ABSTRACT
Gas sensors are crucial devices in various fields such as industrial safety, environmental monitoring, and gas infrastructure. Designed to have high-sensitivity, stability, and reliability, gas sensors are often required to be cost-effective with quick response and compactness. To meet diverse needs, we developed two types of gas sensors based on volumetric and manometric analyses. These sensors could operate by measuring gas volume and pressure changes, respectively, based on emitted gas. These sensors are capable of determining gas transport parameters such as gas uptake, solubility, and diffusivity for gas-charged polymers in a high-pressure environment. These sensors can provide rapid responses within one-second. They can measure gas concentration ranging from 0.01 wt·ppm to 1,500 wt·ppm with adjustable sensitivity and measurement ranges. As a result, such sensor system can be used to facilitate real time detection and analysis of gas transport properties in pure gases including H2, He, N2, O2, and Ar.
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KEYWORDS: Gas sensors, Volumetric measurement, Manometric measurement, Gas uptake, Diffusion
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KEYWORDS: 가스 센서, 부피측정법, 압력측정법, 가스 장입량, 확산
1. Introduction
Gas detecting sensor is crucial for ensuring safety, particularly under environments where hazardous gases like hydrogen or carbon monoxide are released [
1-
10]. Early detection of gas emission and leak can prevent accidents, fires and risks. It is also essential for environmental monitoring, as it helps in detecting pollutants and maintaining air quality. Accurate gas sensing plays an important role in optimizing operations, particularly for renewable energy source like hydrogen. By ensuring precise monitoring of hydrogen gas concentrations, it enhances safety, efficiency and performance throughout the hydrogen production, storage and distribution processes [
11-
22].
In hydrogen refueling station charged to high-pressure H
2, polymer materials play an important role [
23-
45]. For instance, polymer-based materials such as O-ring seals, gasket, liner material and non-metallic pipeline are widely used. It was designed to withstand hydrogen environments. However, these polymers are subjected to harsh conditions including wide temperature fluctuations (-70 to 90
oC) and pressure variations (1 to 90 MPa). These conditions can lead to seal damage, insufficient contact with glove and gas permeation through polymer seals, all of which can result in hydrogen leakage [
46-
52].
Gas permeation including hydrogen in polymer materials also occurs when gases pass through the polymer matrix due to diffusion. This process is influenced by aspects including temperature, pressure and chemical natures of both the gas and the polymer [
53-
55]. For instance, in the use of polymer membranes for gas separation, materials like polyimide are employed to selectively permeate gases like oxygen or carbon dioxide while blocking other gases. A common example is the use of polymeric membranes in CO
2 capture systems, where the membrane's permeability to CO
2 is crucial for effective separation from industrial emissions. However, the permeation rate can vary based on the polymer’s structure, with amorphous polymers typically having higher permeability compared to crystalline ones. Gas permeation is a key consideration in applications like gas storage and delivery, where polymers need to have low gas diffusion/permeability to avoid leakage and maintain system integrity.
Meanwhile, gas sensors are vital for accurately detecting specific gas concentration and leakage across applications where gas is produced, stored and used, such as fuel cells, storage facilities and transportation systems [
56,
57]. These gas sensors are developed based on different sensing principles, each with its own advantages and limitations. Infrared (IR) gas sensing [
58-
60] works on the principle that gas molecules absorb infrared light at specific wavelengths. The intensity of absorbed light is measured and correlated to concentration of the corresponding gas. The main advantages of IR gas sensing include high sensitivity, selectivity and ability to detect gases over a wide range of concentrations. However, it could be affected by environmental conditions including temperature and humidity and may require regular calibration for accurate measurements.
Semiconductor gas sensors [
61-
63] operate based on the principle that gas molecules interact with the surface of a semiconductor material (Typically Metal Oxides), causing a change in its electrical resistance. The change in resistance is measured and intercorrelated to the concentrations of the target gas. The advantages include low cost, fast response and small size. However, they can be influenced by factors like temperature, pressure and humidity and may exhibit cross-sensitivity to other gases, reducing accuracy.
Catalytic combustion gas sensors [
64-
66] operate by detecting gases through the catalytic oxidation of the target gas on a heated catalyst surface, which generates heat. This heat change is measured and used to determine the gas concentration. The advantages include high sensitivity to combustible gases and reliability in detecting flammable gases at low concentrations. However, they have a limited lifespan, especially in the presence of poisons like silicone or lead. The sensors may require regular maintenance to ensure the accurate performance.
An optical spectroscopy gas sensor [
67-
69] operates based on the principle that gas molecules absorb or emit light at specific wavelengths. When light passes through a gas sample or is reflected from it, the gas molecules absorb light at characteristic absorption bands corresponding to their molecular structure. The amount of absorbed light is then measured, which is correlated to concentrations of the gas. Key features of optical spectroscopy gas sensors include high sensitivity, non-destructive measurement and ability to detect low concentrations of gases with high accuracy. These sensors are capable of detecting wide ranges of gases and are immune to interference from most other substances. However, they may be affected by environmental factors like temperature, pressure and the presence of other gases in complex mixtures.
An electrochemical gas sensor [
70-
72] operates by detecting gases through a chemical reaction between the target gas and the electrodes in an electrolyte. This reaction produces electrical currents proportional to concentrations of the gas, which is then measured and used to determine the gas level. The advantages of electrochemical sensors include high sensitivity, low power consumption, and good selectivity for specific gases. However, they could be influenced by factors like temperature and humidity and their lifespan may be limited due to the degradation of the electrodes or electrolyte over time.
Finally, gas chromatography [
73-
79] and mass spectrometry [
80-
82] provide highly precise analysis and commonly used in research and laboratory settings. Gas chromatography separates and analyzes individual components in gas mixtures, while mass spectrometry identifies gas molecules based on their mass after ionization. However, these sensing systems are expensive and require regular maintenance, making them unsuitable for real-time field monitoring.
The conventional gas sensing technologies provide precise measurements but face challenges in specimen size, sensitivity, selectivity and environmental stability. These limitations highlight the need for advanced gas sensors that are compact, have rapid response times, high sensitivity and robust performance across variable field conditions to ensure safety in real-time gas monitoring.
Thus, we have developed two types of gas sensors with the performance to meet these requirements. First, a sensor system utilizing a volumetric measurement (VM) method based on the image processing algorithm is developed [
5,
83]. This system aims to provide the real-time monitoring by connecting to a computer via a GPIB interface and using a diffusion analysis program to accurately measure gas concentration/diffusion in the polymer specimen with the insensitivity to temperature/pressure changes.
Second, a simple and effective gas detection sensor based on a manometric measurement (MM) method was developed using the portable data logger with USB type to measure and record pressure/temperature in a sample container and a diffusion analysis program [
84-
86]. This portable detection system can easily measure gas concentration and diffusion from the polymer samples in real-time on-site without any chemical interactions with gas.
It was demonstrated that the developed two gas sensor systems have the versatility to detect and characterize various gases like H2, He, N2, O2, and Ar, effectively sensing gas adsorption and diffusion in polymer materials in real-time. The sensor has shown reliable performance in sensitivity, stability and response time. The sensor technology presented in this study offers a compact and portable solution capable of replacing large-scale equipment. It has potential applications not only in hydrogen infrastructure safety management but also in the gas industry for real time gas monitoring. We compare the principles, procedures, results and characteristics of each method. Ultimately, two developed gas sensing methods provide valuable insights into the gas transport properties, leakage and sealing capabilities of O-rings under high-pressure conditions. They are applicable in hydrogen fueling stations and the gas industry, enhancing safety and enabling real-time monitoring.
2. Experimental Procedure
2.1 Specimen Preparation and High-pressure Gas Charging
This developed gas sensor is applied to measure gas concentration and diffusion coefficient from polymer specimen during the desorption process of gas charged to high pressure. Polymer specimen used is low-density polyethylene (LDPE). LDPE is widely used for manufacturing containers and gas transport pipes. It is known as its gas-barrier properties when coated. LDPE is used as an O-ring seal material in high-pressure gas chambers. The developed gas detection system allowed us to determine the permeation properties (Solubility, Diffusion Coefficient and Permeability) of polymer samples.
The composition and density details of the polymer sample can be found in prior literatures [
3,
86]. The polymer sample were prepared with the following cylinderical shapes and dimensions:
- LDPE : radius (R) 9.51, thickness (T) 4.89 and 1.57 mm
For high-pressure gas charging, we used a stainless steel 316 chamber at room temperature and desired pressure conditions. Gas charging was conducted at pressure of 5 MPa. The purity of the gases used was as:
• H2: 99.99%, He: 99.99%, N2: 99.99%, O2: 99.99%, Ar: 99.99%
Samples were then charged to the gas at the specified pressure for 24-48 hours. A 48 hours gas charging was sufficient to reach the equilibrium for gas absorption into specimen.
2.2 Volumetric Measurement of the Released Gas from Charged Polymers
A volumetric measurement technique to assess gas diffusion and permeation is developed. This method involves measuring the concentration of gas released from a specimen after charging to high pressure (HP) and decompression.
Fig. 1 illustrates a volumetric analysis system used to quantify the released gas at a room temperature. The system consists of a high-pressure chamber for gas charging and a cylinder immersed in a water container.
Fig. 1Volumetric sensor system to measure the gas uptake and diffusivity emitted by a specimen after charging to HP gas. (a) Specimen charged to gas in a HP chamber. (b) After decompression in the chamber, the specimen was loaded into a graduated cylinder. The cylinder was partially immersed in a water container and gas emission measurements were performed. The ● in cylinder represents the gas emitted from the charged sample
After charging to high-pressure gas and decompression, the specimen was placed in the upper air space of a graduated cylinder, as depicted in
Fig. 1. The gas released from the specimen caused a gradual decrease in the water level within the cylinder. Consequently, the pressure (P) and volume (V) of the gas inside the cylinder varied with time.
The gas within the cylinder adheres to the ideal gas law, expressed as PV = nRT, where R is the gas constant (8.20544 × 10
-5 m³·atm/(mol·K)), T represents the gas temperature inside the cylinder, and n denotes the number of moles of gas released into the cylinder. The variations of pressure P(t) and volume V(t) of the gas in the cylinder can be described as follows [
87]:
where
Po represents the external pressure surrounding the cylinder, g is the gravitation acceleration, and ρ signifies the density of distilled water. The
h(
t) describes the water level within the cylinder over time, while
Vo is the combined volume of gas and water inside the cylinder, measured relative to the water level in the container.
Vh(
t) indicates the time-dependent volume of water in the cylinder, and
Vs represents the volume occupied by the sample. The amount of gas released by the polymer specimen was quantified by tracking the water level position [
Vh(
t)] over time. Consequently, the total moles of gas emitted [
n(
t)] were calculated by measuring the total gas volume [
V(
t)] in the graduated cylinder, which corresponds to the decrease in the water level, as expressed by the following [
87]:
Here, T0 and P0 represent the initial temperature and pressure of the gas in the cylinder, respectively. V(t) is the total volume, consisting of the remaining initial air volume (VA) and the released gas volume [VH(t)], so that V(t) = VA + VH(t). nA denotes the initial mole number of air and nH(t) refers to the time-dependent mole number of gas corresponding to the increase in gas volume due to its release. Therefore, nH(t) was converted to the gas concentration, [C(t)] emitted per unit mass from the specimen as :
For instance, the molar mass of hydrogen gas,
mH2 [
g/mol] is 2.016 g/mol. The molar mass of nitrogen gas
mN2 [
g/mol] is 28.013 g/mol.
msample is the specimen mass. In
Eqs. (2) and
(3), the time-dependent mole number of gas,
nH(
t), was converted to the gas mass concentration, [
C(
t)], by the factor,
k=mGasmsample ⋅nH(t) and
C(
t) are affected by the fluctuations of temperature and pressure in the laboratory environments. To ensure precise measurements, it's essential to compensate for these variations. This compensation can be achieved through automated programs according to
Eq. (3). That is., the terms,
V(
t)(
β(
t)-
α(
t)), indicates the volume change in the
VH(
t), caused by the temperature and pressure variations. The compensation indicates the application of (
t)(
β(
t)-
α(
t)) calculation in
Eq. (3). Thus, the insensitivity of the sensor to variations in temperature and pressure means the application of automatic compensation by the program.
The release of gas was tracked by monitoring changes in water level measurement using image processing algorithm via digital camera in front of the graduated cylinder. The procedure for obtaining the water level (Emitted Gas Volume) from water level measurement is described in previous works [
5,
83].
Fig. 2 illustrates the schematic of the manometric measurement sequence used to determine the concentration and diffusivity of the released gas from specimen at 298 K. The setup includes a highpressure chamber for the gas charging as shown in
Figs. 2(a), a rectangular specimen container equipped with a commercial data logger with USB type and rubber seal in 2(b). The ELP sensors, which were used to measure pressure and temperature, are commercial data loggers capable of simultaneously recording both atmospheric pressure and temperature.
Fig. 2Illustration of manometric sensor system for measuring gas uptake and diffusion coefficient from charged sample using a commercial pressure/temperature logger after high-pressure charging and decompression. (a) The sample charged to gas in the high-pressure chamber. (b) After decompression of the chamber, the charged sample loaded in the rectangular specimen container. Gas emission measurements were carried out using a data logger within the sample container. The ● in specimen container represents the gas emitted from charged sample
After the charging and decompression in the stainless steel chamber, the specimen was transferred into the rectangular specimen container shown in
Fig. 2(b). As the gas realeased from the sample, the pressure inside the vessel increased with elapsed time. Consequently, both the pressure (
P) and temperature (
T) of the gas within the specimen container changed as time progressed. The gas inside the container followed the ideal gas law:
PV =
nRT,
R is the gas constant with 8.20544 × 10
-5 m³·atm/(mol·K), and
n represents the number of moles of the released gas molecules inside the specimen container.
The mole number of gases emitted from charged specimen is obtained by measuring the increase in pressure [
P(
t)] versus time by manometric measurement at a constant container volume. Thus, the total number of moles [
n(
t)] obtained by measuring the increased gas pressure [
P(
t)] due to emitted gas in the cylindrical container is described as [
3,
86]:
nt=PtV0RTt=PtV0RTt=[P0+ΔPt]V0RT0[1+αt]≅PoV0+ΔPtV0RT0[1+αt]=n0+Δtt,with n0=P0V0RT0,Δnt=V0RT0[ΔPt-αtP0-αtΔPt]
where
T0,
V0 and
P0 are the temperature, initial volume and initial pressure of the air at initial time inside the cylinder with the sample, respectively.
P(
t) is the sum of remaining initial air pressure (
Po) and time-varying released gas pressure [Δ
P(
t)] from specimen, i.e.,
P(
t) =
Po + Δ
P(
t),
n0 is remaining initial air mole, and Δ
n(
t) is the time-varying gas mole corresponding to gas pressure increase by the released gas.
α(
t) is the change rate of temperature with respect to
T0. Thus, Δ
n(
t) is transformed into the released gas concentration [Δ
C(
t)] per mass for specimen as [
86]:
where
mg[
g/mol] is molar mass of the gas used; for H
2,
mH2 [
g/mol] = 2.016 g/mol and for N
2,
mN2[
g/mol] = 28.001 g/mol; and
mspecimen is sample mass. First term, Δ
P(
t) in
Eq. (5), is the increase in pressure that is emitted gas from sample. The second term, -
α(
t)
P0, is the pressure change caused by temperature variation [
α(
t)]. The third term,
α(
t)Δ
P(
t), is the pressure change due to both temperature variation [
α(
t)] and pressure increase [Δ
P(
t)].
According to
Eqs. (4) and
(5), the time-varying gas mole, Δ
n(
t), is transformed to gas mass concentration, [Δ
C(
t)], by
k=mgmspecimen . Δ
n(
t) and Δ
C(
t) are affected by both temperature and pressure variations. Thus, we have compensated for the variations caused by changes in temperature and pressure.
Released gas concentration from the gas-charged sample follows Fickian diffusion. Thus, the concentration of released gas,
CE(
t), is calculated as follows [
88,
89]:
where βn represents root of zeroth-order Bessel function, J0(βn). This equation corresponds to solution of Fick’s second diffusion equation for a cylindrical shaped specimen. CE(t = 0) = 0 and CE(t = ¥) = C∞ is saturated gas concentration at infinite time, indicating total gas uptake (Emission Content). D is the gas diffusivity. l and ρ are thickness and radius of cylindrical sample, respectively.
For the exact calculation by
Eq. (6), many terms in the product of two summations are contained. Therefore, dedicated analysis program is developed that calculates precisely
C∞ and
D. With an analysis program based on an optimization algorithm [
90], we accurately calculate
CE(
t) and
D from the measured result by solving the
Eq. (6).
3. Results and Discussion
3.1 Volumetric Measurement
After decompressing a specimen charged with corresponding gas under high pressure, the released gas concentration and diffusivity were determined using the VM method with a graduated cylinder (
Fig. 1). The water level in VM method is measured by employing image processing algorithm and a digital camera [
83].
Fig. 3 displays the measured and fitted results for five gases in cylindrical LDPE determined from the water level measurement by VM. The left sides of
Figs. 3(a)-3(e) show corresponding emitted gas volume (Filled circle) transferred from water level measurement. The right sides of
Figs. 3(a)-3(e) represent corresponding gas emission data (Open square). The diffusion parameters, and
C∞, are derived using an analysis program by
Eq. (6). The fitting line in right side is fitted result using
Eq. (6), with diffusivity (D) and the total gas uptake (
C∞) marked by an arrow. As shown in
Figs. 3(a)-3(e), single mode gas emission behaviors for all gases in LDPE were observed under time depending gas emission measurement. The single-mode gas emission in LDPE results from gas diffusion into the amorphous phase.
Fig. 3Gas uptake and diffusivity determined from five gases in a cylindrical LDPE specimen by volumetric measurement using image processing algorithm and a digital camera. (a-e): Measured gas volume (Filled circle) transformed from the measured water level and emitted gas emission (Open square) transferred from measured gas volume in unit of wt·ppm. The fitting line represents the fitted result using Eq. (6). Diffusivity parameters, D and C∞, is calculated by an analysis program based on Eq. (6). Here, R is radius of cylindrical specimen. T is thickness of cylindrical specimen
3.2 Manometric Measurement
After decompressing a specimen charged with hydrogen under high pressure, the released gas concentration and diffusivity were determined using the MM method for specimen loaded in the cylinder-shaped container (
Fig. 2). The water level in MM method is measured by employing commercial USB-type manometer.
Figs. 4(a)-4(e) display the measured and fitted results for five gases in cylindrical LDPE determined from the water level measurement by MM. The left and right sides of
Figs. 4(a)-4(e) represent emitted gas volume transferred from water level measurement and gas emission content, respectively. The right sides of
Figs. 4(a)-4(e) represent the diffusion parameters,
D and
C∞, derived using a diffusion analysis program by
Eq. (6). The fitting line in right side is fitted data using
Eq. (6), with gas diffusivity and the total gas uptake marked by an arrow. In similarity with
Fig. 3, a single-mode gas emission behaviors for all gases in LDPE were also observed under time varying gas emission measurement in
Fig. 4.
Fig. 4Gas uptake and diffusivity determined from five gases in a cylindrical LDPE specimen by manometric measurement using data logger. (a-e): Measured gas volume (Filled circle) transformed from the measured water level and emitted gas emission (Open square) transferred from measured gas volume in unit of wt·ppm. The fitting line represents the fitted result using Eq. (6). Diffusivity parameters, D and C∞, is calculated by an analysis program based on Eq. (6). Here, R is radius of cylindrical specimen. T is thickness of cylindrical specimen
Moreover, solubility (S) is obtained from gas uptake versus pressure from
Figs. 3 and
4 as follows [
84,
91-
93]:
mg is molar mass of the charged gas and d is density of the sample. The solubility and diffusivity in two sensors determined for H
2, He, N
2, O
2 and Ar gases in LDPE sample are shown in
Tables 1 and
2, respectively.
Table 1Summary for solubility and diffusivity of five gases measured by VM and MM in LDPE
Table 1
|
Sensing method |
Solubility [mol/m3·MPa] |
Diffusion coefficient [×10-11 m2/s] |
|
H2
|
He |
N2
|
O2
|
Ar |
H2
|
He |
N2
|
O2
|
Ar |
|
VM |
5.83 |
1.78 |
8.45 |
15.69 |
19.46 |
23.39 |
52.92 |
2.12 |
3.40 |
2.99 |
|
MM |
6.00 |
1.99 |
7.58 |
15.55 |
18.93 |
24.12 |
60.30 |
2.40 |
3.37 |
2.81 |
In
Table 1, the solubility and diffusion coefficient in two specimens for two sensors have 10 % relative expanded uncertainty for measured value. The solubility and diffusion coefficient results obtained from both the VM and MM were consistent within the estimated relative uncertainty.
We have evaluated the performance of two gas sensing system using volumetric image sensor and manometric data logger sensor. The results of the performance tests are represented in
Table 2, covering sensitivity, resolution, stability, measurable range, response time and figure of merit (FOM). Sensitivity in VM and MM sensor is defined as the mass concentration change relative to the change in measured volume and measured pressure, respectively. The obtained sensitivities were 16.43 wt·ppm/mL for the VM sensor and 11.96 wt·ppm/hPa for the MM sensor. A sensor with higher sensitivity typically provides better resolution. For the VM sensor, the resolution is reflected by the minimum measurable volume of 0.005 mL, corresponding to a mass concentration of 0.08 wt·ppm. For the MM sensor, the resolution is reflected by the minimum measurable pressure of 0.01 hPa, corresponding to a mass concentration of 0.12 wt·ppm. To improve resolution further, it is possible to reduce the inner volume of the graduated cylinder and the sample container or increase the number of specimens. This adjustment would lead to better sensitivity and resolution.
Table 2Performance comparisons for two sensor systems with volumetric and manometric methods
Table 2
|
Performance |
Volumetric measurement |
Manometric measurement |
|
Sensitivity |
16.43 [wt·ppm/mL] |
11.96 [wt·ppm/hPa] |
|
Resolution [wt·ppm] |
0.08 |
0.12 |
|
Stability [%] |
0.2 |
0.2 |
|
Measuring range [wt·ppm] |
Max. 1,400 |
Max. 1,500 |
|
Response time [s] |
~1 |
~1 |
|
FOM [%] |
0.4 |
0.7 |
The stability of two sensor systems is quantified by the standard deviation of measurements taken over 36 hours after gas emission from the specimen ceased. This was found to be less than 0.2% of the mass concentration for both sensors. The measurable range in VM sensor is obtained as the maximum allowable concentration per mass of specimen within graduated cylinder with inner volumes. The measurable range in MM sensor is determined as the maximum allowable concentration per mass of specimen within a specimen container with inner volumes. For both the sensors, the measurable range was 1,400 wt·ppm for VM sensor and 1,500 wt·ppm for MM sensor, which can be adjusted by varying the sample mass, cylinder volume and specimen container volume. The gas sensor’s volume and pressure response are almost instantaneous, occurring within ~1 second of gas emission. The figure of merit (FOM) is defined as the standard deviation between measured data and the theoretical value calculated using
Eq. (3). An FOM value is below 0.4% for VM sensor and 0.7% for MM sensor, indicating good agreement between the measured and theoretical values. Based on the performance testing, the specifications (Sensitivity, Resolution and FOM) of VM sensor are superior to MM sensor.
4. Conclusion
Gas sensors are crucial for ensuring safety and protecting property in gas-related facilities. We have developed two gas sensing systems that utilize volumetric measurements with a graduated cylinder, coupled with an image processing algorithm and a digital camera. The variation in the water level, observed through pixel shifts in the graduated cylinder, is directly linked to changes in water volume caused by the released gas, allowing for precise measurement of gas concentration. By integrating a diffusion-permeation analysis program, this volumetric image-based gas sensor is capable of detecting not only gas concentrations but also solubility/diffusivity from gas-charged specimens under high-pressure conditions.
A straightforward manometric gas sensor was also developed for characterizing gas behavior. The method relies on pressure measurements within a gas charged sample container, utilizing a commercial data logger. The system measures the pressure increase caused by the gas released from high-pressure polymer samples, enabling the determination of gas concentration and solubility/diffusivity by a diffusion analysis program.
The two portable gas sensor systems showcased several key performance metrics: a low detection limit for gas content, a measurable range of up to 1,500 wt·ppm, stability of 0.2%, and a rapid response time within one second. Additionally, the sensors' insensitivity to temperature and pressure fluctuations made them highly reliable for gas detection. The sensing systems, utilizing both volumetric and manometric measurements, successfully demonstrated real-time monitoring and characterization of pure gases such as H2, He, N2, O2 and Ar. The sensors effectively measured gas uptake and diffusivity, considering influencing factors and calculating expanded uncertainty. In conclusion, the main features of the two developed gas sensing methods are summarized as follows:
- Cost-effective and simple techniques: The two methods provide affordable and straightforward solutions for evaluating gas uptake and diffusion coefficient in gas charged polymers under high-pressure.
- Stability against temperature and pressure variations: Both methods are stable under fluctuations in temperature and pressure. Two sensors are independent on a specimen sizes, shapes and gas types.
- Adjustable sensitivity and range: The volumetric and manometric methods offer flexible sensitivity, resolution, and measurement range, allowing for customization based on specific application requirements.
- No chemical interaction: Both sensing methods function without any interaction between the gas molecules and the sensor, ensuring accurate measurements without altering the composition of the gas.
- Visible gas release monitoring: The volumetric method provides visual gas monitoring of gas release by changes in water level.
These two complementary sensing methods are highly effective for measuring gas transport properties in sealing elastomers and can be applied to assess the permeation characteristics of rubber materials and O-rings under high-pressure conditions. They are particularly well-suited for applications in hydrogen fueling stations. The results from both sensing methods demonstrated consistent measurements of gas solubility and diffusivity, with a comprehensive review of their characteristics and performance, ensuring their reliability and applicability in the field.
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Biography
- Ji Hun Lee
Ph.D. candidate in Korea Research Institute of Standards and Science (KRISS). His research interest is polymer materials in hydrogen energy.
- Sang Koo Jeon
Senior researcher in Korea Research Institute of Standards and Science (KRISS). His research interest is polymer materials in hydrogen energy.
