Original Article

Sound Absorption of Natural Fiber Composite from Sugarcane Bagasse and Coffee Silver Skin

Wachara KALASEE1, Putipong LAKACHAIWORAKUN1,2, Visit EAKVANICH1, Panya DANGWILAILUX1,https://orcid.org/0000-0003-2268-9067
Author Information & Copyright
1Department of Engineering, King Mongkut’s Institute of Technology Ladkrabang, Prince of Chumphon Campus, Chumphon 86160, Thailand
2Department of Engineering, Rajamangala University of Technology Phra Nakhon, Bangkok 10800, Thailand
Corresponding author: Panya DANGWILAILUX, (e-mail: panya.da@kmitl.ac.th)

Copyright 2023 The Korean Society of Wood Science & Technology. This is an Open-Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/4.0/) which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.

Received: Jun 15, 2023; Revised: Jul 27, 2023; Accepted: Oct 05, 2023

Published Online: Nov 25, 2023


This study aimed to develop a sound-absorbing composite using sugarcane bagasse (SB) and coffee silver skin (CS) as raw materials. The composite boards were manufactured by bonding the fibers with Melamine Urea-Formaldehyde adhesive, ensuring a consistent thickness of 30 mm. Various densities were employed, namely 380, 450, and 520 kg/m3. The samples were fabricated with different fiber ratios, including SB100%, SB75% with CS25%, and SB50% with CS50%. The sound absorption coefficient (SAC) and noise reduction coefficient (NRC) were measured using the impedance tube method within a frequency range of 63–6,300 Hz. The experimental results revealed that the mixing ratio of CS exerted a notable influence on enhancing the SAC, while the density of the composite board exhibited a significant impact on increasing both the SAC and NRC. Among the densities tested, the optimal value was observed at 520 kg/m3, yielding a SAC value of 0.65 at a frequency of 1,000 Hz and an NRC value of 0.55 for the SB50-CS50 composite plate. These findings underscore the importance of considering the CS mixing ratio and composite board density when aiming to optimize sound absorption properties.

Keywords: sugarcane bagasse; sound absorption coefficient; noise reduction coefficient; coffee silver skin


Noise pollution is a significant factor that negatively impacts sleep quality and is associated with various health issues, including heart disease and stress disorder (He et al., 2021; Jang et al., 2018a; Jariwala et al., 2017). Therefore, the enforcement of noise control measures is crucial and serves as an important protective factor for preserving health-related quality of life (Hwang et al., 2013; Jang et al., 2018b; Kim et al., 2012; Kook et al., 2007; Lee et al., 2011). The utilization of sound-absorbing materials has been recognized as a straightforward and dependable alternative for mitigating noise levels (Kang et al., 2019; Sharma et al., 2020).

Numerous studies have investigated building materials that exhibit exceptional sound absorption characteristics and have explored methods for determining sound absorption rates and identifying suitable sound insulation materials. However, the utilization of synthetic materials such as foam, asbestos, and glass wool raise concern due to their negative environmental impact and contribution to the greenhouse effect, compounded by the uncertain availability of industrial resources and the global surge in their utilization (Linton et al., 2015). In response to efforts aimed at reducing greenhouse gas emissions, there has been a growing interest in recycling various industrial by-products for efficient resource utilization (Kang et al., 2018a, 2018b, 2019). Consequently, researchers have increasingly turned their attention to natural materials as a means to develop environmentally friendly and sustainable sound-absorbing materials (Asdrubali, 2006).

In the agricultural industry of Thailand, various post-production wastes are generated, including bamboo fiber (Koizumi et al., 2002), coconut fiber (Fouladi et al., 2010), sugar cane fiber (Putra et al., 2013), paddy rice fiber (Putra et al., 2013), date palm fibres (Abd ALRahman et al., 2014). and vegetable fiber (Bastos et al., 2012). These waste materials have shown promising potential for sound absorption, particularly in the mid to high frequency range, with sound absorption coefficients (SACs; exceeding 0.5, especially above 1 kHz.). One potential natural waste material is coffee silver skin (CS; Woldesenbet et al., 2014). CS is derived from the hulling, roasting, cleaning, packaging, and sorting processes of coffee (Murthy and Naidu, 2012). There have been several research studies focusing on the use of natural fibers to produce sound-absorbing materials. For instance, natural fiber materials derived from wood, such as wood pellets, have also been investigated for their sound absorption capabilities as an eco-friendly material (Jang, 2022b), rice straw, bagasse, binderless particleboard (Jamaludin et al., 2020) and sandwich particleboard (Iswanto et al., 2020). As for the development of various environmentally friendly sound absorbing materials, such as pine (Pinus densiflora; Jang, 2022d), pollen cones, which can be developed into high quality sound absorbing materials, hinoki cypress cubes (Jang, 2022e), Acanthopanax senticosus wastes (Jang, 2022a) and peanut shells that can be easily recycled (Jang, 2022c).

According to a recent survey, South Koreans have an average daily coffee consumption of two to three cups, with the majority of coffee consumers being in their 40s and 50s. Experts attribute this coffee obsession to Korea’s work culture and several other contributing factors. The data highlights Korea’s longstanding reputation for having one of the highest rates of coffee consumption globally. In 2020, market research firm euromonitor international reported that Korea ranked second in the world in terms of coffee consumption, with an average of 367 cups per person annually. Notably, this figure was more than twice the global average coffee consumption rate at the time, which stood at 161 cups per year (Lee, 2023). Looking back at the year 2019, South Korean imports of thai raw sugar saw a significant increase. Data from the thai sugar milling corporation indicated a year-on-year rise of 148%, reaching 246,179 metric tons for the period between January and April. Additionally, imports of white and refined sugar also surged by 147% during the same period, amounting to 68,960 metric tons (Brian, 2019). Moving on to 2021, South Korea emerged as the 8th largest importer of raw sugar in the world, importing a total of $760 million worth of the product. In the same year, raw sugar ranked as the 135th most imported product in South Korea. The primary sources of South Korea’s raw sugar imports were Australia ($400 million), Thailand ($127 million), El Salvador ($65.4 million), Guatemala ($36 million), and Brazil ($31 million). These figures clearly demonstrate the growth in both the coffee and sugar cane industries in South Korea. However, this growth inevitably leads to increased waste generation in the manufacturing sector. Therefore, it presents an intriguing opportunity for researchers to study effective methods for recycling this waste.

The objective of this research is to develop a sound-absorbing composite using sugarcane bagasse (SB) and CS. Multiple samples were fabricated and tested in an impedance tube to determine their SAC. This paper is organized into four sections. Section 2 provides a brief overview of the composition and methodology. Section 3 presents and discusses the main results, and finally, Section 4 concludes with the main findings.


2.1. Sample fabrication

SB was collected from New Krung Thai Sugar Factory (Kanchanaburi, Thailand). The SB was cut using a chopping machine into approximately 5 mm lengths and then dried in a drying oven at 90°C for 24 hours, resulting in a moisture content of 10% on a dry basis. The dried SB was stored for all subsequent studies and analyses.

CS was obtained from agricultural waste at a robusta coffee producer community enterprise group in Chumphon Province, Thailand. It is different from the coffee grounds because CS is the husk obtained from the grinding of fresh coffee beans in the production of roasted coffee beans. The CS was obtained from the waste of a coffee roasting plant and subsequently dried in an oven at 90°C for 24 hours, resulting in a moisture content of 10% on a dry basis. The dried CS was carefully stored for further analysis. For the preparation of the composite material, the dried SB and CS were mixed at varying ratios: 100:0, 75:25, and 50:50. The resulting mixture was then combined with Melamine-Urea-Formaldehyde from Aica Hatyai, Songkhla, Thailand in a ratio of 3:1. Thorough stirring was conducted to ensure the achievement of homogeneity in the mixture. Subsequently, the resulting mixtures were poured into square molds with dimensions of 300 mm × 300 mm, thickness of 30 mm and subjected to pressing using a hydraulic hot press machine at a temperature of 130°C and a pressure of 220 kgf/cm2 for a duration of 15 minutes. To assess the sound absorption properties, the samples were cut into cylindrical shapes with diameters of 30 mm and 100 mm, and a thickness of 30 mm. For the evaluation of thickness swelling (TS), the samples were cut into square forms with dimensions of 50 mm in width, 50 mm in length, and 30 mm in thickness. The obtained results are presented in Table 1.

Table 1. Composition of prepared composite samples
No. Conditions Ratio (%) Density (kg/m3) Porosity (%) Thickness swelling (%)
Bagasse CS
1 SB100-A 100 - 380 189.07 2.52
2 SB100-B 100 - 450 124.68 2.11
3 SB100-C 100 - 520 57.42 1.35
4 SB75-CS25-A 75 25 380 123.16 0.83
5 SB75-CS25-B 75 25 450 76.54 0.60
6 SB75-CS25-C 75 25 520 46.50 0.37
7 SB50-CS50-A 50 50 380 111.27 0.33
8 SB50-CS50-B 50 50 450 67.26 0.18
9 SB50-CS50-C 50 50 520 30.54 0.08

The thickness of the composites was standardized at 30 mm.

CS: coffee silver skin, SB: sugarcane bagasse.

Download Excel Table

The bulk density of the composite samples was determined by measuring and weighing them using Equation (1):

ρ b u l k =   m   /   V

where ρbulk represents bulk density, m denotes mass, and V signifies volume.

In accordance with the Archimedes principle (Calis Acikbas et al., 2018), the weight of the sample was measured after it underwent boiling in hot water for 1 hour. Subsequently, the sample was dried to remove any residual water by wiping it and recording its weight. It was then subjected to a 2-hour treatment of blowing with hot air at 110°C. Consequently, the porosity of the sample (Φ) was determined using Equation (2):

Φ   =   W w e t   W d r y W w e t   W s u s p e n d   ×   100 %

Where Wssuspend is the sampling weight that suspended in water; Wwet is the sampling weight after wiping water on surface; Wdry is the sampling weight after drying.

The thickness of the specimen samples, which had dimensions of 50 × 50 × 30 mm, was prepared in accordance with ASTM D570 guidelines, resulting in swelling. The TS was calculated using Equation (3):

T h i c k n e s s   s w e l l i n g   =   T l   T 0 T 0   ×   100 %

Where To is the thickness of specimens before the test started and Tl is the thickness of specimens after immersion in distilled water for 24 hours.

Distilled water, renowned for its exceptional purity and absence of impurities, was utilized instead of regular tap water in this study. The substitution of regular tap water, which may contain impurities, has the potential to introduce discrepancies in the porosity results due to unforeseen influences, such as chemical reactions with the specimen. Furthermore, the Urea formaldehyde melamine glue employed in this experiment is widely recognized for its insolubility in water once the curing or hardening process is complete. This adhesive, classified as a thermosetting adhesive, undergoes a solidification process and remains solid without softening or liquefaction when exposed to heat (Ebnesajjad and Landrock, 2014).

2.2. Impedance tube method

The SAC experiments of composite samples were measured using the impedance tube method according to ISO 10534–2. Fig. 1 shows the schematic diagram of the SAC experiment. This experiment was tested at a frequency of 63–6,300 Hz. The test uses tube to measure the SAC of the sample. The low frequency has a diameter of 100 mm and the high frequency has a diameter of 30 mm in Fig. 2 (de Carvalho et al., 2020; Jung et al., 2001; Putra et al., 2018).

Fig. 1. The schematic diagram of impedance tubes.
Download Original Figure
Fig. 2. Composite samples (a) SB100, (b) SB75-CS25, (c) SB50-CS50. SB: sugarcane bagasse, CS: coffee silver skin.
Download Original Figure
2.3. The noise reduction coefficient

The physical environment such as temperature and humidity in the chamber was controlled at constant. Table 2 presents the SAC of the composite board at 63 Hz–6.3 kHz. For the samples which had the ingredient ratio and density different, the SAC of these samples were recorded and considered. The experimental data; the sound absorption coefficient average (SAA); was divided into three groups: low frequency (63 Hz–1 kHz), medium frequency (1 kHz–3 kHz) and high frequency (3 kHz–6.3 kHz). The noise reduction coefficient (NRC); the arithmetic means of the absorption coefficients for a specific material and installation conditions; was determined by the center octave frequencies of 250, 500, 1,000 and 2,000 Hz. Thus, it could be calculated from Equation (4):

N R C   =   α 250 +   α 500 + α 1 , 000 + α 2 , 000 4
Table 2. The sound absorption coefficient values of samples
No. Conditions Sound absorption coefficient (α) SAA NRC
Low frequency (Hz) 63–1 k Middle frequency (Hz) 1 k–3 k High frequency (Hz) 3 k–6 k
1 SB100-A 0.30 0.48 0.49 0.37 0.43
2 SB100-B 0.33 0.50 0.51 0.40 0.46
3 SB100-C 0.36 0.53 0.52 0.42 0.50
4 SB75-CS25-A 0.30 0.50 0.48 0.37 0.45
5 SB75-CS25-B 0.35 0.52 0.52 0.42 0.49
6 SB75-CS25-C 0.38 0.55 0.55 0.44 0.53
7 SB50-CS50-A 0.30 0.51 0.51 0.37 0.46
8 SB50-CS50-B 0.33 0.57 0.58 0.42 0.51
9 SB50-CS50-C 0.36 0.61 0.60 0.45 0.55

SAA: sound absorption coefficient average, NRC: noise reduction coefficient, SB: sugarcane bagasse, CS: coffee silver skin.

Download Excel Table
2.4. Scanning electron microscopy techniques

Scanning electron microscopy (SEM) is a valuable technique for examining the surface structures of biological samples. In this study, the surface structures of the sample boards, including SB and CS, were investigated. SEM (Thermo Scientific Phenom Pharos, RMUTP Lab, Bangkok, Thailand) was used to image the external surface of the composites and cross-section.


3.1. The physical characteristics of the composites

Table 1 presents the physical characteristics of the composites. The results indicate that the composite plates were categorized into three groups based on different sample mixing ratios: 100% SB (SB100), 75% SB mixed with 25% CS (SB75-CS25), and 50% SB mixed with 50% CS (SB50-CS50). The values are expressed in percentages by mass. And each group was further subdivided into three density levels: A at 380 kg/m3, B at 450 kg/m3, and C at 520 kg/m3. The table presents the porosity values alongside the TS. The experimental findings demonstrate a consistent trend: as the density of the composite board increased, both the porosity and TS values decreased across all ratio groups.

3.2. Acoustical properties

Table 2 presents the average values of the SAA and NRC. Based on the experimental observations, it was noted that the composite sheet in the SB100 group displayed an increase in the SAA as the density of the composite increased. This effect was particularly prominent in the high frequency range, leading to the highest SAA value recorded for the SB100-A composite, reaching a maximum value of 0.50. Similarly, the NRC exhibited a consistent increase and reached its maximum value of 0.50 for the SB100-A composite. When SB and CS were combined in the composite, the highest SAA value was observed in the mid-frequency band. Furthermore, increasing the proportion of CS in the mixture resulted in improved SAA values. This trend was also evident in the NRC, as the inclusion of different fibrous materials contributed to enhanced sound absorption properties. Additionally, the incorporation of flex pieces in the composite increased the complexity of the porous structure, further enhancing its sound absorption characteristics. By increasing the density of the composite, the maximum NRC value achieved was 0.55 for the SB50-CS50-C composite.

Fig. 3 presents the SACs of the composites at different ratios and densities. In Fig. 3(a), the variation of the SAC with frequency is depicted. It is noteworthy that the SAC displays an increasing trend at 1,000 Hz and reaches its peak above 2,000 Hz, followed by a slight decrease and subsequent stabilization. An important observation is the influence of density values on the SAC. Specifically, an increase in density corresponds to higher SAC values, as evidenced in the SB100-C composite at 0.54 above 2,000 Hz. Fig. 3(b) illustrates the variation of the SAC with frequency. Initially, the SAC experiences an increase at 1,000 Hz, followed by a decrease at 1,500 Hz, and then rises again to a second peak above 2,000 Hz as evidenced in the SB75-CS25-C composite at 0.60. Subsequently, the SAC gradually decreases slightly and stabilizes. The SAC values are notably affected by the density of the composites. As the density increases, the SAC also increases, indicating the impact of density on sound absorption properties. Fig. 3(c) demonstrates that the SAC exhibits a peak at 1,000 Hz as evidenced in the SB50-CS50-C composite at 0.65, followed by a decrease above 1,500 Hz, and then rises to a second peak above 2,000 Hz. These two peaks are clearly depicted in the graph. Subsequently, the SAC gradually decreases slightly and remains relatively constant. This observation further supports the influence of frequency on the sound absorption characteristics of the composites.

Fig. 3. Sound absorption coefficients at varying densities of the composite. (a) SB100, (b) SB75-CS25, (c) SB50-CS50. SB: sugarcane bagasse, CS: coffee silver skin.
Download Original Figure

Fig. 4 depicts the sound absorption behavior at different mixing ratios for the same density. Fig. 4(a) (Density 380 kg/m3) revealed that at a densityof 380 kg/m3, the SAC values in the low-frequency range exhibited a consistent pattern characterized by a gradual increase at 1,000 Hz, followed by a decrease above 1,500 Hz, and subsequent recovery to higher values at a frequency of 2,000 Hz. The graph demonstrates that each composite material displayed nearly identical sound absorption behavior at this density. In Fig. 4(b) (Density 450 kg/m3), at a density of 450 kg/m3, the SB50-CS50 mixture exhibiteda prominent peak in the SAC above 1,000 Hz, reaching a maximum value of 0.60. This observation aligns with the findings depicted in Fig. 4(c) (Density 520 kg/m3), where the SB50-CS50 mixture demonstrated a distinct peak in SAC above 1,000 Hz at a density of 520 kg/cm3, reaching a maximum value of 0.65.

Fig. 4. Sound absorption coefficients at varying ratio of the composite. SB: sugarcane bagasse, CS: coffee silver skin.
Download Original Figure

These outcomes strongly suggest that the incorporation of CS in the composite mixture contributes to an enhanced sound absorption performance. The observed results indicate that modifying the composite material composition and increasing its density have a notable impact on SAC and NRC as shown in Fig. 5 (density A = 380 kg/m3, B = 450 kg/m3, C = 520 kg/m3), thereby highlighting the importance of material selection and density optimization in achieving the desired sound absorption characteristics (Nandanwar et al., 2017; Qui and Enhui, 2018).

Fig. 5. Noise reduction coefficient performance with difference density of composites. SB: sugarcane bagasse, CS: coffee silver skin, NRC: noise reduction coefficient.
Download Original Figure
3.3. Scanning electron microscopy images

Fig. 6 depicts the SEM image of the composite surface and the cross-section image, revealing the intricate arrangement of two natural fibers, BS and CS, within the composite structure. This complex configuration contributes to the enhanced sound-absorbing properties of the composite materials.

Fig. 6. SEM image of composite surface and the cross-section (bar = 200 μm). SEM: scanning electron microscopy.
Download Original Figure


In this study, the SACs of a natural fiber composite made from SB and CS were investigated using the impedance tube technique which gave the following conclusions:

  1. The composite materials comprising SB and CS were tested for their sound absorption properties. It was observed that increasing the density of the sample sheets resulted in higher SAC values, with the density of 520 kg/m3 yielding the most favorable outcome. The interesting result can be further developed to achieve a higher density, thereby increasing efficiency in other areas such as improved mechanical characteristics. However, one must consider the porosity of the material, as it can affect sound adsorption efficiency.

  2. The mixing ratio of the composite material plays a crucial role in enhancing its sound absorption properties, and the addition of CS has been found to be particularly beneficial. Based on the experimental results, it is recommended to use a ratio of 50% SB and 50% CS, as this composition allows for the formation of a complex structure inside the material, thereby improving its sound absorption characteristics.

  3. Increasing the density of the composites also had a significant impact on the swell values. Among the experimental groups, the mixture with a ratio of 50% SB and 50% CS exhibited the highest anti-TS value.

  4. This experiment showcases the potential of SB and CS as promising materials for the production of sound-absorbing products, presenting an environmentally friendly alternative.


No potential conflict of interest relevant to this article was reported.


The authors extend their appreciation to Aica Hatyai Co., Ltd. and Ban Tham Sing Coffee Group Community Enterprise for their generous support in providing raw materials for this research. Special thanks to Rajamangala University of Technology Phra Nakhon (RMUTP) and King Mongkut’s Institute of Technology Ladkrabang (KMITL), Prince of Chumphon Campus, for providing the invaluable opportunity to conduct this research.



Abd ALRahman, L., Raja, R.I., Rahman, R.A., Ibrahim, Z. 2014. Comparison of acoustic characteristics of date palm fibre and oil palm fibre. Research Journal of Applied Sciences, Engineering and Technology 7(8): 1655-1660.


Asdrubali, F. 2006. Survey on the acoustical properties of new sustainable materials for noise control. In: Tampere, Finland, Proceedings of the Euronoise 2006 Conference, pp. 1-10.


Bastos, L.P., de Melo, G.S.V., Soeiro, N.S. 2012. Panels manufactured from vegetable fibers: An alternative approach for controlling noises in indoor environments. Advances in Acoustics and Vibration 2012: 698737.


Calis Acikbas, N., Ture, Y., Gurlek, E., Ozcan, S., Soylu, S., Acikbas, G., Gudu, T. 2018. Microstructural characterization, mechanical, physical and thermal properties of a diesel particulate filter. Arabian Journal for Science and Engineering 43: 1383-1394.


de Carvalho, P.S., Dalla Nora, M., da Rosa, L.C. 2020. Development of an acoustic absorbing material based on sunflower residue following the cleaner production techniques. Journal of Cleaner Production 270: 122478.


Ebnesajjad, S., Landrock, A.H. 2014. Adhesives Technology Handbook. William Andrew, Norwich, NY, USA.


Esquivel, P., Jiménez, V.M. 2012. Functional properties of coffee and coffee by-products. Food Research International 46(2): 488-495.


Fouladi, M.H., Nor, M.J.M., Ayub, M., Leman, Z.A. 2010. Utilization of coir fiber in multilayer acoustic absorption panel. Applied Acoustics 71(3): 241-249.


He, C., Zhang, B., Lu, J., Qiu, R. 2021. A newly discovered function of nitrate reductase in chemoautotrophic vanadate transformation by natural mackinawite in aquifer. Water Research 189: 116664.


Hwang, S., Kim, J., Kwon, H., Seok, S.Y. 2013. Sound transmission loss through double walls. International Journal of Naval Architecture and Ocean Engineering 50(2): 64-68.


Iswanto, A.H., Hakim, A.R., Azhar, I., Wirjosentono, B., Prabuningrum, D.S. 2020. The physical, mechanical, and sound absorption properties of sandwich particleboard (SPb). Journal of the Korean Wood Science and Technology 48(1): 32-40.


Jamaludin, M.A., Bahari, S.A., Zakaria, M.N., Saipolbahri, N.S. 2020. Influence of rice straw, bagasse, and their combination on the properties of binderless particleboard. Journal of the Korean Wood Science and Technology 48(1): 22-31.


Jang, C., Hui, S., Lu, W., Cowan, A.J., Morscher, R.J., Lee, G., Liu, W., Tesz, G.J., Birnbaum, M.J., Rabinowitz, J.D. 2018a. The small intestine converts dietary fructose into glucose and organic acids. Cell Metabolism 27(2): 351-361.E3.


Jang, E.S. 2022a. Experimental investigation of the sound absorption capability of wood pellets as an eco-friendly material. Journal of the Korean Wood Science and Technology 50(2): 126-133.


Jang, E.S. 2022b. Investigation of sound absorption ability of Acanthopanax senticosus wastes. Journal of the Korean Wood Science and Technology 50(6): 404-413.


Jang, E.S. 2022c. Investigation of sound absorption ability of hinoki cypress (Chamaecyparis obtusa) cubes. Journal of the Korean Wood Science and Technology 50(5): 365-374.


Jang, E.S. 2022d. Peanut shells as an environmentally beneficial sound-absorbing material. Journal of the Korean Wood Science and Technology 50(3): 179-185.


Jang, E.S. 2022e. Use of pine (Pinus densiflora) pollen cones as an environmentally friendly sound-absorbing material. Journal of the Korean Wood Science and Technology 50(3): 186-192.


Jang, E.S., Kang, C.W., Kang, H.Y., Jang, S.S. 2018b. Sound absorption property of traditional Korean natural wallpaper (Hanji). Journal of the Korean Wood Science and Technology 46(6): 703-712.


Jariwala, H.J., Syed, H.S., Pandya, M.J., Gajera, Y.M. 2017. Noise pollution & human health: A review. Indoor and Built Environment 1(1): 1-4.


Jung, S.S., Jho, M.J., Kook, C., Kim, S.W. 2001. Determination of sound absorption coefficient and impedance in impedance tubes. In: Mokpo, Koera, Proceedings of the Korean Society for Noise and Vibration Engineering Conference, pp. 244-249.


Kang, C.W., Jang, E.S., Jang, S.S., Kang, H.Y. 2018a. Comparison of transfer function method and reverberation room method in measuring the sound absorption coefficient of rice straw particle mat. Journal of the Korean Wood Science and Technology 46(4): 362-367.


Kang, C.W., Jang, E.S., Jang, S.S., Kang, H.Y. 2018b. Measurement of sound transmission loss in a sound barrier filled with the rice-straw particles by the transfer function and laboratory measurement methods. Journal of the Korean Wood Science and Technology 46(4): 338-345.


Kang, C.W., Lee, N.H., Jang, S.S., Kang, H.Y. 2019. Sound absorption coefficient and sound transmission loss of rice hull mat. Journal of the Korean Wood Science and Technology 47(3): 290-298.


Kim, C., Chang, T., Kim, D.S. 2012. Characteristics analysis of highway traffic noise. Transactions of the Korean Society for Noise and Vibration Engineering 22(12): 1191-1198.


Koizumi, T., Tsujiuchi, N., Adachi, A. 2002. The development of sound absorbing materials using natural bamboo fibers. WIT Transactions on the Built Environment 59: 157-166.


Kook, J.H., Jung, C.W., Yun, J.H., Kim, J.S. 2007. Experimental study on wall sound transmission loss at construction equipment machinery room. In: Mokpo, Korea, Proceedings of the Korean Society for Noise and Vibration Engineering Conference, pp. 701-705.


Lee, J.H., Kim, B.S., Kim, K.J. 2011. Study of sound transmission characteristics of using a scale reverberation chamber and vibro acoustic FEM. In: Mokpo, Korea, Proceedings of the Korean Society for Noise and Vibration Engineering Conference, pp. 92-95.


Lee, Y.S. 2023. Work culture, pandemic fuel Koreans’ craving for caffeine. https://www.koreaherald.com/view.php?ud=20230314000601


Linton, S.J., Kecklund, G., Franklin, K.A., Leissner, L.C., Sivertsen, B., Lindberg, E., Svensson, A.C., Hansson, S.O., Sundin, Ö., Hetta, J., Björkelund, C., Hall, C. 2015. The effect of the work environment on future sleep disturbances: A systematic review. Sleep Medicine Reviews 23: 10-19.


Murthy, P.S., Naidu, M.M. 2012. Recovery of phenolic antioxidants and functional compounds from coffee industry by-products. Food Bioprocess Technology 5: 897-903.


Nandanwar, A., Kiran, M.C., Varadarajulu, K.C. 2017. Influence of density on sound absorption coefficient of fibre board. Open Journal of Acoustics 7: 1-9.


Putra, A., Abdullah, Y., Efendy, H., Farid, W.M., Ayob, M.R., Py, M.S. 2013. Utilizing sugarcane wasted fibers as a sustainable acoustic absorber. Procedia Engineering 53: 632-638.


Putra, A., Or, K.H., Selamat, M.Z., Nor, M.J.M., Hassan, M.H., Prasetiyo, I. 2018. Sound absorption of extracted pineapple-leaf fibres. Applied Acoustics 136: 9-15.


Qui, H., Enhui, Y. 2018. Effect of thickness, density and cavity depth on the sound absorption properties of wool boards. Autex Research Journal 18(2): 203-208.


Sharma, S.K., Shukla, S.R., Sethy, A.K. 2020. Acoustical behaviour of natural fibres-based composite boards as sound-absorbing materials. Journal of the Indian Academy of Wood Science 17: 66-72.


Woldesenbet, A.G., Woldeyes, B., Chandravanshi, B.S. 2014. Characteristics of wet coffee processing waste and its environmental impact in Ethiopia. International Journal of Research in Engineering and Science 2(4): 1-5.