Analysis for Adsorbed Odor from Car Air Conditioner Evaporator Kazuhisa Uchiyama*, Osamu Kasebe**, Kengo Kobayashi***, Shigeyuki Sato****, Hiroshi Ito***** DENSO CORPORATION 1-1 Showa-cho Kariya-shi Aichi 448-8661 JAPAN *[email protected], **[email protected], ***[email protected] TOYOTA CENTRAL R&D LABS., INC. 41-1, Aza Yokomichi, Oaza Nagakute, Nagakute-cho, Aichi-gun, Aichi-ken, 480-1192, JAPAN **** [email protected], ***** [email protected] Abstract: As one of measures to improve the environment in a car, we have decreased the foul odor and the dusty odor caused by the car air conditioner evaporator. However, the problem with adhesive odor is still left unresolved. We analyzed the odor from cars with a sensory test and instrumental analysis. And we simulated the odor with an evaporator desktop test bench with airflow controller, air temperature and humidity controller for testing odor from an evaporator. We proved that the odor is composed mainly of substances from exhaust gas, tobacco smoke and others. We found, (a) three principal components of adhesive odor with PCA (principal component analysis), (b) a close correlation between odor sensory test data and instrumental analysis data with multivariate analysis, and (c) specified main odor substances (ex. Lower fatty acids, Hydrocarbons and Aldehydes). These odor substances tend to become noticeable while the air conditioner is operated with the compressor turned on and off. This operating pattern is increasingly used recently for energy saving purpose. With the evaporator desktop test bench, we found that hydrophobic odor substances (ex. Toluene) are released while evaporator’s surface is changing from ‘Dry’ to ‘Wet’ (temperature falls down and flocculated water breaks out on the surface). And while changing from ‘Wet’ to ‘Dry’, the flocculated water vaporizes and hydrophilic odor substances (ex. Lower fatty acids) come up together. Consequently we have identified the components of inherent odors that smell while H2O is condensing and vaporizing (= the compressor is turned on and off). And we clarify the odor generation mechanism from an evaporator surface. Key words: Air Conditioning, Human Engineering, Evaporator, Odor 1. Introduction Heater core For the past several years, we have been trying to minimize the odor emitted from the car air conditioner evaporator (Fig.1). As the user's odor tolerance threshold becomes lower, on the other hand, an unpleasant odor is still emitted from the source of components collecting even after Blower Evaporator Fig.1 Car Air Conditioner System and Evaporator the current surface treatment capable of controlling an "uncomfortable odor" caused by bacteria and a "dusty odor" resulting from corrosive products on the evaporator (Fig.2). An odor from the evaporator surface-treated in the current process was traced by means of monitored vehicles on a continuous basis. One of the 23 users of the monitored vehicles made a complaint about an annoying "odor" in five months after the start of monitoring. In contrast, four of the 23 users made a complaint Odor Type indicated a different type of odor unlike the uncomfortable odor or dusty odor. In addition, we counted the bacteria on the surface of six units including these two and found out that the number Resin Reacted Layer ? Chromate Layer Bacteria Counter -measure Adsorption and Desorption of Odor Al(OH) 3 Odor Mechanism Sweat,Tobacco Dusty Growth of Bacteria Cause in ten months. A check for any odor from two of these units Rotten Odor Evaporator Evaporator Biocide New Coating Odor Evaporator Filter Fig.2 Odor of Car Air Conditioner was below the odor-emitting minimum level, presenting no problem. We thereby cleaned up the two evaporators so as to remove the collecting foreign material to a completely acceptable "odor" level and noticed that these odors were caused by the collecting components, resulting in "adsorbed odors". And when the compressor is set in control mode Normal Pattern intended for saving energy as currently observed, such Comp ON OFF rising or lowering on the surface of the evaporator. Evaporator Temp. The purpose of this study is to identify the ON Comp OFF an odor would be enhanced in addition to temperature (Fig.3) No Odor An Example of Eco-mode Pattern causative substance of such an "odor" possibly resulting from the components accumulating on the surface of the evaporator and determine the odor Wet to Dry Evaporator Temp. mechanisms components through the analysis, clarify Wet enough Dry to Wet Odor Car Running Car Stopping Fig.3 Comp. Operation Mode and Odor how the adsorbed odor arose. 2. Materials and Methods Before developing an odor evaluation method, we analyzed how an odorous stimulus was transmitted. The odorous stimulus first stimulates the olfactory cells on the "olfactory epithelium" as olfactory receptors in the nasal cavities, then goes through the olfactory nerve, and finally reaches the brain. At this Brain Olfactory Epithelium Odor Substances Recognition First Study, Restudy Memory time, if the concentration of the odorous components is Decision Odor Substances Emotion Image Measurement Chemical Analysis Odor Sensory Test Fig.4 Flow of Stimulus and Measurement at a sufficiently high level for the stimulative pulse from the olfactory cells to exceed a definite level (the concentration of the odorous components at this time is called as "threshold concentration"), then the signal is perceivable as an odor to determine the kind of odor (Fig.4). A search of those parameters objectively identified in the process from the generation of an odorous stimulus to the recognition of the odor will indicate that data can be collected through instrumental analysis for an "odorous component" and through odoring evaluation questionnaires for an "emotion or image." 2.1 Identifying Odor causative substances 2.1.1 Samples for Odor sensory test and Instrumental analysis We picked samples, and divide in two for instrumental analysis and the odor sensory evaluation value. 2.1.2 Odor sensory test for PCA and multiple regression analysis At first step, we made an attempt to develop a new evaluation strategy for relating the test values by means of instrumental analysis with the odor sensory *PCA:Principal Component Analysis Odor Sensory Test 2.72 Sampling Bag Cars evaluation values of the same samples. To correlate PCA* the results of analysis to the odoring evaluation values, and the causative substances. Fig.5 Sensory Test and PCA Analysis on the chief ingredients of the results of the odoring evaluation will identify objective parameters while the odor component analysis values are specified as descriptive parameters. Since the intensity of an odor in the vehicle is supposed to be highly correlated with the level of Odor C -2.72 -2.72 0.00 2.72 Partial Regression judgment criteria, which are available to group the plots (Fig.5). The odoring evaluation values in these vehicles are selected as Factor 1 0.00 Odor A Questionnaire we focused on relationships between the types of odor Factor 2 Odor B Y = β1X1 + β2X2 + β3X3 + . . . + βpXp Observed Value Explanatory Variate (Instrumental Analysis Data) Fig.6 Multiple Regression Analysis the component characterizing the odor of cigarette smoke, we believe that those components closely correlated to the odoring evaluation values are imported into the descriptive parameters when the variables are selected by performing multiple regression analysis (Fig.6). Each of the individual groups consists of similar members, based on the evaluation quadrants for people. The samples collected from the actual vehicle and prepared for odoring evaluation were divided into two and shared by instrumental analysis. Placed in odor bags, these samples were submitted to the panels (or testers) to receive responses by means of an SD method questionnaire. (1) Panels: Invoked were general engineers and office workers who had little preliminary knowledge of odors and were not interested in this evaluation. (2) Samples for evaluation: With an odorless specimen added as a blank, all the samples were resorted on a random basis irrespective of the sampling sequence from the vehicles in such a manner that the contents of the samples were unperceivable. Then, they were SampleNo. 1. Check on the number that you feel. [odor intensity] 5 Intense Odor 4 Strong Odor 3 Odor Easily Sensed Odor 2 Weak Odor 1 Barely Recognizable Odor 0 No Odor smoking was selected to conduct a test by means of curtains blocking off the direct rays of the sun under a temperature and humidity condition not making the panels feel uncomfortable. (4) Questionnaire: The terms indicating the types of odors were previously selected through several prior tests. By making [Odor Pleasantness / Unpleasantness] 2 Pleasant 1 Rather Pleasant 0 Neither -1 Rather Unpleasant -2 Unpleasant -3 Very Unpleasant 2. Fill in the box that you feel. 3 : Very much so 2 : Considerable 1 : Little so blank : Not at all named with alphabetic characters to conduct a blind test. (3) Evaluation environment: A silent chamber facing south without Name Date Acid Sweet Burnt Acrid Fusty Interior odor Damp mop Dirty sock Fishy Fish and meat Exhaust gas Festering trash Sweat Comment ( Dusty Cosmetics Tobacco Garbage ) Thank you Fig.7 Questionnaire inquiries about (1) Intensity of odor, (2) Degree of comfort / uncomfortableness, and (3) Type of odor in addition to (4) Miscellaneous requesting comments without restriction. Regarding the type of odor, the checkers were requested to respond with "3", "2","1" or "blank" as the degree of consistency with the word representing the odor used for the questionnaire. These results "3", "2" and "1" were then converted into 3 points, 2 points, and 1 point respectively when being totalized. (Fig.7) In the questionnaire, the intensity of odor and the degree of Table 1. Odor Intensity unpleasantness were adopted as the evaluation items and 5 4 3 2 1 0 ranked at six intensity levels and seven degrees respectively (Tables 1 and 2). 2.1.3 Instrumental analysis for multiple regression analysis We have decided to perform analysis by means of the possibly optimum strategy for each kind of "odorous" components supposed to exist in the odor for each sort of sources and the actual vehicle. Under the conditions shown in Appendix A, instrumental analysis was performed on each sort of components. A blank test was definitely conducted before and after sampling a specimen in Intense Odor Strong Odor Odor Easily Sensed Weak Odor with the Kind of Recognizable Odor Barely Recognizable Odor No Odor Table 2. Odor Pleasantness / Unpleasantness 3 2 1 0 -1 -2 -3 Very Pleasant Pleasant Rather Pleasant Neither Pleasant nor Unpleasant Rather Unpleasant Unpleasant Very Unpleasant each test to keep checking the background value when conducting this test. 2.2 Clarifying adsorbed odor mechanisms At the second step, we tried to not only determine the odor-emit ting components through PCA and multiple regression analysis but also clarified how the adsorbed odor arose. 2.2.1 Samples A smoking device was used to introduce and familiarize a cigarette odor along with cigarette smoke to the evaporator placed on the car air conditioner test bench and the mini core bench (After-mentioned. See 2.2.2.). In order to simulate the actual familiarizing conditions, the evaporator temperature was kept cycled between the condensing point and the vaporizing point to apply the odor. 2.2.2 Odor sensory test on Test bench and Mini-core bench We prepared the onboard car air conditioner ‘Test Bench’ (see Fig.8 for further information) traditionally used on an evaluation chamber basis and fabricated a new desktop test bench (hereafter called the "mini Temperature-controlled Room Conditioned Clean Out Air Air Conditioner Unit core bench" as shown in Fig.9) incorporating a small-size evaporator (hereafter called the "mini core") and intended for laboratory evaluation. Internally covered with stainless steel to facilitate cleaning, the onboard car air conditioner R134a Sampling Bag Exhaust Canister Fig.8 Test Bench evaluation bench is capable of controlling the evaluation chamber at a specified temperature and humidity and running the car air conditioner placed in the chamber. The evaluation panels enter this chamber to odor and evaluate the odor in turn. Additionally, to avoid raising the intensity of the odor in the chamber, the system is designed in such a manner that the ambient air is deodorized through an active carbon filter and always introduced at a constant rate. On the other hand, the mini core (a small size evaporator) built in the mini core bench is of a small size and low thermal capacity. Mini-Core Sampling Bag Hot Cold Furthermore, the temperature controls are simplified OUT by means of a noncombustible liquid heat film in place of chlorofluorocarbons. The mini core is shielded from the outside with the sampling bag in such a way that the IN Circulation Systems Fig.9 Mini-Core Bench Conditioned Clean N2 temperature and humidity of the nitrogen running in the bag can be controlled at discretion. Table 3 lists typical test conditions. By means of these test benches, we performed odoring evaluation and instrumental analysis. The odoring evaluation was completed at a low temperature of 20°C and a relative humidity between 40 % and 60 % from the typical conditions as described above. We ranked the intensity of odor and the degree of Table 3. Test Conditions Assembly Test Bench Temperature (degree) Humidity (%RH) Mini-Core Bench 20 ~ 30 40 ~ 60 20 ~ 25 30 ~ 60 unpleasantness at six intensity levels and seven degrees (Table 1 and Table 2). In advance, a T&T-Olfactometer was used to select approximately ten evaluation panels that were not handicapped in olfactory capability, followed by training to an odor intensity evaluation error between 0.5 and 1.0 among the individuals. Three or five panels were selected to mark the samples and find the average. 2.2.3 Instrumental analysis on a Test bench and on a Mini-core bench Sampling on test bench, we firstly collected the odor in Tedler-bag and a canister, and then condensed odor samples from them, on Tenax-TA or other devices (DNPH-Silica, Sr(OH)2 glass beads, Chromosorb 101 and others). Sampling on mini-core bench, we could collect the odor to a canister or condensed odor samples directly. Instrumental analysis conditions are the same (see Appendix A). 3. Results and Discussions 3.1 Correlation between instrumental analysis values and the odor sensory evaluation values 3.1.1 PCA result By wrapping up the above-mentioned questionnaires, we performed analysis on the principal components. As a result of the principal component analysis, three principal components having eigenvalue more than one were identified. Additionally, since the degree of contribution was Table 4. Test Conditions Factor Eigenvalue 1 2 3 4 Contribution 5.309 2.549 1.059 0.482 0.531 0.255 0.106 0.048 Accumulated Contribution 0.531 0.786 0.892 0.940 found sufficient over 80 percent and at approximate 90 percent for up to the third chief ingredient, the adsorbed odor evaluation quadrants would be reproducible with the first to third principal components only (Table 4). Next, we started to characterize the principal components as the judgment criteria (Table 5). The first principal component was named as the "Unpleasantness" presenting high factor loadings with the "Odor Pleasantness / Unpleasantness" and the terms presenting unpleasant odors such as "burning, dusty, smoky, and exhaust gaseous" and "acid, sweet, and cosmetics" (with the uncomfortable quadrants defined to be positive due Table 5. Test Conditions Variate Intensity Unpleasantness Acid Sweet Burned Dusty Tobacco Exhaust Gas Cosmetics Interior Materials Factor1 Factor2 -0.163 0.831 -0.803 -0.868 0.815 0.871 0.721 0.753 -0.827 0.038 0.979 0.372 0.511 0.450 0.448 0.066 0.529 0.274 0.454 0.471 Factor3 Factor4 -0.014 0.216 -0.170 -0.079 -0.219 -0.267 -0.242 -0.024 -0.222 0.866 -0.076 -0.174 0.161 0.062 -0.017 0.104 -0.276 -0.024 -0.007 0.045 to the converted parameters). While the terms on the uncomfortable side reading a positive factor load present no problem, the other terms of the comfortable side have the term "acid" typically expressing an unpleasant odor, raising a suspicion. We thereby interviewed the panels to make a survey to find out that the samples marked this time with "acid" were of a "citrus fragrance (deodorant)" odor and with a judgment for a preferable odor in addition to a description of "deodorant" noted in the voluntary response column, presenting no inconsistency with the results. Likewise the second principal component was named as "intensity" because the "intensity" factor loading was found at a high level. For the three remaining principal components, only "interior odor" presented a high factor loading. The reason why the "interior odor" was identified as a judgment criterion would be that the panels who were closely connected as occupants to vehicles were familiar with such an interior odor like the vehicles and, therefore, the odor is separately perceived and assessed unlike the typical uncomfortable odors such as exhaust emissions. 3.1.2 Factor loading Fig.10 shows the factor loadings for each term plotted about the principal component axis. Factor 2 1.0 Factor 3 1.0 Interior Odor Intensity These plots indicate Acid 0.5 that the evaluation quadrants are clarified 0 with the three evaluation axes, indicating how closely the term is related to the Cosmetic Interior Sweet Tobacco Odor Exhaust Gas Burned Unpleasantness Dusty Factor 0 1 -0.5 degree of uncomfortableness for the -0.5 -1.0 -1.0 samples used this time. -0.5 0 0.5 Fig.10 Factor Loading 3.1.3 Principal component score 0.5 1.0 -1.0 -1.0 Sweet Acid Cosmetic Intensity -0.5 Unpleasantness Factor Exhaust Gas Burned 1 Tobacco Dusty 0 0.5 1.0 The scores of the principal components from the results of "odor" evaluation in the actual vehicle are plotted with ‘• ○’ about the three axes. Furthermore, (1) Smoking vehicles are plotted with ‘•’ and (2) Vehicles using odorants (or aromatics) are plotted with ‘○’ to enclose each segments. In addition, those vehicles with a short actual driving period (i.e., almost new vehicles) and those with comments indicating a plastic and vinylic odor are encompassed (Fig.11). 1st principal component: Smoking vehicles on the uncomfortable (positive) side and deodorant using vehicles on the comfortable (negative) side. 2nd principal component: Vehicles with a strong smoky odor placed on the intensive (positive) side. 1.1 3rd principal component: Vehicles 0 with a strong interior or plastic odor placed on the intensive interior odor (positive) side. We acquired these results and found out that each principal Intensity 2.2 (+) Uses Perfumes Group -1.1 -2.2 -2.2 2.2 Very Smoky (+) 1.1 Plastic Vinyl 䊶䊶 Unplea -santness 0 Smoking Group -1.1 Interior Odor -1.1 Uses Perfumes Group -2.2 0 1.1 2.2 -2.2 -1.1 : Smoking Car : Aromatic, Cosmetics, Perfumes Fig.11 Principal component score (+) Almost New Strong Interior Odor (+) 䊶䊶 䇭 Unplea -santness Smoking Group 0 1.1 : Others 2.2 component definitely corresponded to the vehicle and that the odors could unequivocally be segregated by means of these evaluation axes. 3.1.4 Discussion about determining the odor causative substances Having identified the evaluation axis for the adsorbed odors by performing analysis on the principal components through the odoring evaluation, we describe correlations between the results of this odoring evaluation and the findings of the analysis. Multiple regression analysis was performed with the representative Odor Intensity = k log (Odor Substance Concentration) + a element for each evaluation axis used as the objective parameter and with 5 4 3 2 1 0 Odor Intensity the component analysis values used as the descriptive parameter. At this time, the component analysis values were converted into logarithmic variables for this analysis because the logarithmic physical values such as odor component concentration are widely known to be in proportion as the 0.1 1 10 100 Concentration (ppb) Weber-Fechner’s low (Fig.12). Fig.12 Weber-Fechner’s low The questionnaire item “Odor Pleasantness / Unpleasantness”" was used for the first principal component element “Unpleasantness”, the item “Intensity of odor” was used for the second principal component “Intensity,” and the item “New vehicle odor and interior” was used for the third principal component “Interior odor”. As a result of the multiple regression analysis, we acquired a high-precision regression equation to identify those odor causative substances. Furthermore, we checked for the ޓޓޓ ޓޓޓ ޓޓޓޓޓ ޓޓޓޓޓ Unpleasantness = 0.469*log(Substanece-A)+0.449*log( -B)+0.204*log( -C)+ … R:0.987, R**2:0.908 ޓޓ Intensity = 0.326*log(Substanece-D)+0.537*log( -E)+0.253*log( -F)+ … R:0.978, R**2:0.910 Interior Odor = 0.301*log(Substanece-G)+0.615*log( -H)+0.362*log( -I)+ … R:0.961, R**2:0.846 Fig.13 Result of the Multiple Regression Analysis adsorbed odor from the evaporator by means of those components incorporated in the regression equation and those not incorporated. As a result, the components imported into the regression equation presented a higher odor intensity than that of the other components not imported, backing the results of the analysis. (Fig.13) 3.2 Adsorbed odor mechanisms 3.2.1 Result of the test bench This section describes the findings of the evaluation on the air conditioner test bench. (1) Results of odoring evaluation Fig.14 shows the results of the odoring evaluation. The vertical axis of the graph refers to the operation modes of the air conditioner, indicating the changes of Dry (with the blower), ON (with the compressor turned on), and OFF Mode 2 3 4 5 +1 Unpleasantness 0 -1 -2 -3 ON ON (continual) By allowing five evaluators to odor in turn, it is difficult to (continual) conduct continuous evaluation with a limited number of Odor Intensity 1 Dry (with the compressor turned off). The horizontal axis refers to the intensity of odor and the degree of unpleasantness. 0 OFF OFF Fig.14 Result of Odoring evaluation odoring times and only five times was available for evaluation on a spot basis all over the modes. While the odor varied in a consecutive manner, a long time lag required each time for exchanging the panels resulted in fluctuations. Additionally, in the cigarette odor-familiarizing test conducted this time, a part of the panels complained about uncomfortableness due to a highly intensive odor and about olfactory fatigue as the odor accumulated in the evaluation chamber, indicating an error expansion factor. (2) Results of instrumental analysis Fig.15 shows the results of the instrumental analysis. Likewise the vertical axis of the graph refers to the operation modes and the horizontal axis refers to the concentration (in ppb) of the odorous component. As an example, the behavior of i-Valeric acid known as an unpleasant component is described. Mode In a part, a negative 0 0.2 Concentration (ppb) 0.4 0.6 0.8 1.0 Dry value resulted by subtracting the blank value (as marked with "ND" on the graph) and, therefore, a significant difference is ON ND ON ND (continual) unlikely between the analysis values, indicating difficult OFF analysis even by highly sensitive analyzing strategy. OFF ND (continual) 3.2.2 Mini core bench Fig.15 Result of Instrumental Analysis: i-Valeric Acid Next, the results of the odoring evaluation on the mini core bench are shown along with the findings of the analysis in Fig.16 and Fig.17. (1) Results of odoring sensory evaluation The horizontal axis refers to the elapse time, indicating the changes of Dry (with blower only and the mini core at normal temperature), ON (with the mini core at low temperature and the compressor turned on in reproduction mode). The vertical axis refers to the intensity of odor on the upper side and the degree of unpleasantness on the lower side (Fig.16). Unlike the results with the onboard car air conditioner evaluation bench described above, it was possible to Intensity temperature and the compressor turned off in reproduction 4 Dry ON OFF 3 Intensity NG 2 1 Good 0 Good Unpleasantness -1 -2 NG -3 -5 0 5 10 15 20 Time (min) Fig.16 Result of Odoring evaluation Unpleasantness mode), and OFF (with the mini core at normal 25 30 35 evaluate the samples at short time intervals without causing olfactory fatigue by fitting the nose with the silicon tube connected with the outlet only when the odor is smelt. While omitted in the figure, the fluctuations among the panels were limited below 0.5 because of no olfactory fatigue. This section describes the results of the instrumental analysis. In the same manner, the horizontal axis refers to the elapse time and indicates the changes of the Dry, ON, and OFF modes and the bar graphs along the vertical axis refer to the concentration of the component (Fig.17). On the mini core bench, unlike the results with the Concentration (ppb) (2) Results of instrumental analysis 0.6 Dry ON i-Valeric Acid Toluene * 1/10 0.4 0.2 0.0 OFF -5 0 5 10 15 20 Time (min) Fig.17 Result of Instrumental Analysis 25 30 onboard car air conditioner evaluation bench, the concentration of the odorous component in each mode presented a significant difference from the blank and the concentration of the component also presented a significant difference between the modes. For example, variations in i-Valeric acid and toluene are shown as functions of time. Judging from the results of odoring evaluation (Fig.16) and the instrumental analysis (Fig.17), the remarkable point is that the behavior of toluene and i-Valeric acid varies depending whether the unit is turned on or off. With the unit turned on, the concentration of water-repellent toluene was at a high level when condensed water was present. With the unit turned off, on the other hand, the concentration of the water-soluble i-Valeric acid component was at a high level with the odor intensity also at a high level when the condensed water was vaporized. In other words, these results imply all over again that the collection odor would be caused by and closely related with condensed water. In addition, these findings indicate that the degree of unpleasantness is highly related to the amount of i-Valeric acid and these odorous components accelerate the degree of unpleasantness. 3.2.3 Discussions about odor mechanism The reason why it was difficult to perform instrumental analysis on the onboard car air conditioner evaluation bench was as follows: 1.Adversely affected by the ambient air to result in an unstable blank. 2.High wind velocity reduced the odor generation period of time and allowed differences between the bag sampling individuals and adsorption to the bag. These factors seem to have degraded quantitativeness. In contrast, on the mini core bench, the blank was kept at a low level by using the mini core in a clean environment and it was possible to reproduce the behavior of condensed water on the surface of the evaporator at a low air flow rate to enable the testers to evaluate the odorous components on a stable basis. As described above, we have succeeded in identifying how an odor is familiarized with the car air conditioner by relating the generation or evaporation of condensed water due to evaporator temperature rising and lowering and the emission of the odorous components of the collection odor through the odoring evaluation and the instrumental analysis (Fig.18). As shown in the figures, the water-repellent components represented by toluene from among the odorous components collecting on the surface of the evaporator are emitted in the form of displacement with moisture in response to the start of water condensation with the compressor turned on and this is felt as the collection odor when the unit is turned on. Next, condensed, as additional the moisture evaporator is surface temperature is lowered in the continuous turn-on mode with the evaporator covered 1. Dry Hydrophobic Substance Hydrophilic Substance H2O Odor Substances 䇭 Evaporator’s Surface 3. ON Continual : Wet enough Hydrophilic Substance’s Elution 2. ON : Dry to Wet Hydrophobic Substance Released Ex. Toluene Flocculated Water Odor Intensity: Strong 4. OFF : Wet to Dry Hydrophilic Substance’s Vaporization Ex. i-Valeric acid Flocculated Water Odor Intensity: Weak Odor Intensity: Very Strong Fig.18 Adsorbed Odor Mechanism with water on the surface, the emission of the odorous components is reduced, and the intensity of the odor transfers at a low level. During this, the water-soluble components such as less-carbon fatty acids represented by i-Valeric acid increasingly dissolve from the surface of the evaporator into the condensed water. Finally, with the compressor turned off, the moisture evaporates and the water-soluble components dissolved in the condensed water vaporize with the moisture and felt as an odor when the unit is turned off (at the lower right corner of Fig.18). 4. Conclusions To determine the odor cause, we performed instrumental analysis and odor sensory evaluation. We found out for the first time that the instrumental analysis values of the adsorbed odor were highly correlated to the odor sensory evaluation values and identified the odor causative components. These causative substances adsorbed on the evaporator surface tend to become noticeable while the air conditioner is operated with the compressor turned on and off for energy saving purpose. With the evaporator ‘Mini-core bench’, we simulated adsorbed odor and found that • Hydrophobic odor substances (ex. Toluene) are released while evaporator’s surface is changing from ‘Dry’ to ‘Wet’ (temperature falls down and flocculated water breaks out on the surface). • While changing from ‘Wet’ to ‘Dry’, the flocculated water vaporizes and hydrophilic odor substances (ex. i-Valeric acid) come up together. • We clarify the odor generation mechanism from an evaporator surface. To improve comfortableness in the occupant compartment, these odors possibly emitted from the air conditioner must be minimized in the future by, for example: • Determining the sources of the odor-emitting components in question to minimize the rate of the odorous components flowing into the air conditioner by eliminating the causative factors and; • Installing a deodorization filter allowing only a limited part of the odorous components to flow into the upstream of the evaporator to prevent the odorous components from adhering. These measures are noticeable. References 1. Special Pollution Section, Atmospheric Integrity Bureau, Environment Agent; Technical guidelines for the three-point comparison type odor bag strategy, - from a odoring test procedure study report by the Environment Agent -, Environment and measurement technology, vol.9, No.9, (1982). 2. Special Pollution Section, Atmospheric Integrity Bureau, Environment Agent; Fundamental data for teaching and developing the bad-odor olfactory test procedure, Environment and measurement technology, vol.9, No.10, (1982). 3. Toshiyuki Tanaka; Sampling organic chemical compounds gases in the air by the adsorption and capture strategy at normal temperature Part 1, Basic principles, Environment and measurement technology, vol.16, No.1, (1989). 4. Toshiyuki Tanaka; Sampling organic chemical compounds gases in the air by the adsorption and capture strategy at normal temperature Part 2, Actual atmospheric measurement and sample measurements, Environment and measurement technology, vol.16, No.2, (1989). 5. Toshiyuki Tanaka; Performance of the Tenax-GC sampling tube for analysis on volatile organic chemical compounds at ppb level in the air, Air pollution society paper, Volume No.19, Number 6, (1984). 6. Nobuyuki Kashihira; Effect of sample injection through gas chromatography - Measuring a sulfide by means of GC-FPD -, Environment and measurement technology, vol.16, No.2, (1989). 7. Emiko Sudo; Measuring methods in environmental analysis, Environment and measurement technology, vol.12, No.9, (1985). Tomohiko Ishiguro; Details of how to measure the public specified bad-odor substances along with instructions, Environment and measurement technology, vol.14, No.1, (1987). 8. Kazuhisa Uchiyama, et al.; Analysis on odors adsorbed by the car air conditioner - Analyzing sensory odor evaluation and instrumental analysis data by means of multivariate analysis -, Compilation before Academy Lecture Meeting by Society of Automotive Engineers of Japan, Inc. Nos.981, 293, (1998), and 9831919. 9. Shigeyuki Sato; Quality of air in the passenger compartment, Toyota Central Laboratory Research and Development review, Vol.33, No.4, (1998). 10. Shigeyuki Sato et al.; Study in relation to odors of automobiles, Compilation before Academy Lecture Meeting by Society of Automotive Engineers of Japan, Inc. Nos.981, (1998), and 9831892. Appendix A Table 6. Aldehyde Analysis Conditions Trapping: DNPH Silica Cartridge (Waters SepPak) Instrument (HPLC): Shimazu LV-10VP, Detector: UV (350nm) Column: Inertsil ODS-80A (GL Science) Mobile Phase: CH3CN/H2O = 55/45, 1.5mL/min Column compartment: 40 degree Injection Volume: 25µL Table 7. Ammonia Analysis Conditions Trapping: Impinger 10ml H2O Instrument (IC): DIONEX DX-120, Conductivity Detector Column: IonPacCS12A, Guard Column: IonPacCG12A Eluent: 20mM CH3SO3H, Flow Rate: 1.0mL/min Suppresser: CSRS-1 (Recycle Mode), Column Temp.: 40 degree Table 8. Nitrogen Compound Analysis Conditions Trapping: 6L Canister → Tenax-TA (at -78 degree) Instrument (GC): Shimazu GC-14B Column: UnicarbonB-2000, Carrier Gas: He 50ml/min, Oven Temp.: 70 degree for 5min, 70-120 degree at 8 degree/min Inj Temp.: 200 degree, Detector: FTD Table 9. Sulfur Compound Analysis Conditions Trapping: 6L Canister → Chromosorb 101 (at –78 degree) Instrument (GC): Shimazu GC-9A Column: β, β’-ODPN 4m Carrier Gas: N2 70ml/min, Oven Temp.: 70 degree Isothermal Inj Temp.: 120 degree, Detector: FPD Table 10. Low Boiling HC Analysis Conditions Trapping: 6L Canister Instrument: Entech 7000 + GC/MS: HP 6890 + 5972A Column: HP-1, Length: 60m, Film: 1µm, ID: 0.32mm Carrier He: 1.0ml/min, Oven Temp.: 35 degree for 5min, 35-80 degree at 4 degree/min, 80-240 degree at 10 degree/min, 240 degree for 20min Detector: MSD, Interface Temp.: 280 degree Table 11. High Boiling HC Analysis Conditions Trapping: Tenax-TA (at RT) Thermal Desorption: 280 degree Instrument (GC/MS): Gerstel TDS + Agilent 6890+Agilent 5973N Column: HP-1, Length: 60m, Film: 1µm, ID: 0.32mm Carrier He: 1.0ml/min, Oven Temp.: 35 degree for 5min, 35-80 degree at 4 degree/min 80-240 degree at 10 degree/min, 240 degree for 20min Detector: MSD, Interface Temp.: 280 degree Table 12. Lower Fatty Acid Analysis Conditions Trapping: Sr(OH)2 Coated Glass Beads Instrument (GC): Shimazu GC-14B Column DB-Wax, Length: 60m, Film: 0.25µm, ID: 0.32mm Carrier He: 1.0ml/min, Oven: 120-240 degree at 8 degree/min Inj Temp.: 250 degree, Detector: FID
© Copyright 2026 Paperzz