Device for detecting insect larvae and adult insects in a store by sensing volatile and chemical pheromones of insect larvae and adult insects
阅读说明:本技术 通过感测昆虫幼虫和昆虫成虫的挥发性信息素和化学信息素来检测储藏物中的昆虫幼虫和昆虫成虫的装置 (Device for detecting insect larvae and adult insects in a store by sensing volatile and chemical pheromones of insect larvae and adult insects ) 是由 尼古拉斯·约瑟夫·斯米兰尼奇 赛缪尔·费尔斯通·赖克特 法兰克·伯纳德·图德龙 于 2019-02-01 设计创作,主要内容包括:用于通过感测诸如挥发性信息素、化学信息素和利它素之类的气相标志物来检测储藏物中存在的昆虫幼虫和昆虫成虫的低成本、高精确度且便携的装置。本文公开的方法、装置和系统利用了传感器阵列,传感器阵列配置为同时测量多个目标标志物并过滤背景气体,同时保持紧凑、高度精确且易于操作。(A low cost, high precision and portable device for detecting insect larvae and adult insects present in a deposit by sensing gas phase markers such as volatile pheromones, semiochemicals and kairomones. The methods, devices, and systems disclosed herein utilize a sensor array configured to simultaneously measure multiple target markers and filter background gas while remaining compact, highly accurate, and easy to operate.)
1. A method of identifying insect infestation of a deposit by detecting one or more target Volatile Organic Compounds (VOCs) within a target fluid stream, the method comprising:
providing an apparatus, the apparatus comprising:
a sensor array comprising a plurality of VOC sensors, wherein each VOC sensor comprises:
a substrate having a first side and a second side;
a resistive heater circuit formed on the first side of the substrate;
a sensing circuit formed on the second side of the substrate; and
a chemically sensitive film formed over the sensing circuitry on the second side of the substrate;
heating one or more of the plurality of VOC sensors to at least a first operating temperature;
contacting the one or more VOC sensors with the target fluid stream;
determining a set of conductance change values (Δ K) corresponding to each of the one or more VOC sensors in contact with the target fluid streami) (ii) a And
determining a concentration of a gas component ([ X ] of one or more target VOCs) within the target fluid stream based on the set of conductance change values]n)。
2. The method of claim 1, wherein the method further comprises:
measuring a signal conductance of the one or more VOC sensors after contacting the one or more VOC sensors with the target fluid stream;
wherein the set of conductance change values (Δ K) is determined based on a difference between the signal conductance of each of the one or more VOC sensors in contact with the target fluid stream and a baseline conductance of each of the respective VOC sensorsi)。
3. The method of claim 2, wherein the baseline conductance of the one or more VOC sensors is measured when the one or more VOC sensors are in an atmosphere free of any target VOC.
4. The method of claim 3, wherein the method further comprises:
adjusting the baseline conductance of one or more VOC sensors after contact with at least one target VOC to match the baseline conductance of the respective VOC sensor prior to contact with at least one target VOC, wherein the baseline conductance is adjusted by heating one or more VOC sensors to at least a second operating temperature.
5. The method of claim 2, wherein the method further comprises:
contacting one or more of the plurality of VOC sensors with a sample fluid stream, the sample fluid stream being free of any target VOC; and
measuring the baseline conductance of the one or more VOC sensors.
6. The method of claim 1, wherein the method further comprises:
determining one or more specific net conductance values for one or more VOC sensors, wherein each specific net conductance value corresponds to one of the target VOCs.
7. The method of claim 6, wherein the specific net conductance value for each corresponding target VOC is determined by:
contacting the one or more VOC sensors with a control fluid stream having a known concentration of the target VOC;
measuring a test conductance of each of the one or more VOC sensors; and
for each of the one or more VOC sensors, a specific net conductance value is calculated based on the measured test conductance of the VOC sensor and the known concentration of the target VOC within the control fluid stream.
8. The method of claim 7, wherein the method further comprises:
determining a plurality of specific net conductance values for one or more VOC sensors, wherein each of said specific net conductance values for each of said VOC sensors corresponds to a different target VOC.
9. The method of claim 6, wherein the gas constituent concentration ([ X ] of the one or more target VOCs within the target fluid stream is determined based on the set of conductance changes and one or more specific net conductance values for each of the one or more VOC sensors]n)。
10. The method of claim 1, wherein the first operating temperature is between about 180 ℃ and about 400 ℃.
11. The method of claim 1, wherein the target fluid flow is an air sample taken from within a vicinity of the reservoir to be evaluated.
12. A device for detecting one or more target Volatile Organic Compounds (VOCs) within a target fluid stream, the device comprising:
a sensor array having a plurality of VOC sensors, wherein each VOC sensor comprises:
a substrate;
a resistive heater circuit formed on a first side of the substrate;
a sensing circuit formed on a second side of the substrate; and
a chemically sensitive film formed over the sensing circuitry on the second side of the substrate.
13. The device of claim 12, wherein the sensor array comprises about two to about ten VOC sensors.
14. The device of claim 12, wherein the resistive heater circuit of at least one of the plurality of VOC sensors is a serpentine pattern having a warp wire width of about 0.288mm to about 0.352mm and a warp wire spacing width of about 0.333mm to about 0.407 mm.
15. The device of claim 12, wherein the sensing circuitry of at least one of the plurality of VOC sensors comprises first and second sensing elements forming a pair of extended interdigitated contacts;
wherein the first sensing element comprises a plurality of extended contacts, each contact having a latitudinal wire width of about 0.162mm to about 0.198mm and a latitudinal wire spacing of about 0.738mm to about 0.902 mm; and
wherein the second sensing element comprises a plurality of extended contacts, each contact having a latitudinal wire width of about 0.162mm to about 0.198mm and a latitudinal wire spacing of about 0.738mm to about 0.902 mm.
16. The device of claim 15, wherein each of the first and second sensing elements comprises at least three extended contacts, and wherein the sensing circuitry has a latitudinal wire spacing between each extended contact of the first and second sensing elements of about 0.288mm to about 0.352 mm.
17. The device of claim 12, wherein at least one of the resistive heater circuit and the sensing circuit is formed from a composition comprising platinum, and the chemically sensitive film is a nanocrystalline tin oxide film formed from an aqueous tin oxide gel.
18. The device of claim 12, wherein the chemically sensitive membrane comprises a dopant selected from the group consisting of: platinum; palladium; molybdenum; tungsten; nickel; ruthenium; and osmium.
19. The apparatus of claim 12, wherein the sensor array is operatively connected to a controller configured to:
measuring a conductance of one or more VOC sensors of the plurality of VOC sensors;
determining a set of conductance change values corresponding to each of the one or more VOC sensors in contact with the target fluid stream; and
determining a gas constituent concentration of one or more target VOCs within the target fluid stream based on the set of conductance change values.
20. A system for identifying insect infestation of a deposit, the system comprising:
a test chamber enclosing a sensor array, the sensor array comprising a plurality of VOC sensors;
an air transfer unit configured to recover a fluid flow and deliver the fluid flow to the testing chamber; and
a controller operatively connected to the air delivery unit and the sensor array, wherein the controller is configured to:
operating the air transfer unit to recover the fluid stream from the testing chamber and deliver the fluid stream to the testing chamber, wherein one or more of the plurality of VOC sensors are in fluid contact with the fluid stream;
operating the sensor array to measure conductance of one or more VOC sensors of the plurality of VOC sensors;
determining a set of conductance change values corresponding to each of the one or more VOC sensors; and
determining a gas constituent concentration of one or more target VOCs within the fluid stream based on the set of conductance change values.
21. The system of claim 19, wherein at least one of the one or more target VOCs within the fluid stream is selected from the group consisting of: 4, 8-dimethyldecanal; (Z, Z) -3,6- (11R) -dodecadien-11-olide; (Z, Z) -3, 6-dodecadienolide; (Z, Z) -5,8- (11R) -tetradecadien-13-olide; (Z) -5-tetradecene-13-lactone; (R) - (Z) -14-methyl-8-hexadecenal; (R) - (E) -14-methyl-8-hexadecenal; gamma-ethyl-gamma-butyrolactone; (Z, E) -9, 12-tetradecadienylacetate; (Z, E) -9, 12-tetradecadien-1-ol; (Z, E) -9, 12-tetradecadienal; (Z) -9-tetradecene acetate; (Z) -11-hexadecene acetate; (2S,3R, 1' S) -2, 3-dihydro-3, 5-dimethyl-2-ethyl-6 (1-methyl-2-oxobutyl) -4H-pyran-4-one; (2S,3R, 1' R) -2, 3-dihydro-3, 5-dimethyl-2-ethyl-6 (1-methyl-2-oxobutyl) -4H-pyran-4-one; (4S,6S,7S) -7-hydroxy-4, 6-dimethyl-3-nonanone; (2S,3S) -2, 6-diethyl-3, 5-dimethyl-3, 4-dihydro-2H-pyran; 2-palmitoyl-1, 3-cyclohexanedione; and 2-oleoyl-1, 3-cyclohexanedione.
Background
The following disclosure relates generally to insect and insect infestation detection techniques, chemical sensing techniques, gas detection techniques, volatile organic compound analysis techniques, gas sensing microchip arrays, and methods and apparatus related thereto. The present invention finds particular application in connection with techniques involving highly sensitive and selective detection of insects in stored food and other products or materials.
Storage insects ("SPI") are most commonly found in food products, food materials, or infesting equipment that prepares, processes, packages, or stores the food. The economic losses these pests cause in processing, transportation and storage systems can be millions of dollars per pollution, product recall, consumer complaints/prosecution, and pest control application events (Arthur et al, 2009). In addition, some SPI can have health consequences if taken inadvertently, causing gastric stress in infants and the elderly (Okamura, 1967).
Current insect detection relies on flashlight inspection and the use of traps with a variety of synthetic pheromone lures and traps that capture SPI adults. Pheromones are volatile organic compounds ("VOCs") emitted from males and/or females of an individual species. Pheromone lures and traps are dependent on insect mobility, and these can be significantly affected by temperature. Pheromone volatility, quantity/mass, and human mobility and insect dynamics interact with these elements, resulting in considerable variability in trap data. The interpretation of trap capture is based on a small sampling of the population (2% to 10% or less). This makes detection and remediation of pest infestation difficult.
Indian meal moth ("IMM") is the most common deposit insect found in the United states (Mueller, 1998; Resener 1996). In the united states, such insects are more common than any other insect in the storage of food and grain. IMM adults can be found almost anywhere in the temperate regions of the world. Furthermore, in the united states and europe, IMM is one of the pests responsible for the greatest damage. This insect survives so well in our environment for two reasons: 1) during the transient life of the female, it lays down a large number of eggs; and 2) genetic alteration of IMM or the ability to survive in humans in response to pesticides used to protect their food (drug resistance). IMM was found to be the most resistant insect known to man. During the fifty years, the genetic composition of this insect has been altered to combat the commonly used insecticide Malathion (Malathion). In the 70's of the 19 th century, IMM began to show evidence of resistance to this common pesticide. IMM gave 60,000 times the resistance to this insecticide.
IMM is most commonly found on equipment that prepares, processes, packages or stores food as finished food, food materials such as stored wheat products, milled/processed wheat and other stores such as milled cereal products, flour, bran, pasta products, spices, or infests. IMM larvae are the destructive life stage of the insect and are very greedy. Larvae are highly mobile and can constantly seek new food sources. The value of foods is destroyed by the food they consume, the woodchips they leave, and the net that larvae leave as they move.
In addition, IMM is often a precursor to insects for other stores. Infection with untreated IMM may be an indicator of impending infection with other SPIs (Mueller, 2016). The five most common storage insects (SPIs) include Indian meal moth (Indian meal moth Plodia interpunctella), warehouse beetles (bark beetle varibian), mealworm beetles (Tribolium spp.), corn beetles (Oryzaphium spp.), and tobacco beetles (Nicotiana tabacum sericorn) (Mueller, 1998; Hagstrum and Subramanyam, 2006). The economic losses caused by these pests in processing, transportation and storage can be millions of dollars per pollution, product recall, consumer complaints/prosecution, and pest control application events (Arthur, 2009). However, there is no effective low cost method to monitor and detect them.
Several SPI pheromones have been identified but are not commercially available due to short shelf life and production cost (Phillips et al, 2000). These compounds are unique, but can attract interspecific competitors, such as in storage food moth populations and complex species of the genus pissodes. The single pheromone (Z, E) -9, 12-tetradecadienylacetate is the major pheromone of the genus oryza incertulas, but will attract the other three food moths of the species mealworm. The pheromone compound R, Z14-methyl-8-hexadecenal is a major component that attracts storage beetles (bark beetles), but will also attract three other common species of the genus bark beetle, including quarantine pests (bark beetles, khapra beetles). A single compound, 4, 8-dimethyldecanal, attracts several tenebrio molitor (species of the genus theliopsis), and (Z, Z) -3, 6-dodecadien-11-olide attracts two species of tenebrio molitor (species of the genus diabrotica), but the pheromone (4S,6S,7S) -4, 6-dimethyl-7-hydroxy-3-nonanone of the tobacco beetle (tobacco beetle) is unique to this species.
Furthermore, with respect to possible target semiochemicals and/or kairomones, these semiochemicals and kairomones are high molecular weight VOCs. As a result, their vapor pressure and concentration in the headspace above infested stores will be low and therefore more difficult to detect.
Accordingly, it is desirable to eliminate variability and uncertainty in detecting pest presence/absence, abundance, and location through the use of methods, devices, and systems that can detect and determine the concentration of multiple pheromones. Furthermore, it would be desirable to provide methods, devices and systems that can detect other deposit insect larvae by sensing semiochemicals/kairomones of the insect larvae in a similar manner. The threshold concentration may be established to immediately determine whether the most common SPI is present in a trailer, land/sea container, bulk tote, pallet or closet of bagged material. It is also desirable to provide the ability to detect VOC concentration gradients, which help to locate and accurately describe structures, wall voids, cracks and crevices or SPI infestation within a device. Furthermore, it would be desirable to provide a handheld device that can eliminate many of the dependencies on insect mobility and environment as factors affecting activity from the SPI monitoring model.
Cited references
The following references are mentioned, the entire disclosures of which are incorporated herein by reference:
Arthur F.H.Johnson J.A.Neven L.G.Hallman G.J.Follett P.A.(2009).Insect Pest Management in Postharvest Ecosystems in the United States ofAmerica.Outlooks on Pest Management,20:279–284.
hagstrum D.W. and Subramanyam B. (2006). Fundamentals of Stored-produced engineering.St.Paul: AACC Int.
Mueller, David K (1998). Stored Product Protection A Period of Transmission. instruments Limited, Ind. Pernals.
Okumura, G.T, (1967). A Report of Cantharis and Allergy used by Trogopera (Coleoptera: Dermestidae). California Vector Views, Vol.14No.3, pages 19-22.
Phillips, T.W., Cogan, P.M., and Fadamiro, H.Y. (2000). Pheromones in B.Subramanyam and D.W.Hagstrum (Eds.). Alternatives to Pesticides in Stored-Product IPM, p.273. 302. Boston Kluwer academic Press, Mass
Resener, A.M (1997). National Survey of Stored produced instruments. Fumigants and Pheromones, pp.46, 3-4.
Disclosure of Invention
Disclosed in various embodiments herein are low-cost and high-precision methods, devices, and systems for identifying insect infestation of a storage (e.g., food) based on the detection of one or more target volatile organic compounds ("VOCs") within a target fluid stream (e.g., an air sample) sampled from the vicinity of the storage. The disclosed methods, systems and devices with minimal cost and high precision enable real-time, non-invasive detection of insect larva semiochemicals/kairomones or insect adult pheromones in the environment of a deposit.
According to a first embodiment of the present disclosure, there is provided a method of identifying insect infestation of a deposit by detecting one or more target VOCs within a target fluid stream, the method comprising the steps of: providing a device comprising a sensor array having a plurality of VOC sensors; heating one or more VOC sensors of a plurality of VOC sensors to at least a first operating temperature; contacting one or more VOC sensors with a target fluid stream; determining a set of conductance change values corresponding to each of the one or more VOC sensors in contact with the target fluid stream; and determining a gas constituent concentration of one or more target VOCs within the target fluid stream based on the set of conductance change values. Further, each VOC sensor of the provided sensor array comprises: a substrate having a first side and a second side; a resistive heater circuit formed on a first side of a substrate; a sensing circuit formed on a second side of the substrate; and a chemically sensitive film formed over the sensing circuitry on the second side of the substrate. In particular embodiments, the method may include correcting the baseline resistance of the VOC sensor to an earlier baseline value after sampling the VOC marker in the fluid stream, which may be accomplished by adjusting the operating temperature of one or more VOC sensors after each sampling of the target VOC.
In accordance with another embodiment of the present disclosure, there is provided an apparatus for detecting one or more target VOCs within a target fluid stream, the apparatus comprising: a sensor array having a plurality of VOC sensors, wherein each VOC sensor comprises: a substrate; a resistive heater circuit formed on a first side of a substrate; a sensing circuit formed on a second side of the substrate; and a chemically sensitive film formed over the sensing circuitry on the second side of the substrate.
In accordance with another embodiment of the present disclosure, there is provided a system for identifying insect infestation of a deposit, the system comprising: a test chamber surrounding the sensor array; an air transfer unit configured to recover a fluid flow and deliver the fluid flow to a testing chamber; and a controller operatively connected to the air delivery unit and the sensor array. The sensor array includes a plurality of VOC sensors, and the controller is configured to: operating the air transfer unit to withdraw the fluid stream from the target area and deliver the fluid stream to the testing chamber; operating the sensor array to measure the conductance of one or more of the plurality of VOC sensors; determining a set of conductance change values corresponding to each of the one or more VOC sensors; and determining a concentration of the gas component of the one or more target VOCs within the fluid stream based on the set of conductance change values.
Drawings
The disclosure may take form in various components and arrangements of components, and in various steps and arrangements of steps. The drawings are only for the purpose of illustrating preferred embodiments and are not to be construed as limiting the disclosure.
Fig. 1 is a flow diagram illustrating a method of identifying insect infestation according to one embodiment of the present application.
Fig. 2A-2B are flow diagrams illustrating another method of identifying insect infestation according to another embodiment of the present application.
Fig. 3 is a block diagram illustrating a system configured to perform the methods disclosed herein, according to one embodiment of the present application.
Fig. 4A-4B are schematic views of a first side (fig. 4A) and a second side (fig. 4B) of a single VOC sensor according to certain embodiments of the present application.
Fig. 5 is a schematic view of a single VOC sensor suspended in a holder according to one embodiment of the present application.
Fig. 6 is a representative side cross-section of a sensor array including a plurality of VOC sensors according to an embodiment of the present application.
FIG. 7 is a block diagram of an infestation detection system according to one embodiment of the present application.
Fig. 8A to 8D are graphs showing the sensitivity of a VOC sensor array according to an embodiment of the present application to various target volatile organic compounds.
Fig. 9A-9C are graphs showing the response of a first VOC sensor to the presence of three target deposit insects ("SPIs"), according to one embodiment of the present application.
Fig. 10A-10C are graphs showing the response of a second VOC sensor to the presence of three target deposit insects ("SPIs"), according to another embodiment of the present application.
Fig. 11A-11C are graphs showing the response of a third VOC sensor to the presence of three target deposit insects ("SPIs"), according to one embodiment of the present application.
Fig. 12A-12C are graphs showing the response of a fourth VOC sensor according to one embodiment of the present application to the presence of three target deposit insects ("SPIs").
Fig. 13A-13D are graphs showing the response of four VOC sensors to the presence of varying amounts of three target deposit insects ("SPIs"), according to one embodiment of the present application.
Detailed Description
In the following specification and the claims which follow, reference will be made to a number of terms which shall be defined to have the following meanings.
Definition of
In the following specification and the claims which follow, reference will be made to a number of terms which shall be defined to have the following meanings. Although specific terms are used in the following description for the sake of clarity, these terms are intended to refer only to the particular structure of the embodiments selected for illustration in the drawings, and are not intended to define or limit the scope of the disclosure. In the drawings and the following description, it is to be understood that like numeric designations refer to components having like functions. Further, it should be understood that the drawings are not to scale.
The singular forms "a", "an" and "the" include plural referents unless the context clearly dictates otherwise.
In this document, the term "comprising" is used as requiring the presence of specified components/steps and allowing the presence of other components/steps. The term "comprising" should be interpreted as including the term "consisting of … …" allowing only the specified components/steps to be present.
Numerical values should be understood to include the following: the numerical values are the same when reduced to the same number of significant digits and the numerical values differ from the stated value by less than the experimental error of conventional measurement techniques of the type described in this application to determine the value.
All ranges disclosed herein are inclusive of the endpoints and independently combinable (e.g., a range of "2 mm to 10 mm" is inclusive of the endpoints, 2mm and 10mm, and all intermediate values).
The term "about" may be used to include any numerical value that may be varied without changing the basic function of the value. When used with a range, "about" also discloses the range defined by the absolute values of the two endpoints, e.g., "about 2 to about 4" also discloses the range "2 to 4". More specifically, the term "about" can refer to plus or minus 10% of the indicated number.
The terms "ppm" and "ppb" should be understood to mean "parts per million" and "parts per billion", respectively. As used herein, "ppm", "ppb", and the like refer to volume fraction, not mass fraction or mole fraction. For example, a value of 1ppm may be expressed as 1 μ V/V, while a value of 1ppb may be expressed as 1 nV/V.
The present disclosure may be understood more readily by reference to the following detailed description and the various drawings discussed therein.
Method of producing a composite material
Disclosed herein are methods for determining the presence of insect infestation in stores by highly sensitive and highly selective detection of the presence of one or more target volatile organic compounds ("VOCs"), such as certain semiochemicals, kairomones and/or pheromones of various store insects ("SPIs").
Referring to fig. 1, a
In particular embodiments, the
In a preferred embodiment, the target fluid stream is an air sample taken from the vicinity of the reservoir being evaluated for possible insect infestation. That is, the target fluid flow may be a gas sample from a headspace above the target reservoir.
In further embodiments, the one or more target VOCs are semiochemicals, kairomones and/or pheromones associated with one or more insects such as SPI. In particular, the one or more target VOCs can be semiochemicals, kairomones and/or pheromones associated with, for example, tribolium castaneum, warehouse beetles, indian meal moth and/or tobacco beetles. In particular embodiments, at least one of the one or more target VOCs within the fluid stream may be selected from the group consisting of: 4, 8-dimethyldecanal; (Z, Z) -3,6- (11R) -dodecadien-11-olide; (Z, Z) -3, 6-dodecadien-lactone; (Z, Z) -5,8- (11R) -tetradecadien-13-olide; (Z) -5-tetradecene-13-lactone; (R) - (Z) -14-methyl-8-hexadecenal; (R) - (E) -14-methyl-8-hexadecenal; gamma-ethyl-gamma-butyrolactone; (Z, E) -9, 12-tetradecadienylacetate; (Z, E) -9, 12-tetradecadien-1-ol; (Z, E) -9, 12-tetradecadienal; (Z) -9-tetradecene acetate; (Z) -11-hexadecene acetate (Hexa-decenyl acetate); (2S,3R, 1' S) -2, 3-dihydro-3, 5-dimethyl-2-ethyl-6 (1-methyl-2-oxobutyl) -4H-pyran-4-one; (2S,3R, 1' R) -2, 3-dihydro-3, 5-dimethyl-2-ethyl-6 (1-methyl-2-oxobutyl) -4H-pyran-4-one; (4S,6S,7S) -7-hydroxy-4, 6-dimethyl-3-nonanone; (2S,3S) -2, 6-diethyl-3, 5-dimethyl-3, 4-dihydro-2H-pyran; 2-palmitoyl-1, 3-cyclohexanedione; and 2-oleoyl-1, 3-cyclohexanedione.
Referring to fig. 2A and 2B, a
In step S04, a device is provided that includes a sensor array having a plurality of VOC sensors. Each VOC sensor of the sensor array comprises: a substrate; a resistive heater circuit; a sensing circuit; and a chemically sensitive film formed over the sensing circuit. In some implementations, a resistive heater circuit can be formed on a first side of a substrate, a sensing circuit can be formed on a second side of the substrate, and a chemically sensitive film can be formed over the sensing circuit on the second side of the substrate.
In particular embodiments, the sensor array comprises a plurality of different VOC sensors. That is, by including a catalytic material in the chemically sensitive film (i.e., active layer), the surface composition of one or more of the plurality of VOC sensors can be altered. In other words, the chemically sensitive film of the one or more VOC sensors may comprise a dopant. In some embodiments, the dopant can be, for example, a transition metal. For example, the dopant may be selected from the group consisting of: platinum; palladium; molybdenum; tungsten; nickel; ruthenium; osmium.
In step S206, one or more VOC sensors of the plurality of VOC sensors are heated to at least a first operating temperature. In particular embodiments, the working temperature is between about 180 ℃ and about 400 ℃. In other embodiments, the operating temperature of one or more VOC sensors is maintained during subsequent steps of the method. In particular, the heating circuit of each VOC sensor can be used to measure and control the temperature of the VOC sensor throughout its operation.
In particular embodiments of the
In step S210, one or more VOC sensors of the plurality of VOC sensors are contacted with the sample fluid stream. In a preferred embodiment, the sample fluid stream is a volume of air without any target VOC that can be tested with the
In step S212, a baseline conductance of one or more VOC sensors in contact with the sample fluid stream is measured using the sensing circuitry of the VOC sensors. Since the thin film formed on the sensing circuitry of the VOC sensor is chemically sensitive (e.g., semi-conductive), the current flowing in the material is due to electrons in the conduction band of the thin film, which may be affected by undesired and/or target compounds (e.g., target VOCs). Thus, after the operating temperature is reached and contacted with a gas sample (i.e., sample fluid stream) that does not contain a marker gas (i.e., a fluid stream having at least one target VOC) in step S206, the resistance of the VOC sensor is measured and recorded as a baseline resistance or baseline conductance. In some embodiments, a set of baseline conductances is determined
And the set of baseline conductances includes a baseline conductance for each of the plurality of VOC sensors (e.g.)。In step S216, the sample fluid stream is brought out of contact with the VOC sensors of the sensor array. In particular embodiments, this may include purging a chamber or reactor containing the sensor array and/or one or more VOC sensors.
In step S218, one or more VOC sensors are contacted with a control fluid stream (e.g., a marker gas) having a known concentration of at least one target VOC.
In step S220, a control conductance of each of the one or more VOC sensors in contact with the control fluid stream is measured. The resistance/conductance of the VOC sensor changes because contact with the control fluid stream can make more or less electrons available for chemically sensitive membrane based conduction.
Then, in step S222, a specific net conductance value for each of the one or more VOC sensors is determined based on the measured test conductance of the VOC sensor and the known concentration of the target VOC within the control fluid stream. As studied and disclosed herein, the amount of conductance change may be proportional to the concentration of the gas, where the specific net conductance ("SNC") as used herein refers to the proportionality coefficient. In particular embodiments, the first target VOC concentration of the control fluid stream is from about 10ppb to about 400 ppb. In a preferred embodiment, the control fluid stream has a target VOC concentration of about 200 ppb.
For one or more of the plurality of VOC sensors, the resulting change between the baseline conductance and the measured control conductance is determined and divided by the indicated (i.e., known) concentration to give the SNC value (i.e., a measure of the sensitivity of the chip to the gas), typically expressed in units of "nano-mho/parts per billion" or "nmho/ppb". In this application, each chip will have a different SNC for each target gas of interest.
For further calibration, in step S226, at least steps S218-S222 may be repeated for additional control fluid flows to obtain a plurality of specific net conductance ("SNC") values for one or more VOC sensors, wherein each specific net conductance value for each VOC sensor corresponds to a different target VOC. In some embodiments, the plurality of SNC values is a set of SNC values ({ SNCi,X} 224, and the set of SCN values includes SNC values for one or more target VOCs corresponding to each of the plurality of VOC sensors (e.g., for a first VOC sensor,
in the case of the second VOC sensor,etc.) wherein X isnRepresents a particular target VOC.The
Turning to fig. 2B, after the calibration step 208, the baseline conductance of the VOC sensor may be adjusted in step S232 by: the method includes the steps of cleaning a sensor array chamber of the target VOC, measuring the conductance of one or more VOC sensors, comparing the measured conductance to a corresponding baseline conductance, and heating the one or more VOC sensors to at least a second operating temperature such that the conductance of each VOC sensor at the second operating temperature matches the corresponding baseline conductance 214.
After the adjusting step S232 or the heating step S206, the one or more VOC sensors are contacted with the target fluid stream at step S234. In particular embodiments, the target fluid stream is an air sample taken from the vicinity of the reservoir being evaluated for possible insect infestation. Thus, the target fluid stream may comprise one or more target VOCs, such as semiochemicals, kairomones and/or pheromones associated with one or more insects (e.g., SPI). For example, for certain SPIs, several pheromones and semiochemicals are listed in tables 1 and 2 below:
TABLE 1 SPI and pheromones thereof
TABLE 2 IMM pheromone and semiochemical components
In step S236, the signal conductance of the one or more VOC sensors is measured after contacting the one or more VOC sensors with the target fluid stream.
Then, in step S238, a set of conductance change values ({ Δ K) for one or more VOC sensors of the sensor array is determinedi}). In particular embodiments, for each VOC sensor, the conductance change value may be determined as follows:
wherein i is an integer,. DELTA.KiIs the conductance change value, K, of the VOC sensor iiFor measuring the signal conductance of the VOC sensor i in the presence of a target fluid flow
Is the baseline conductance of the VOC sensor i.In step S240, a gas constituent concentration ([ X ] of one or more target VOCs within the target fluid stream is determined based on the set of conductance change values]n). In particular embodiments, more than one target may be present in the target fluid stream, in addition to other background and/or interfering gasesVOC, making analysis difficult. In particular embodiments, the concentration of the gas constituent of the one or more target VOCs ([ X ") within the target fluid stream is determined based on the set of conductance change values and the one or more SNCs for each VOC sensor]n). In other embodiments, the concentration of the gas constituent of one or more target VOCs ([ X ]) within the target fluid stream is determined by solving a system of equations]n) For example, the system of equations shown below:
ΔK1=SNC1A[A]+SNC1B[B]+SNC1C[C]+SNC1D[D]
ΔK2=SNC2A[A]+SNC2B[B]+SNC2C[C]+SNC2D[D]
ΔK3=SNC3A[A]+SNC3B[B]+SNC3C[C]+SNC3D[D]
ΔK4=SNC3A[A]+SNC4B[B]+SNC4C[C]+SNC4D[D]
wherein Δ KiFor a measured change in conductance of sensor "i", i "is in the range of 1 to 4, SNCijFor "specific net conductance" of sensor "i" when contacted by gas (e.g., target VOC) "j", which is gas or gas species A, B, C or D, and [ X]Is the concentration of gas A, B, C or D, expressed as gas volume-to-volume, i.e., liters of gas per liter of total atmosphere.
Although only four target VOCs (i.e., A, B, C and D) and four sensors (i.e., 1, 2,3, and 4) are shown above, the number of target VOCs and the number of VOC sensors present in the analysis may vary depending on different applications or different uses and is not limited to only four. As a result, the problem of determining the concentration of several target VOCs and/or background gases and interfering gases present within a certain fluid stream becomes possible.
In some embodiments, the
In particular embodiments, the user interface may be a dedicated screen, such as a TFT LCD screen, an IPS LCD screen, a capacitive touch screen LCD, an LED screen, an OLED screen, an AMOLED screen, or the like. In other embodiments, the user interface may include a wired or wireless communication protocol, such as bluetooth, BLE, Wi-Fi, 3G, 4G, 5G, LTE, etc., and may be configured to communicate the results of the analysis to an auxiliary device (e.g., mobile phone, tablet, computer, etc.) of the associated user via the communication protocol.
In a preferred embodiment, the target fluid stream is an air sample (or volume) taken from the vicinity of the reservoir being evaluated for possible insect infestation. In step S244, steps S232-S242 may be repeated by sampling multiple target fluid streams (e.g., air samples) from within multiple adjacent areas of the deposit to be evaluated. That is, the
In other embodiments of the
In step S250, the
These and other aspects of the apparatus used to implement the
Device and system
An apparatus and system for performing the above-described
Referring to fig. 3, a block diagram of an
As shown in fig. 4A and 4B, which illustrate a first side (fig. 4A) and a second side (fig. 4B) of a
The heater circuit material may be, for example, lithographically patterned into a desired pattern on the
Turning now to FIG. 4B,
The sensing circuit material may be, for example, photolithographically patterned into a desired pattern on the
Similarly, the
In some embodiments, each of the first and
The
In addition, the
In particular embodiments,
Due to the chemical structure of the target VOC and the operating conditions of each
TABLE 3 semiochemical/kairomones chemical Structure
In a preferred embodiment, the
Each
With further reference to fig. 6, a side view of an
In other words, the
Returning to FIG. 3, additional components of infestation detection system 302 are described in accordance with aspects of the present application. A system 302 for identifying insect infestation of a deposit is provided, the system 302 including a
In various embodiments, the
The air transfer unit 302 may also define a fluid flow path for fluid flow 384 from outside the system 302 to the flow 314 entering the inlet 310 of the
Further, the
The
In some embodiments, the system 302 also includes one or more
The system 302 may also include a power supply 388, the power supply 388 being operatively connected to at least one of the
The various components of the described system will now be discussed in more detail with reference to fig. 7. As shown, fig. 7 illustrates a block diagram of a
As shown, the
As used herein, the term "software" is intended to include any collection or set of instructions executable by a computer or other digital system for configuring the computer or other digital system to perform a task intended as software. The term "software" is intended to include such instructions stored in a storage medium such as RAM, hard disk, optical disk, etc., and is also intended to include so-called "firmware" as software stored on ROM, etc. Such software may be organized in various ways and may include software components organized as libraries, internet-based programs stored on remote servers and the like, source code, interpreted code, object code, directly executable code, and the like. It is contemplated that the software may invoke system level code or invoke other software residing on a server or other location to perform some function.
In various embodiments,
The
As previously described, the
The air
The operating
As described above, the
In any case, in various embodiments, a