CA1169747A - Gaseous contaminant dosimeter - Google Patents
Gaseous contaminant dosimeterInfo
- Publication number
- CA1169747A CA1169747A CA000379830A CA379830A CA1169747A CA 1169747 A CA1169747 A CA 1169747A CA 000379830 A CA000379830 A CA 000379830A CA 379830 A CA379830 A CA 379830A CA 1169747 A CA1169747 A CA 1169747A
- Authority
- CA
- Canada
- Prior art keywords
- dosimeter
- receptacle
- channels
- gaseous contaminant
- interior
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
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Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N1/00—Sampling; Preparing specimens for investigation
- G01N1/02—Devices for withdrawing samples
- G01N1/22—Devices for withdrawing samples in the gaseous state
- G01N1/2273—Atmospheric sampling
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N1/00—Sampling; Preparing specimens for investigation
- G01N1/02—Devices for withdrawing samples
- G01N1/22—Devices for withdrawing samples in the gaseous state
- G01N1/2273—Atmospheric sampling
- G01N2001/2276—Personal monitors
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- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Physics & Mathematics (AREA)
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Biomedical Technology (AREA)
- Molecular Biology (AREA)
- Engineering & Computer Science (AREA)
- Measurement Of Radiation (AREA)
- Sampling And Sample Adjustment (AREA)
Abstract
ABSTRACT OF THE DISCLOSURE
A personal dosimeter for collecting a quantity of a gaseous contaminant in proportion to its average ambient concentration over the time of collection is provided. The dosimeter consists essentially of a closed receptacle containing a gas-collection medium, a channel-containing diffusion device forming a part of the boundary of the receptacle and a porous, hydrophobic film in contact with the interior side of the barrier.
A personal dosimeter for collecting a quantity of a gaseous contaminant in proportion to its average ambient concentration over the time of collection is provided. The dosimeter consists essentially of a closed receptacle containing a gas-collection medium, a channel-containing diffusion device forming a part of the boundary of the receptacle and a porous, hydrophobic film in contact with the interior side of the barrier.
Description
~L~9~7~7 TIT~E
Gaseous Contaminant Dosimeter BACKGROUWD OF THE INVENTION
__ _ _ Field of the Invention ; This invention is related to a personal dosimeter for registering gaseous contaminants in the atmosphere. More particularly, it is related to a dosimeter capable of collecting a quantity of con-taminant in proportion to its average atmospheric concentration to aid in determining the integrated exposure level to the contaminant.
Description ôf The Prior Art In response to the increasing concern about the health of workers who are exposed to harmful pollutants in the air, it has become necessary to monitor the concentration of the air-borne contaminants.
One developm nt for this purpose involved a rather large air pump which would force air to be sampled through a filter, trapping particulate contami~ants.
This obviously is unavailing for the monitoring of gaseous contaminants and, even for particles, is not accurate to determine concentration of the particles in the sampled atmosphere.
Personal sampling devices which are worn by individual workers and which passively collect the contaminants have also been used. For example, a device which utilized the molecular diffusion of the gas to be monitored to collect the sample has been described in ~merican Industrial Hygiene Association Journal, Volume 34, pages 78-81 (1973).
This device and others like it, called impinging tubes, are often cumbersome to use since their design and delicate construction necessitate that they always be oriented properly to accurately sample the atmosphere and to prevent dislocation of the sampling 3~ 7 mechanisms within the tu~e.
Therefore, there remains a need for a personal dosimeter that simply but accurately collects gaseous contaminants in proportion to their average atmospheric concentration.
SUMMAR~ OF THE INVE~TION
According to the present invention, there is provided a personal dosimeter for collecting a gaseous contaminant in proportion to its average ambient concentration during the collection time where the dosimeter consists essentially of a closed receptacle;
a collecting medium for the gaseous contaminant within the receptacle;
a diffusion device, forming a part of the boundary of said receptacle, the device containing a plurality of through-and-through channels adapted for the gaseous contaminant to diffuse therethrough from the atmosphere to the interior of the receptacle, said channels each having a length-to-diameter ratio of at least 3 and said channels providing the only communication between the atmosphere and the interior of the receptacle; and a porous, hydrophobic, inert film covering the interior openings of said channels.
BRIEF DESCRIPTION OF THE DRAWINGS
Figure 1 is a magnified perspective view of a diffusion device usable in the present invention.
Figure 2 is a top view of a gaseous contaminant dosimeter utilizing the diffusion device of Figure 1.
Figure 3 is a partial perspective view of the dosimeter of Figure 2.
Figure 4 is an exploded view of another dosimeter of the present invention.
. .
~ ~,S~ 7 Figure 5 ls a cross-sectional view of the assembled dosimeter of Figure 4.
DETAILED DESCRIPTIOW OF T~E ~NVENTION
The dosimeters of this invention collect a gaseous contaminant in proportion to its average concentration in the atmosphere during the collection period and provide for the expedient determination of this concentration. This is achieved by passively sampling the gaseous contaminant in ambient air in proportion to its cor.centration therein by allowing the contaminant to diffuse into an interior portion of the dosimeter where it is maintained,by a collecting medium situated therein, until it is analyzed.
The collecting medium holds the gaseous contaminant or its ions in a form that is more readily analyzable than is the gaseous form. After collection, the medium is removed from the dosimeter and treated with appropriate reagents to product color, the intensity of wnich is dependent upon the amount of gaseous contaminant collected. The time-average ambient concentration can then be determined, as later explained, with a previously-calibrated colorimeter or spectrophotometer. Alternatively, the contaminant can be separated from the collecting medium and its quantity determined, for example, by gas chromatography wherein the results of the gas chromatography analysis have been previously calibrated against known time-average ambient concentrations of the contaminant. The preferred method of determination is colorimetric.
Generally, the collecting medium is a material that absorbs, adsorbs, reacts or otherwise combines with the gaseous contaminant being measured. Regard-less of the manner in which the medium interacts, 7~7 as above, with the contaminant, the quantity orstrength of the collecting medium in the dosimeter should be sufficient to interact completely wich the total quantity of gaseous contaminant which is anticipated to be collected. The collecting medium will often be specific to the particular gaseous contaminant being monitored. Examples, meant to be representative but not limiting, include aqueous solutions of oxidizing a~ents or triethanol amine to absorb nitrogen dioxide, solutions of potassium or sodium tetrachloromercurate to absorb sulfur dioxide, solutions of sulfuric or other acids to absorb ammonia, and distilled water or a solution of sodium bisulfite to absorb formaldehyde. Charcoal or powdered carbon of high surface area, powders of metals, or metal salts can be used to adsorb many other organic contaminants.
Methods for colorimetric analysis, for example, for sulfur dioxide, nitrogen dioxide, ammonia, or formaldehyde, in air, are described in National Institute for Occupational Safety and Health method numbers 160 (publication 121, 1975), 108 (publication 136, 1974), 205 (publication 121, 1975) and 125 (publication 136, 1974), respectively.
The techniques therein described are readily adaptable with respect to absorbing solution and color-forming reagents for use in connection with collection by the dosimeter of the present invention.
One preferred embodiment of the present invention is shown in Figures 2 and 3 and is des-cribed and can be formed as follows. A base sheet 3 of impermeable polymeric material is provided to form one side of the receptacle portion of the dosimeter. The sheet is preferably transparent and thermoplastic and can be made of polymers of olefin, 7~
halogenated polymers, polyesters, or ionomer resins.
Preferred materials are the ionomer resins shown in U.S. Patent No. 3,264,272 issued August 2, 1966 to R. W. Rees. They are the ionic copolymers of alpha-olefins and alpha, beta-ethylenically unsaturated carboxylic acids of 3-8 carbon a~oms having 10-90% of the carboxylic acid ~roups neutralized with metal ions.
The size of sheet 3 is not cri-tical but is preferably a size easily adaptable for use in a personal dosimeter which is to be worn or readily carried. The collecting medium is placed in tne central portion of sheet 3. When the medium is a liquid, this can be accomplished by first forming a depression in the central portion of the sheet by applying pressure thereto with an appropriate die, heated or otherwise. The depressed area of sheet 3 is the central portion of the interior, designated 5, of the dosimeter.
After the collecting medium has been placed on sheet 3, a second top-sheet 4 corresponding to sheet 3 in composition and substantially in size is placed over sheet 3. Heat and pressure are then applied to the three areas ~ to provide permanent, fluid-tight bonding at the three corresponding edges of sheets 3 and 4. Adhesives or other forms of bonding can also be used provided the bonds are permanent and fluid-tight and the adhesive is inert to the collecting medium.
An elongate gas diffusion device l llaving a plurality of through-and-through channels 2 is positioned parallel and proximate to the fourth, unbonded edge of base sheet 3 and parallel and flush with the fourth, unbonded edge of top sheet 4.
The open channels 2 of device 1 are thus oriented '7~
horizontally with respect to the plane of sheet 3 and perpendicularly with respect to the fourth edges of sheets 3 and 4. On the interior side 7 of device 1, covering the channel openings of this interior side, is a porous, hydrophobic film, described in more detail below. Diffusion device 1, thus placed between sheets 3 and ~, is bonded to the sheets by the application of heat and pressure or by use of adhesives which should be impermeable and chemically inert to the collecting medium.
The bond between diffusion device l and each of sheets 3 and 4 should be liquid-tight and air-tight, thus completely enclosing the interiox 5 of the receptacle formed by sheets 3 and 4. The relative positions of diffusion device l and sheets 7 and 8 are such that the channels 2 provide the only communication between the atmosphere and the interior 5 of the receptacle.
It is also possible to form the dosimeter of Figures 2 and 3 saving the placement of the collecting medium, when it is a liquid, for last.
In such a case, the dosimeter is otherwise formed as described above. The collecting medium can be placed by piercing top sheet 4 at an appropriate spot with a hypodermic needle and injecting a measured amount of the collecting medium into the interior. The hole made by the hypodermic needle can then be thermally sealed.
Diffusiondevice 1 allows the gaseous contaminant to diffuse through each of channels
Gaseous Contaminant Dosimeter BACKGROUWD OF THE INVENTION
__ _ _ Field of the Invention ; This invention is related to a personal dosimeter for registering gaseous contaminants in the atmosphere. More particularly, it is related to a dosimeter capable of collecting a quantity of con-taminant in proportion to its average atmospheric concentration to aid in determining the integrated exposure level to the contaminant.
Description ôf The Prior Art In response to the increasing concern about the health of workers who are exposed to harmful pollutants in the air, it has become necessary to monitor the concentration of the air-borne contaminants.
One developm nt for this purpose involved a rather large air pump which would force air to be sampled through a filter, trapping particulate contami~ants.
This obviously is unavailing for the monitoring of gaseous contaminants and, even for particles, is not accurate to determine concentration of the particles in the sampled atmosphere.
Personal sampling devices which are worn by individual workers and which passively collect the contaminants have also been used. For example, a device which utilized the molecular diffusion of the gas to be monitored to collect the sample has been described in ~merican Industrial Hygiene Association Journal, Volume 34, pages 78-81 (1973).
This device and others like it, called impinging tubes, are often cumbersome to use since their design and delicate construction necessitate that they always be oriented properly to accurately sample the atmosphere and to prevent dislocation of the sampling 3~ 7 mechanisms within the tu~e.
Therefore, there remains a need for a personal dosimeter that simply but accurately collects gaseous contaminants in proportion to their average atmospheric concentration.
SUMMAR~ OF THE INVE~TION
According to the present invention, there is provided a personal dosimeter for collecting a gaseous contaminant in proportion to its average ambient concentration during the collection time where the dosimeter consists essentially of a closed receptacle;
a collecting medium for the gaseous contaminant within the receptacle;
a diffusion device, forming a part of the boundary of said receptacle, the device containing a plurality of through-and-through channels adapted for the gaseous contaminant to diffuse therethrough from the atmosphere to the interior of the receptacle, said channels each having a length-to-diameter ratio of at least 3 and said channels providing the only communication between the atmosphere and the interior of the receptacle; and a porous, hydrophobic, inert film covering the interior openings of said channels.
BRIEF DESCRIPTION OF THE DRAWINGS
Figure 1 is a magnified perspective view of a diffusion device usable in the present invention.
Figure 2 is a top view of a gaseous contaminant dosimeter utilizing the diffusion device of Figure 1.
Figure 3 is a partial perspective view of the dosimeter of Figure 2.
Figure 4 is an exploded view of another dosimeter of the present invention.
. .
~ ~,S~ 7 Figure 5 ls a cross-sectional view of the assembled dosimeter of Figure 4.
DETAILED DESCRIPTIOW OF T~E ~NVENTION
The dosimeters of this invention collect a gaseous contaminant in proportion to its average concentration in the atmosphere during the collection period and provide for the expedient determination of this concentration. This is achieved by passively sampling the gaseous contaminant in ambient air in proportion to its cor.centration therein by allowing the contaminant to diffuse into an interior portion of the dosimeter where it is maintained,by a collecting medium situated therein, until it is analyzed.
The collecting medium holds the gaseous contaminant or its ions in a form that is more readily analyzable than is the gaseous form. After collection, the medium is removed from the dosimeter and treated with appropriate reagents to product color, the intensity of wnich is dependent upon the amount of gaseous contaminant collected. The time-average ambient concentration can then be determined, as later explained, with a previously-calibrated colorimeter or spectrophotometer. Alternatively, the contaminant can be separated from the collecting medium and its quantity determined, for example, by gas chromatography wherein the results of the gas chromatography analysis have been previously calibrated against known time-average ambient concentrations of the contaminant. The preferred method of determination is colorimetric.
Generally, the collecting medium is a material that absorbs, adsorbs, reacts or otherwise combines with the gaseous contaminant being measured. Regard-less of the manner in which the medium interacts, 7~7 as above, with the contaminant, the quantity orstrength of the collecting medium in the dosimeter should be sufficient to interact completely wich the total quantity of gaseous contaminant which is anticipated to be collected. The collecting medium will often be specific to the particular gaseous contaminant being monitored. Examples, meant to be representative but not limiting, include aqueous solutions of oxidizing a~ents or triethanol amine to absorb nitrogen dioxide, solutions of potassium or sodium tetrachloromercurate to absorb sulfur dioxide, solutions of sulfuric or other acids to absorb ammonia, and distilled water or a solution of sodium bisulfite to absorb formaldehyde. Charcoal or powdered carbon of high surface area, powders of metals, or metal salts can be used to adsorb many other organic contaminants.
Methods for colorimetric analysis, for example, for sulfur dioxide, nitrogen dioxide, ammonia, or formaldehyde, in air, are described in National Institute for Occupational Safety and Health method numbers 160 (publication 121, 1975), 108 (publication 136, 1974), 205 (publication 121, 1975) and 125 (publication 136, 1974), respectively.
The techniques therein described are readily adaptable with respect to absorbing solution and color-forming reagents for use in connection with collection by the dosimeter of the present invention.
One preferred embodiment of the present invention is shown in Figures 2 and 3 and is des-cribed and can be formed as follows. A base sheet 3 of impermeable polymeric material is provided to form one side of the receptacle portion of the dosimeter. The sheet is preferably transparent and thermoplastic and can be made of polymers of olefin, 7~
halogenated polymers, polyesters, or ionomer resins.
Preferred materials are the ionomer resins shown in U.S. Patent No. 3,264,272 issued August 2, 1966 to R. W. Rees. They are the ionic copolymers of alpha-olefins and alpha, beta-ethylenically unsaturated carboxylic acids of 3-8 carbon a~oms having 10-90% of the carboxylic acid ~roups neutralized with metal ions.
The size of sheet 3 is not cri-tical but is preferably a size easily adaptable for use in a personal dosimeter which is to be worn or readily carried. The collecting medium is placed in tne central portion of sheet 3. When the medium is a liquid, this can be accomplished by first forming a depression in the central portion of the sheet by applying pressure thereto with an appropriate die, heated or otherwise. The depressed area of sheet 3 is the central portion of the interior, designated 5, of the dosimeter.
After the collecting medium has been placed on sheet 3, a second top-sheet 4 corresponding to sheet 3 in composition and substantially in size is placed over sheet 3. Heat and pressure are then applied to the three areas ~ to provide permanent, fluid-tight bonding at the three corresponding edges of sheets 3 and 4. Adhesives or other forms of bonding can also be used provided the bonds are permanent and fluid-tight and the adhesive is inert to the collecting medium.
An elongate gas diffusion device l llaving a plurality of through-and-through channels 2 is positioned parallel and proximate to the fourth, unbonded edge of base sheet 3 and parallel and flush with the fourth, unbonded edge of top sheet 4.
The open channels 2 of device 1 are thus oriented '7~
horizontally with respect to the plane of sheet 3 and perpendicularly with respect to the fourth edges of sheets 3 and 4. On the interior side 7 of device 1, covering the channel openings of this interior side, is a porous, hydrophobic film, described in more detail below. Diffusion device 1, thus placed between sheets 3 and ~, is bonded to the sheets by the application of heat and pressure or by use of adhesives which should be impermeable and chemically inert to the collecting medium.
The bond between diffusion device l and each of sheets 3 and 4 should be liquid-tight and air-tight, thus completely enclosing the interiox 5 of the receptacle formed by sheets 3 and 4. The relative positions of diffusion device l and sheets 7 and 8 are such that the channels 2 provide the only communication between the atmosphere and the interior 5 of the receptacle.
It is also possible to form the dosimeter of Figures 2 and 3 saving the placement of the collecting medium, when it is a liquid, for last.
In such a case, the dosimeter is otherwise formed as described above. The collecting medium can be placed by piercing top sheet 4 at an appropriate spot with a hypodermic needle and injecting a measured amount of the collecting medium into the interior. The hole made by the hypodermic needle can then be thermally sealed.
Diffusiondevice 1 allows the gaseous contaminant to diffuse through each of channels
2 according to Fick's Law, which is expressed in relevant form as ~- 6 M = D-C t A/L
where M = quantity of gaseous contaminant transferred (mg) S D = diffusion coefficient of ~he gaseous ` contaminant through air (cm2/min) C = concentration of the contaminant in the atmosphere (mg/cm3) t = time of exposure (minutes) A = cross-sectional area of the channel ( cm2 ) L = distance in direction of diffusion, herein channel length (cm) Values of D for various gaseous contami-nants are readily available from the literature.
The purely diffusional nature of the transfer of the gaseous contaminant through the channels, at a rate in linear proportion to its atmospheric con-centration, provides the integrating character of the dosimeter.
Gas diffusion device 1 is preferably made from materials that are non-hygroscopic and both chemically and physically inert to the gaseous contaminant and to the collecting medium.
Examples are polyethylene, polypropylene, polymers or copolymers of tetrafluoroethylene and hexa-fluoropropylene, and stainless steel. The above-named polymers are preferred since they can be easily injection-molded.
As can be seen from Fick's Law, the number and diameter of the channels affect the quantity of gaseous contaminant collected since they affect the total cross-sectional area available for transfer. The quantity of contaminant collected is also inversely proportional to the length of . ' .
-7~7 the channels. Although these parameters are not necessarily critical to the integrating operation of the diffusion device, it has been found that when each of the channels has a length-to-diameter ratio of at least 3, preferably at least 4.5, the dosimeter attains the desired insensitivi~ to relative atmospheric motion caused by wind or move-ment of the wearer. It has further been found that the use of about 5-500 channels, preferably lO-100 channels,eaah having a diameter of about 50-1000 microns and a length of about 1.0-25.0 mm, preferably
where M = quantity of gaseous contaminant transferred (mg) S D = diffusion coefficient of ~he gaseous ` contaminant through air (cm2/min) C = concentration of the contaminant in the atmosphere (mg/cm3) t = time of exposure (minutes) A = cross-sectional area of the channel ( cm2 ) L = distance in direction of diffusion, herein channel length (cm) Values of D for various gaseous contami-nants are readily available from the literature.
The purely diffusional nature of the transfer of the gaseous contaminant through the channels, at a rate in linear proportion to its atmospheric con-centration, provides the integrating character of the dosimeter.
Gas diffusion device 1 is preferably made from materials that are non-hygroscopic and both chemically and physically inert to the gaseous contaminant and to the collecting medium.
Examples are polyethylene, polypropylene, polymers or copolymers of tetrafluoroethylene and hexa-fluoropropylene, and stainless steel. The above-named polymers are preferred since they can be easily injection-molded.
As can be seen from Fick's Law, the number and diameter of the channels affect the quantity of gaseous contaminant collected since they affect the total cross-sectional area available for transfer. The quantity of contaminant collected is also inversely proportional to the length of . ' .
-7~7 the channels. Although these parameters are not necessarily critical to the integrating operation of the diffusion device, it has been found that when each of the channels has a length-to-diameter ratio of at least 3, preferably at least 4.5, the dosimeter attains the desired insensitivi~ to relative atmospheric motion caused by wind or move-ment of the wearer. It has further been found that the use of about 5-500 channels, preferably lO-100 channels,eaah having a diameter of about 50-1000 microns and a length of about 1.0-25.0 mm, preferably
3.0-8.0 mm, provides a device that is su ficiently sensitive to low ambient contaminant concentrations but is still of a conveniently small size.
A porous, hydrophobic film of 15-1000 micron thickness is placed over the channel openings on the interior side 7 of diffusion device 1, the side communicating with the interior ~ o the dosimeter. The film can be made, for example, of polymers or copolymers of tetrafluoroethylene and hexafluoropropylene. The function of the film is to prevent the absorbing solution, if that form of collecting medium is used, from flowing into the channels of diffusion device 1 and to further reduce sensitivity to atmospheric motion. Accordingly, the porosity of the film and the size of its pores should be selected so that these functions are performed without interfering with the passage of the gaseous contaminant from the interior ends of the channels to the absorbing solution. That is, the diffusion of gaseous contaminant through this film should be significantly greater than the diffusion through the channels so that the overall rate of diffusion is essentially controlled only by the channels. It has been found that a film that is . 8 , 7~
50-80% porous with a pore size of 0.1-3.0 microns is sufficient for this purpose when channels as previously~described are used.
The diffusion device 1 of Figure 1 and the dosimeter of Figures 2 and 3 are an example of preferred embodiments of the present invention but the invention is not limited thereto The diffusion device, for example, can be in the shape of a plug sealed into the face of either sheet 3 or sheet 4.
Similarly, the receptacle of the dosimeter need not be pouch-like as hereinbefore decribed but, for example, could be in the form of a rigid cuvette.
Such an embodiment of the present invention is shown in Figures 4 and 5. With respect to these Figures, there is shown a personal dosimeter composed of a circular base cup 8 having cylindrical walls which define an open cavity 9. Base cup 8 is pro-vided with flange 13, having circular opening 14, which permits the assembled dosimeter to be fastened easily to a person's clothing. A friction-fitting circular cap ll tightly engages base cup 8 in a manner forming closure of cavity 9. Cap ll has a plurality of channels 12 of circular cross-section extending therethrough towards cavity 9. The channel-containing cap 11 functions as a gas diffusion device following Fick's Law and therefore the number, length, and diameter of channels 12 of cap 11 are selected as previously described for channels 2 of diffusion device l.
Cap ll and base cup 8 are preferably made from materials that are non-hygroscopic and both chemically and physically inert to the gaseous contaminant and to the collecting medium. The materials described for construction of diffusion device l are equally preferable for use in making 7~7 cap 11 and base cup 8.
A porous, hydrophobic,inert film 10 is placed over the channel openings on the interior face of cap 11. This film performs the same fun~tions as earlier described with respect to the dosimeter of Fig~res 2 and 3. Film 10 preferably is 15~1000 microns in thickness and has a porosity of 50-80% with a pore size of 0.1-3.0 microns. It is preferably made of polymers or copolymers of tetrafluoroethylene or hexafluoropropylene, although any hydrophobic, inert material of the above physical characteristics is sufficient.
In assembled form, the friction-fit between base cup 8 and cap 11 is liquid~tight and air-tight, thus completely enclosing cavity 9 of cup 8.
Channels 12 of cap 11 thus provide the only com-munication between the atmosphere and cavity 9 and the collecting medium therein. The collecting medium preferably completely fills cavity g and is retained therein, against seepage through channels 12, by film 10.
In use, a dosimeter of this invention is exposed to the air containing the gaseous contaminant for a period of time for which the average contaminant concentration is sought. When the collecting medium is an absorbing solution, for example, a measured amount of the solution is then withdrawn from thedosimeter by, for example~ a hypodermic syringe.
When the analysis is to be made photo-metrically, the withdrawn absorbing solution is mixed with appropriate color forming reagents which change the color of the absorbing solution. The intensity of color so formed is dependent upon the amount of gaseous contaminant collected. Although it is often desirable to have a self-contained dosimeter, as shown in U.S. Patent 4,208,371, in which the reagents are contained in the dosimeter ` 10 , ~
7~7 and no withdrawal of material is necessary, this is sometimes impractical. An example o this is where the reagents are highly acidic, as in the color-production for formaldehyde where the reagents are chromatropic acid and sulfuric acid. In such cases, it is difficult to package the reagents in a s~able and safe form, and the simple dosimeter of the present invention is well suited for these applications.
The dosimeter of this invention can be calibrated to give a direct relationship between colorimetric or spectrophotometric readings and average ambient concentration of the gaseous contaminant. This can be accomplished by follGwing a calibration procedure similar to that described in U.S. Patent 4,208,371. In such a procedure, several dosimeters are exposed over a given period of time to various known concentrations of a con-taminant for which calibration is sought. The dosimeters contain the same kinds and amounts of collecting medium. Spectrophotometric readings, for example, are determined or at least two dosimeters at each of several known concentrations, and a straight-line is plotted, using a least-squares analysis, through the data points thus obtained.
A porous, hydrophobic film of 15-1000 micron thickness is placed over the channel openings on the interior side 7 of diffusion device 1, the side communicating with the interior ~ o the dosimeter. The film can be made, for example, of polymers or copolymers of tetrafluoroethylene and hexafluoropropylene. The function of the film is to prevent the absorbing solution, if that form of collecting medium is used, from flowing into the channels of diffusion device 1 and to further reduce sensitivity to atmospheric motion. Accordingly, the porosity of the film and the size of its pores should be selected so that these functions are performed without interfering with the passage of the gaseous contaminant from the interior ends of the channels to the absorbing solution. That is, the diffusion of gaseous contaminant through this film should be significantly greater than the diffusion through the channels so that the overall rate of diffusion is essentially controlled only by the channels. It has been found that a film that is . 8 , 7~
50-80% porous with a pore size of 0.1-3.0 microns is sufficient for this purpose when channels as previously~described are used.
The diffusion device 1 of Figure 1 and the dosimeter of Figures 2 and 3 are an example of preferred embodiments of the present invention but the invention is not limited thereto The diffusion device, for example, can be in the shape of a plug sealed into the face of either sheet 3 or sheet 4.
Similarly, the receptacle of the dosimeter need not be pouch-like as hereinbefore decribed but, for example, could be in the form of a rigid cuvette.
Such an embodiment of the present invention is shown in Figures 4 and 5. With respect to these Figures, there is shown a personal dosimeter composed of a circular base cup 8 having cylindrical walls which define an open cavity 9. Base cup 8 is pro-vided with flange 13, having circular opening 14, which permits the assembled dosimeter to be fastened easily to a person's clothing. A friction-fitting circular cap ll tightly engages base cup 8 in a manner forming closure of cavity 9. Cap ll has a plurality of channels 12 of circular cross-section extending therethrough towards cavity 9. The channel-containing cap 11 functions as a gas diffusion device following Fick's Law and therefore the number, length, and diameter of channels 12 of cap 11 are selected as previously described for channels 2 of diffusion device l.
Cap ll and base cup 8 are preferably made from materials that are non-hygroscopic and both chemically and physically inert to the gaseous contaminant and to the collecting medium. The materials described for construction of diffusion device l are equally preferable for use in making 7~7 cap 11 and base cup 8.
A porous, hydrophobic,inert film 10 is placed over the channel openings on the interior face of cap 11. This film performs the same fun~tions as earlier described with respect to the dosimeter of Fig~res 2 and 3. Film 10 preferably is 15~1000 microns in thickness and has a porosity of 50-80% with a pore size of 0.1-3.0 microns. It is preferably made of polymers or copolymers of tetrafluoroethylene or hexafluoropropylene, although any hydrophobic, inert material of the above physical characteristics is sufficient.
In assembled form, the friction-fit between base cup 8 and cap 11 is liquid~tight and air-tight, thus completely enclosing cavity 9 of cup 8.
Channels 12 of cap 11 thus provide the only com-munication between the atmosphere and cavity 9 and the collecting medium therein. The collecting medium preferably completely fills cavity g and is retained therein, against seepage through channels 12, by film 10.
In use, a dosimeter of this invention is exposed to the air containing the gaseous contaminant for a period of time for which the average contaminant concentration is sought. When the collecting medium is an absorbing solution, for example, a measured amount of the solution is then withdrawn from thedosimeter by, for example~ a hypodermic syringe.
When the analysis is to be made photo-metrically, the withdrawn absorbing solution is mixed with appropriate color forming reagents which change the color of the absorbing solution. The intensity of color so formed is dependent upon the amount of gaseous contaminant collected. Although it is often desirable to have a self-contained dosimeter, as shown in U.S. Patent 4,208,371, in which the reagents are contained in the dosimeter ` 10 , ~
7~7 and no withdrawal of material is necessary, this is sometimes impractical. An example o this is where the reagents are highly acidic, as in the color-production for formaldehyde where the reagents are chromatropic acid and sulfuric acid. In such cases, it is difficult to package the reagents in a s~able and safe form, and the simple dosimeter of the present invention is well suited for these applications.
The dosimeter of this invention can be calibrated to give a direct relationship between colorimetric or spectrophotometric readings and average ambient concentration of the gaseous contaminant. This can be accomplished by follGwing a calibration procedure similar to that described in U.S. Patent 4,208,371. In such a procedure, several dosimeters are exposed over a given period of time to various known concentrations of a con-taminant for which calibration is sought. The dosimeters contain the same kinds and amounts of collecting medium. Spectrophotometric readings, for example, are determined or at least two dosimeters at each of several known concentrations, and a straight-line is plotted, using a least-squares analysis, through the data points thus obtained.
Claims (6)
1. A personal dosimeter for collecting a gaseous contaminant in proportion to its average ambient concentration during the collection time, the dosimeter consisting essentially of a closed receptacle;
a collecting medium for the gaseous contaminant within the receptacle;
a diffusion device, forming a part of the boundary of said receptacle, the device containing from 10-100 through-and-through channels adapted for the gaseous contaminant to diffuse therethrough from the atmosphere to the interior of the receptacle, said channels each having a diameter of from 50-1000 microns and a length of from 3.0-8.0 mm and said channels providing the only communication between the atmosphere and the interior of the receptacle; and a porous, hydrophobic, inert film covering the interior openings of said channels.
a collecting medium for the gaseous contaminant within the receptacle;
a diffusion device, forming a part of the boundary of said receptacle, the device containing from 10-100 through-and-through channels adapted for the gaseous contaminant to diffuse therethrough from the atmosphere to the interior of the receptacle, said channels each having a diameter of from 50-1000 microns and a length of from 3.0-8.0 mm and said channels providing the only communication between the atmosphere and the interior of the receptacle; and a porous, hydrophobic, inert film covering the interior openings of said channels.
2. The dosimeter of Claim 1 in which said receptacle is a pliable pouch of polymeric material.
3. The dosimeter of Claim 1 in which said receptacle consists essentially of a cup-like containiner having an open end and a cap engaging the container and covering the open end, and in which said diffusion device is embodied by at least a portion of the cap.
4. The dosimeter of Claim 1 in which the film has a thickness of from 15-1000 microns, a porosity of from 50-80%, and a pore size of from 0.1-3.0 microns.
5. The dosimeter of Claim 4 in which the collecting medium is an absorbing solution.
6. The dosimeter of Claim 5 in which the absorbing solution is for formaldehyde.
Applications Claiming Priority (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US16043880A | 1980-06-17 | 1980-06-17 | |
| US160,438 | 1980-06-17 | ||
| US25085481A | 1981-04-03 | 1981-04-03 | |
| US250,854 | 1981-04-03 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA1169747A true CA1169747A (en) | 1984-06-26 |
Family
ID=26856890
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA000379830A Expired CA1169747A (en) | 1980-06-17 | 1981-06-16 | Gaseous contaminant dosimeter |
Country Status (12)
| Country | Link |
|---|---|
| AR (1) | AR225818A1 (en) |
| AU (1) | AU7184481A (en) |
| BR (1) | BR8103735A (en) |
| CA (1) | CA1169747A (en) |
| DE (1) | DE3123834A1 (en) |
| ES (1) | ES8203511A1 (en) |
| FR (1) | FR2484642A1 (en) |
| GB (1) | GB2078371A (en) |
| IT (1) | IT1138423B (en) |
| NL (1) | NL8102892A (en) |
| PT (1) | PT73205B (en) |
| SE (1) | SE8103286L (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE3902402C1 (en) * | 1989-01-27 | 1990-06-13 | Draegerwerk Ag, 2400 Luebeck, De | |
| EP1655594A1 (en) | 2004-11-08 | 2006-05-10 | Vlaamse Instelling Voor Technologisch Onderzoek (Vito) | Diffusive sampling device |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB1456234A (en) * | 1973-05-24 | 1976-11-24 | Kodak Ltd | Formaldehyde testing material |
| US4256694A (en) * | 1978-06-05 | 1981-03-17 | Minnesota Mining And Manufacturing Company | Carbon monoxide monitoring system |
| US4208371A (en) * | 1978-07-07 | 1980-06-17 | E. I. Du Pont De Nemours And Company | Gaseous contaminant dosimeter with diffusion device therefor and method |
| US4269804A (en) * | 1979-08-24 | 1981-05-26 | E. I. Du Pont De Nemours And Company | Self-contained gaseous contaminant dosimeter |
-
1981
- 1981-05-25 SE SE8103286A patent/SE8103286L/en not_active Application Discontinuation
- 1981-06-12 BR BR8103735A patent/BR8103735A/en unknown
- 1981-06-15 AU AU71844/81A patent/AU7184481A/en not_active Abandoned
- 1981-06-16 CA CA000379830A patent/CA1169747A/en not_active Expired
- 1981-06-16 DE DE19813123834 patent/DE3123834A1/en not_active Withdrawn
- 1981-06-16 NL NL8102892A patent/NL8102892A/en not_active Application Discontinuation
- 1981-06-16 ES ES503075A patent/ES8203511A1/en not_active Expired
- 1981-06-16 AR AR285725A patent/AR225818A1/en active
- 1981-06-16 PT PT73205A patent/PT73205B/en unknown
- 1981-06-16 GB GB8118537A patent/GB2078371A/en not_active Withdrawn
- 1981-06-16 IT IT22351/81A patent/IT1138423B/en active
- 1981-06-17 FR FR8111931A patent/FR2484642A1/en not_active Withdrawn
Also Published As
| Publication number | Publication date |
|---|---|
| GB2078371A (en) | 1982-01-06 |
| SE8103286L (en) | 1981-12-18 |
| AR225818A1 (en) | 1982-04-30 |
| IT8122351A0 (en) | 1981-06-16 |
| PT73205A (en) | 1981-07-01 |
| DE3123834A1 (en) | 1982-04-08 |
| IT1138423B (en) | 1986-09-17 |
| FR2484642A1 (en) | 1981-12-18 |
| ES503075A0 (en) | 1982-04-01 |
| NL8102892A (en) | 1982-01-18 |
| BR8103735A (en) | 1982-03-02 |
| PT73205B (en) | 1982-07-01 |
| AU7184481A (en) | 1981-12-24 |
| ES8203511A1 (en) | 1982-04-01 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| MKEX | Expiry |