1. Introduction
Nanoparticulate matter among air pollutants is a growing environmental concern worldwide. A data book on automotive particulate matter (PM) reduction published by the National Assembly of the Republic of Korea indicates that diesel vehicles account for 29 percent of the total PM emissions in the Seoul Metropolitan Area, followed by construction equipment (accounting for 22 percent). These results signify that diesel engines are responsible for more than half of PM emissions in the Seoul Metropolitan Area [
1]. A few years ago, research studies reported poorer performance of the after-treatment device due to an increase in the driving mileage of in-use vehicles [
2,
3]. Furthermore, concerns are being raised over air pollution triggered by aged diesel vehicles and construction equipment without after-treatment devices. Against this backdrop, stronger controls and regulations are being imposed, as manifested in the following measures. Firstly, government-backed projects for attaching after-treatment devices, such as the diesel particulate filter (DPF), to aged diesel vehicles are being pursued. Secondly, retrofit attachment projects of PM-NOX simultaneous reduction devices for Euro-4 heavy-duty diesel vehicles or those subject to lower standards are being done. Lastly, maintenance regulations for diesel vehicles are being enforced [
4].
The DPF is a device that prevents PM from being exhausted into the atmosphere by filtering the matter generated from diesel vehicles, and the substrate inside the DPF serves as a filter. Once a certain amount of soot is accumulated after being filtered by the substrate, the soot regeneration process takes place. However, when the substrate is aged, it may be internally damaged due to various reasons, such as thermal stress occurring during the regeneration process, vibrations generated while driving, and increasing back pressure caused by the loaded PM [
5,
6,
7]. Damage on the substrate leads to a lower filtering performance, resulting in excessive PM emissions. As a prevention measure, DPFs must be checked on a regular basis, and such a periodic inspection of in-use vehicles typically assesses the status of and maintains the DPF by measuring the smoke concentration of diesel vehicle emissions. To evaluate the status of the DPF, a measurement of the smoke concentration and an on-board diagnostics (OBD) test are carried out, and a visual test is executed after removing the DPF from the vehicle in case the smoke concentration exceeds the regulation standards. However, the visual test after the removal has limitations, such as its long duration and difficulties in identifying the internal problems of the substrate.
Nondestructive testing using the X-ray imaging technique is deemed as a valid alternative to overcome such limitations. Nondestructive testing utilized for the DPF include ultrasonic testing and neutron radiographic testing, other than radiographic testing [
8,
9,
10]. Ultrasonic testing detects a change in the density using signals. However, in case it is difficult to conduct an accurate check, the pertinent part is removed, and liquid is inserted for further analysis. Therefore, the liquid makes the testing technique an invalid approach to see if soot and ash are accumulated. Neutron radiographic testing, a testing technique more sophisticated than the radiographic one, shows outstanding transmittance. However, it is expensive and sensitive to safety, as it is used as equipment specifically for large reactors, posing difficulties in taking a measurement for the after-treatment device.
Radiographic testing usually uses three types of X-ray detection methods in medical institutions. Firstly, in the analog method, an X-ray film is used as a detector. However, after taking an X-ray, a liquid is required to develop the film, and the development process takes a lot of time. In addition, the film must be replaced after each imaging, and it is impossible to transfer the image to a computer. Therefore, the analog method is rarely used nowadays. Secondly, there is the digital radiography (DR) method, in which a flat panel detector (FPD) is used. After taking an X-ray, it can be transferred to a computer within a few seconds without a separate process, and additional image processing is possible. Furthermore, it is possible to obtain excellent images even with a lower radiation dose compared to the analog method. However, the equipment is expensive, and the digital FPD is sensitive to handling. Accordingly, there is a high risk of damage to the FPD when used as a target for mechanical devices. Thirdly, the computed radiography (CR) method is easily understood as a combination of analog and DR. The CR method is used an imaging plate (IP) as a detector. After taking an X-ray, when IP is inserted into the CR reader, the image is transmitted to the computer through the image processing process. CR transmits images faster than analog but slower than DR. Nevertheless, in the same way as DR, CR can also be transmitted to a computer for additional image processing. In addition, the CR is lower than DR in investment cost, and the IP detector is easier to manage than FPD, so it can be used for various purposes. For comparison, the characteristic comparison table of the X-ray detection methods is shown in
Table 1, and the workflow of the X-ray detection methods is shown in
Figure 1.
Besides that, there are computed tomography (CT) X-ray methods. Since the CT X-ray method takes 360° of an object, it is possible to obtain an accurate image. Therefore, Waseda University and the National Institute of Advanced Industrial Science and Technology in Japan conducted a study on the transfer and accumulation of ash based on images taken using the CT X-ray imaging technique (
Figure 2) [
11,
12]. Furthermore, Korea University identified the length and shape of ash employing the CT X-ray imaging technique (
Figure 3) [
13]. However, CT X-ray equipment is expensive, and removal is inevitable when taking DPF. Accordingly, the CT X-ray method takes a lot of time to take a DPF. On the other hand, the DPF installed under vehicles was estimated to be able to take an image in a short period of time using portable CR X-ray equipment and flexible IP without its actual removal. Accordingly, a study was conducted to measure the damaged DPF using the CR X-ray imaging technique [
14]. As the CR X-ray imaging technique photographs an object unidirectionally, there are no research studies applying the technique on vehicles, as it has limitations in obtaining a highly clear image required to identify characteristics of ash accumulation on each channel of the substrate. In this study, Image J software (capable of image processing and analysis) was used, and the accumulation of soot and ash was analyzed based on the pixel values obtained through the histogram function.
3. Test Results and Observations
3.1. Accumulation of Carbon Powder and Ash Powder
A test was carried out to check if the ash was accumulated inside the DPF substrate, as it could increase back pressure, reducing the power and specific fuel consumption of an engine as well as affecting the durability of the substrate. As there is not only ash but soot inside the substrate, carbon powder, similar to soot, and ash powder were placed on the new substrate to see if they were accumulated based on a comparison of pixel values.
3.1.1. Results from Images of Substrate with Accumulated Carbon Powder
The maximum allowable quantity of soot was assumed to be 6 g/L (mass per volume of substrate) before regeneration, and the volume of the substrate used in the test was calculated to be about 4.12 L based on the standard [
16]. Therefore, the maximum allowable quantity of soot in the entire substrate was estimated to be 24.72 g, which was rounded up to 25 g for the convenience of the testing. In this study, contents of carbon powder, which is similar to soot that is accumulated in the substrate, in six different quantities were compared by taking an X-ray. The images of the substrate in these six different conditions are shown in
Table 5.
New substrate (0 g): The new substrate has nothing accumulated inside.
Accumulation 12.5 g: 50% of the maximum accumulated quantity is accumulated in the substrate.
Accumulation 25 g: The maximum accumulated quantity of substrate.
Accumulation 62.5 g, 100 g, and 125 g: Excessively accumulated quantity setting for better visual observation.
In the case of
Table 5a, showing the new substrate, the plug on the inlet and the outlet appeared white. As for
Table 5b, displaying the substrate with 12.5 g of carbon powder, an area appearing extremely pale white on the upper part of the plug was witnessed as carbon powder was accumulated on the outlet of the substrate.
Table 5c, with an image of the substrate with 25 g of carbon powder, shows a larger area colored pale white. In cases of
Table 5d, with the substrate with 62.5 g of the powder,
Table 5e, with 100 g, and
Table 5f, with 125 g, it was visually observed that carbon powder, accumulated in the shape of a mountain on the outlet of the substrate, appeared in pale white.
3.1.2. Analysis of Images of Substrate with Accumulated Carbon Powder
As the area where carbon powder was accumulated was shown in extremely pale white on the images, it is not easy to visually determine whether it was actually accumulated. For this reason, an analysis was attempted to check the accumulation status with the pixel values after setting the center of the outlet of the substrate as the ROI with Image J and comparing the values with those of the new substrate (
Figure 7a). Before setting the ROI, it was identified through Image J that the resolution of each carbon powder image was 1430 × 1722 pixels. The identical location and size (300 × 240 pixels) of each image were set as ROI, and the average pixel value and the standard deviation data were produced using the histogram feature (
Figure 7b).
The data are given in
Figure 8 and
Table 6. The gap between the pixel value of the substrate with 12.5 g of carbon powder, whose accumulation was dimly visible on the image, and that of the new substrate was 8.503, which is deemed valid, given the standard deviation of the pixel value. The larger the accumulated quantity becomes, the higher the gap with the pixel value of the new substrate gets, indicating that it is possible to analyze the accumulation status.
3.1.3. Results from Images of Substrate with Accumulated Ash Powder
X-ray images of the substrate with ash powder in four different quantities—12.5 g, 25 g, 100 g, and 125 g—were taken to compare their pixel values with those from the images of carbon powder accumulation, and they are shown in
Table 7. As for
Table 7a, depicting the substrate with 12.5 g of ash powder, the plug and the upper part of the plug are shown in white more than those in
Table 5a, displaying the new substrate due to the accumulation of ash powder. In the case of
Table 7b, with 25 g of ash powder, the area accumulated with ash powder on the outlet of the substrate appeared white clearly and was easily observable. Even in
Table 7c, with 100 g of ash powder, and
Table 7d, with 125 g of ash powder, both of which were excessive in quantity, the accumulation status was easily visually identifiable.
3.1.4. Analysis of Images of Substrate with Accumulated Ash Powder
The resolution of each ash powder image was identified to be the same 1430 × 1722 pixels as the carbon powder images. In addition, pixel values, shown in
Figure 9 and
Table 8, were obtained through histograms by setting the same ROI as in the analysis on the images of carbon powder accumulation. The gap between the pixel value of the substrate with the least accumulated ash powder of 12.5 g and that of the new substrate was 18.998, which is deemed valid considering the standard deviation. Therefore, it is confirmed that it is also possible to analyze the status of ash accumulation, as with carbon powder accumulation.
3.2. Comparison between Pixel Values of Carbon Powder and Ash Powder
A comparison between the images of carbon powder accumulation and those of ash powder accumulation through a visual observation indicated that the area of accumulated ash appeared relatively whiter (
Table 9). A graph comparing an increase in pixel values upon the accumulation of carbon powder and of ash powder, measured at the same ROI, is given in
Figure 10. As for the images of ash powder, when the accumulated quantity gets higher, the pixel value dramatically increases. Ash consists of elements with higher atomic numbers than carbon, as they are generally derived from engine oil. Therefore, it is denser than carbon powder, resulting in a lower X-ray transmittance, which leads to an assumption that a certain area appears whiter in the images.
It is confirmed that it is possible to analyze the accumulation status through CR X-ray imaging when ash is accumulated on the substrate. Therefore, it is deemed possible to observe the accumulation of ash remnants after the regeneration process by taking a CR X-ray to the DPF equipped with a canister. As for the PM accumulation, it is estimated to be difficult to tell whether it is accumulated through a visual observation as it is mainly made of carbon; however, it is possible to conduct an analysis based on pixel values.
3.3. Summary of Verification Results and Observations
It is confirmed that the area accumulated with carbon powder or with ash powder appeared white based on CR X-ray images and that the color of the area of accumulated ash powder was whiter. In addition, it is verified that it is possible to analyze the accumulation status by comparing pixel values produced by Image J. Therefore, this study shows that it is confirmed to be technically possible to diagnose the accumulation status of soot and ash using the CR X-ray imaging technique and Image J. However, although the qualitative evaluation through CR X-ray images has been sufficiently proven, the numerical values obtained through Image J are only pixel values, so it is not enough to be called a quantitative evaluation. In order for the pixel values obtained to be demonstrated by quantitative evaluation, additional studies are needed, such as uncertainty analysis. In addition, as the substrate without canister was photographed, research is necessary to analyze whether soot and ash are accumulated in the DPF of in-use vehicles, and more thought should be given to the adaptability of the technique.
In recent years, various radiation studies have been conducted, including experiments to evaluate X-ray-radian and gamma-radian-based systems using Monte Carlo radiation transmission tools [
17,
18,
19,
20]. The CR X-ray imaging technique is expected to make contributions to the environment by diagnosing whether a DPF is damaged and detecting illegal remodeling at vehicle inspection stations. It is also expected to be used for various purposes, such as for DPF cleaning shops and retrofit manufacturers to determine whether the DPF is sustainably usable after a cleaning process or needs to be repaired. As portable X-ray systems and flexibly bendable IP are produced and sold in mass quantities, the technique is deemed easily accessible.