiluminescence with luminol. NH 3 Detection: High levels of ammonia can be monitored, employing the above-described principles of the CO 2 sensor, using an NH 3 -NH 4 Cl buffer solution and an appropriate pH indicator and visible absorbence detection. Much lower levels of ammonia can be monitored using a system in which the ammonia is captured in a phenol-sodium nitroprusside solution followed by two sequential reactions, I.e., (a) with alkaline EDTA and then (b) with sodium hypochlorite. (see, e.g., "Electroosmotically Pumped Capillary Format Sequential Injection Analysis with a Membrane Sampling Interface for Gaseous Analytes", Liu and Dasgupta, Analytica Chimica Acta, Volume 308, pages 281-285, 1995). The color of the indophenol blue formed can be monitored with an orange-red LED emitting at 630 nm. An even more sensitive method consists also of a sequential reaction system and fluorometric sensing. In the latter technique, the ammonia is collected into an acidic receptor liquid and reacts with separately introduced solutions of o-phthalaldehyde and 2-mercaptoethanol (or sulfite) to form an intensely fluorescent isoindole. Ozone Detection : Ozone can be detected either in the luminometric or the absorptiometric mode using the liquid-core waveguide. A great variety of intensely fluorescent dyes, including Eosin or Rhodamine, are oxidized by ozone and the oxidation is accompanied by light emission. Ozone also selectively decolorizes indigo derivatives and this bleaching can be monitored with a LED-based detector (see, e.g., "Automated Measurement of Aqueous Ozone Concentration", Darby et al, Process Control and Quality, volume 6, pages 229-243, 1995). Either sensing mode can be used for the monitoring of ozone in ambient air or for process control applications in ozonation plants for the production of potable water. Hydrogen Peroxide Detection : Measurement of hydrogen peroxide has become Important because it is the sterilizing agent of choice in many bioreactor operations. Hydrogen peroxide can be determined luminometrically using alkaline luminol containing a catalyst such as potassium ferricyanide in the core of the waveguide, this reagent produces intense chemiluminescence when contacted with H 2 O 2 . Hydrogen peroxide can also be monitored fluorometrically by using an oxidizable phenolic substrate such as p-Cresol and a peroxidase enzyme or its suitable mimic such as an ammoniacal solution of bovine hematin in the core of the waveguide. The resulting product is intensely fluorescent. Many colorimetric methods for measuring H 2 O 2 are also known in the art. Chlorine Detection : Chlorine is routinely monitored in water and air environments both in industry and by consumers. Chlorine reacts selectively with o-tolidine or tetramethylbenzidine in solution to form intensely yellow products that can be monitored by filling such a solution inside a liquid core waveguide and using a blue LED as the source for absorptiometric measurements. Concentrated Acid Detection : The measurement of concentrated acids is an important problem in many industries. In the nuclear material processing industry, concentrated HNO 3 and HCI solutions are frequently used and it is important to measure the acidity in such media. This cannot be accomplished with simple pH sensing. Renewable reagent fiber optic based sensors have been used to address the problem using ion permeable membranes but there are difficulties due to the permeability dependence of such membranes on the presence of other membranes (see e.g., "A Renewable-Reagent Fiber-Optic Sensor for Measurement of High Acidities", Kuhn and Dyke, Analytical Chemistry, Volume 68, pages 2890-2894, 1996). Molecular HNO 3 and HCI can permeate through PDD-TFE and thus the use of a liquid core waveguide with a buffered Indicator solution inside offers an ideal solution to this problem. Detection of Organic Compounds in Water: The foregoing examples have served to show that the analytes that can be detected/identified through practice of the present invention can be in the gas phase or the solution phase. The only criterion that determines the applicability of the invention is sufficient permeability of the target analyte through the waveguide defining membrane. Thus, the present invention has applicability to the determination of dissolved organics in water whether these are present in trace amounts or in larger concentrations as occur in leakage of organic solvents or fuel from underground storage/disposal facilities into groundwater. In many cases, it will be possible to provide an organic solvent that is transparent in the near infrared (NIR) spectroscopy range or substantially into the UV range as the core of the waveguide which will collect the contaminants from water and on which direct NIR or UV spectroscopy can be carried out. In a second mode, specific reactions can be carried out with many organic compounds to yield products that are easily optically detectable. Intensely colored products are formed from halocarbons (contamination of ground water for example by chlorinated hydrocarbons is of considerable concern) by the Fujiwara reaction. A reaction based fiber optic sensor has already been reported for this purpose (see, e.g., "Multicomponent Determination of Chlorinated Hydrocarbons Using a Reaction-Based Chemical Sensor. 1. Multivariate Calibration of Fujiwara Reaction Products", Henshaw et al, Analytical Chemistry, Volume 66, pages 3328-3334, 1994). The same reaction approach can be directly adapted to the present liquid core waveguide sensor with far greater sensitivity. In the above discussion, it is implicit that laser and other light sources such as tungsten lamps, LEDs, mercury arc and others will be used as light sources for fluorescence and absorption measurement of the indicator fluid. A laser light source can be used in the present invention as means to generate Raman light spectra. Raman spectra have the particular advantage that molecules in the indicator fluid can exhibit unique "signature" spectra; thus enabling the separate analysis of specific molecules within a multl-molecular mixture in the fluid. The unique benefits of Raman spectroscopy within a liquid filled waveguide have been described In U.S. Patent 5,604,587. Figure 3 discloses an embodiment of the present Invention which employs a helical coil of permeable polymer tubing 50 mounted In a larger cylindrical housing 52 having a mouthpiece 54 at one end. A human subject will respire through the mouthpiece. His/her respiratory gases pass over the helical coil structure and exit via the opposite open end 55 of housing 52. The helical coiled shape of tubing 50 assures that a large length of the liquid reagent core waveguide formed thereby will be exposed to respired gases within the relatively small volume of the breath-through housing 52. The surface area of the permeable waveguide within the containment cylinder is thus maximized and, accordingly, the sensitivity of the probe that will be exposed to the transient gases of interest is also maximized. Additionally, as will be discussed further below in the description of Figure 5, judicious selection of the internal volume of housing 52 and the size of the gas discharge opening 55 will further increase sensitivity by establishing a pressure differential across the tubing to thereby enhance the rate of gas permeation through the tube. The ends of the helical coil exit the housing 52 via small holes 56 which are sealed with an appropriate adhesive. Excitation light and core fluid are delivered to the proximal end 58 of the helical coil. The exit point for both the core fluid and the attenuated light signal is indicated at 60. When the above-described novel sensing technique relies upon the detection of light generated by either fluorescence or chemiluminescence, the method and apparatus of the present invention provides a significant increase in sensitivity. Light generated by either fluorescence or chemiluminescence is scattered in all directions and, accordingly, only a small fraction of the total light generated is propagated along the interior of the liquid filled waveguide. Referring to Figure 4, a further embodiment of apparatus for use in the practice of the comprises a vessel 70 in which a liquid core waveguide 72 Is disposed. In this embodiment, the tubing comprising waveguide 72 is wound into a coll having the form of a flat spiral which essentially defines a plane. The flat spiral configuration of waveguide 72 compacts the length of the waveguide into a small volume. A specimen to be analyzed is introduced to vessel 70 at Inlet port 74 and will exit the vessel at a discharge port 76. The reagent/core liquid will be Introduced to waveguide 72 at Inlet 78 and will be discharged from the waveguide at outlet 80. Considering the above-discussed example of an ozone detector, the reagent delivered to the waveguide via inlet 78 would be a fluorescent dye such as Eison or Rhodamine. The ozone containing gas will be introduced to vessel 70 via inlet port 74. Light will be emitted as a result of the stimulation, by injected light, of the product of oxidation of the dye by ozone which has permeated through the wall of waveguide 72. The emitted light will be efficiently detected by a pair of planar photocell arrays 82 and 84. Alternatively, one of the photocell arrays may be replaced with a flat mirror. The apparatus of Figure 4 may, by additionally sensing light transmitted through the waveguide, be employed for simultaneous absorption and fluorescent detection of independent gas species. When the Figure 4 apparatus is employed to detect chemiluminescence, obviously a source of stimulation light is not required. Figure 5 schematically represents another way of enhancing the sensitivity of the techniques of the present invention. As depicted in Figure 5, the waveguide 10 of Figure 1 is disposed within a housing 86 which may, in the manner to be described below, be pressurized. In the apparatus of Figure 5, a specimen gas is delivered to the interior of container 86 by means of a pump 88 disposed in an Inlet duct 90. The discharge conduit 92 for the specimen gas will be provided with a valve 94 which will be controllable. The pump 88 and valve 94 allows the pressure of the specimen gas about the exterior of the waveguide tube 14 to be controlled to a desired level above atmospheric pressure. This ability to increase the ambient pressure results in a very considerable increase in sensitivity by increasing the concentration of the specie of interest and, thereby, increasing the permeation of the gas specie through the wall of tube 14 through increasing the pressure gradient across the wall of tube 14. Continuing to refer to Figure 5, the disclosed embodiment of the invention may be employed as an in-line monitor for control purposes. For example, it may be desired to achieve control over the amount of a particular gas dissolved in a core liquid 12' which is pumped through tube 14 by means of a pump 96, the flow of the liquid 12' also being controlled by means of a valve 98. Through exercise of control over pumps 88 and 96 and valves 94 and 98, the pressure difference between the interior of housing 86 and the interior of tube 14 can be varied in such a manner as to cause gases to move into or out of the core liquid 12'. The detection modality, as described above in the discussion of Figure 1, will then be employed to monitor and control the concentration of the gas of interest in the core liquid 12'. While preferred embodiments have been described, various modifications and substitutions may be made thereto. Accordingly, it is understood that the present invention has been described by way of illustration and not limitation.

Claims: A method for optical detection of chemical substances comprising: forming a self supporting tubular member (14, 32, 50, 72), said tubular member defining a hollow axial core region (12), said tubular member consisting of an optically clear material which is gas and vapor permeable and liquid impervious, said material having a refractive index which is less than 1.33; filling the core region of the tubular member with a light transmitting liquid reagent having an index of refraction which exceeds that of said material comprising said tubular member whereby said tubular member may function as a liquid core optical waveguide (10), said liquid undergoing a change in an optical characteristic thereof upon exposure to a chemical substance of interest which has diffused through said tubular member; passing light through the liquid reagent; receiving light which has passed through the liquid reagent; and detecting a change in an optical characteristic of the liquid reagent by analyzing the received light. The method of claim 1 wherein the step of passing comprises: injecting analysis light into the core region (12) of the tubular member(14) at an end thereof, the injected light being guided by the tubular member whereby the analysis light travels through the liquid reagent. The method of claim 1 or 2 wherein the step of detecting comprises sensing fluorescence of said reagent. The method of claim 1 or 2 wherein the step of detecting at least in part comprises sensing luminescence of said reagent. The method of claim 2 wherein the step of detecting comprises sensing analysis light which is not absorbed by passage through the liquid reagent in the core region (12) of the tubular member (14). The method of claim 2 or 5 wherein the step of passing comprises directly coupling an optical fiber (18) to the core region and launching analysis light into the core region (12) with a launching angle that is within the acceptance angle of the liquid core optical waveguide (10). The method of claims 1 to 6 wherein said tubular member (14) includes a wall having a thickness of about 75 micrometers. The method of claims 1 to 8 wherein said tubular member (14) consists of a PDD-TFE copolymer. The method of claim 1 or 2 wherein the step of detecting comprises measuring the Raman spectra of the liquid reagent. The method of claim 1 or 2 wherein the step of detecting comprises measuring the absorption of the transmitted analysis light by the liquid reagent. The method of claim 1 further comprising the step of controlling the pressure of the ambient environment to thereby influence the rate of permeation of the chemical substance of interest through the tubular member (14, 50, 72). The method of claim 11 further comprising the step of transmitting analysis light into the core region (12) with a launching angle which is within the acceptance angle of the liquid core optical waveguide (10), and wherein the step of detecting comprises receiving light which has passed through the liquid reagent and detecting a change in an optical characteristic of the liquid reagent by analyzing the received light. The method of claim 12 wherein the step of controlling pressure comprises: placing the tubular member (50, 72) within an enclosure (52, 86), the interior of the enclosure defining the ambient environment; and varying the enclosure interior pressure to thereby vary the gradient between the liquid reagent pressure and the enclosure interior pressure. The method of claim 13 wherein the step of varying pressure comprises exercising control over the enclosure interior pressure to establish a desired pressure in the enclosure (52, 86). The method of claim 14 wherein the step of placing the tubular member (50, 72) within an enclosure (52, 86) comprises placing the tubular member within a closed chamber, the chamber interior being isolated from the environment surrounding the enclosure. The method of claim 13 wherein the step of placing the tubular member (50) within an enclosure comprises positioning the tubular member (56) within a breathing tube (52), the tube having a mouthpiece (54) on a first end and a restricted discharge opening (55) displaced from the mouthpiece, gas delivered to the tube interior via the mouthpiece flowing over the tubular member to reach the discharge opening. The method of claim 13 wherein the step of detecting comprises measuring the absorption of the transmitted analysis light by the liquid reagent. The method of claim 13 wherein the step of detecting comprises measuring the fluorescence which occurs in the liquid reagent. The method of claim 13 wherein the step of detecting comprises measuring the luminescence of the liquid reagent. The method of claim 13 wherein the step of detecting comprises measuring the Raman spectra of the liquid reagent. The method of claim 13 further comprising forming a portion of the tubular member (72) into a spiral configuration prior to the filling thereof. Apparatus for use in the optical detection of chemical species in the gas or vapor phase comprising: a rigid, self-supporting tubular optical waveguide (10), said tubular waveguide consisting of an optically clear amorphous polymer having a refractive index of less than 1.33, said tubular waveguide being impermeable to liquid and being permeable to gas and vapor; a liquid reagent disposed in the core region (12) of said tubular optical waveguide, said reagent having an index of refraction which exceeds the refractive index of said polymer, said reagent being light conducting and being characterized by an optical property which is modified when exposed to a chemical specie of interest in the gas or vapor phase; an enclosure (52, 70, 86), said enclosure defining a chamber sized and shaped to receive at least a sensor portion of said optical waveguide, said enclosure having gas inlet and outlet ports (54, 55, 74, 76, 90, 92) whereby a pressurized specimen in gaseous form may be delivered into said chamber; a light source (16) coupled to a first end of said waveguide for transmitting analysis light into the reagent confined within the waveguide core region with a launching angle which is within the acceptance angle of the waveguide; and means (22) for monitoring a change in an optical characteristic of the reagent which occurs upon permeation of the chemical specie of interest through the wall of the waveguide. The apparatus of claim 22 wherein said enclosure includes means (88) for causing the pressure of the specimen in the chamber to exceed the ambient pressure at the exterior of the enclosure. The apparatus of claim 23 wherein said monitoring means comprises a receiver positioned to detect light which is passed through the core liquid for a distance which is at least equal to the length of the waveguide. The apparatus of claim 24 wherein said waveguide is formed into a coil (72) to increase the surface area thereof disposed within said chamber. The apparatus of claim 25 wherein said coiled waveguide is in the form of a flat spiral which defines a plane and wherein said monitoring means comprises at least a first planar array of photocells (82), said array being disposed within said chamber and in substantially parallel relationship to said waveguide defined plane. The apparatus of claim 23. wherein said waveguide is formed into a coil (50) and wherein said enclosure comprises a breathing tube having a mouthpiece (54) at a first end thereof. The apparatus of claims 22 to 27, wherein said waveguide includes a copolymer of PDD with TFE.

Inventors: DASGUPTA PURNENDU K, FEIN HARRY, LIU SU YI, DASGUPTA, PURNENDU K., FEIN, HARRY, LIU, SU YI
Applicants: WORLD PREC INSTR INC, WORLD PRECISION INSTRUMENTS, INC.
Application year: 1998
Main classification: G01N21
IPC codes: G01N21, G02B6