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Physical and Mechanical Properties of Biodegradable Pot Derived from Oil Palm Empty Fruit Bunch and Sodium Alginate

Abstract

Efforts to overcome the problem of agroplastic waste (in the form of pots, polybags, and other planting containers) continue to be studied. This research investigated the use of oil palm empty fruit bunch (OPEFB) and sodium alginate in the production process of biodegradable pots. This study also investigated the comprehensive features of biodegradable pots which included physical, mechanical, structural (chemical), and morphological properties. Physical and mechanical characterization showed that the moisture content, specific gravity, water absorption, ultimate tensile strength (UTS), and elongation at break of the examined biodegradable pots increased with increasing sodium alginate content. Biopot-3 with 15% sodium alginate exhibited the highest UTS at 1.29 MPa and elongation at break at 6.77%. FTIR spectra in the 400-4000 cm-1 region showed that all examined biodegradable pots exhibited identical spectra which most of the peaks showed the characteristics of cellulose, hemicellulose, and alginate. While, XRD patterns showed that the biodegradable pot material has an amorphous structure with 2θ angles being 21.69º, 22.01º, and 22.03º, respectively. Surface morphology analysis by SEM revealed that Biopot-1 containing 5% sodium alginate (the lowest sodium alginate content) exhibited many porous cavities, indicating that the matrix could not completely fill the space between the fibers. It contrasts with Biopot-2 and Biopot-3 (10% and 15% sodium alginate, respectively), which have a morphology with a denser surface. In general, the produced biodegradable pots exhibited adequate functional properties as ecologically friendly planting containers, but further research is required to investigate their field applicability.

Keywords:
agroplastic; biocomposite; biopot; cellulose; thermopressing

GRAPHICAL ABSTRACT

HIGHLIGHTS

  • Oil palm empty fruit bunch is sufficient to be used as reinforcement on the biopot production.

  • Application of sodium alginate deliver a positive effect on the biopot’s mechanical properties.

  • Properties of the developed biopot indicate the possibility to substitute the plastic pot use.

HIGHLIGHTS

  • Oil palm empty fruit bunch is sufficient to be used as reinforcement on the biopot production.

  • Application of sodium alginate deliver a positive effect on the biopot’s mechanical properties.

  • Properties of the developed biopot indicate the possibility to substitute the plastic pot use.

INTRODUCTION

Plastic waste, including agro-plastics such as pots and polybags, has been the most severe environmental problem due to their resistant to decomposition by natural processes [11 Jambeck JR, Ji Q, Zhang Y-G, Liu D, Grossnickle DM, Luo Z-X. Plastic waste inputs from land into the ocean. Science (80- ). 2015;347(6223):768-71.,22 Akhir J, Allaily, Syamsuwida D, Budi SW. Water absorption and quality of environmentally friendly seedling containers made from waste paper and organic materials. Rona Tek Pertan. 2017;10(2):1-11.]. Organic materials based-planting containers or biodegradable pots are alternatives to answer the issues. Moreover, biodegradable pots (biopots) are not harmful to the plant roots because they can be transferred directly from the nursery to the plantation without disassembly [33 Postemsky PD, Marinangeli PA, Curvetto NR. Recycling of residual substrate from Ganoderma lucidum mushroom cultivation as biodegradable containers for horticultural seedlings. Sci Hortic (Amsterdam) [Internet]. 2016;201:329-37. Available from: http://dx.doi.org/10.1016/j.scienta.2016.02.021
http://dx.doi.org/10.1016/j.scienta.2016...

4 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
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5 Balestri E, Vallerini F, Seggiani M, Cinelli P, Menicagli V, Vannini C, et al. Use of bio-containers from seagrass wrack with nursery planting to improve the eco-sustainability of coastal habitat restoration. J Environ Manage [Internet]. 2019;251(July):109604. Available from: https://doi.org/10.1016/j.jenvman.2019.109604
https://doi.org/10.1016/j.jenvman.2019.1...

6 Calcagnile P, Sibillano T, Giannini C, Sannino A, Demitri C. Biodegradable poly(lactic acid)/cellulose-based superabsorbent hydrogel composite material as water and fertilizer reservoir in agricultural applications. J Appl Polym Sci. 2019;136(21):1-9.

7 Rafee SNAM, Lee YL, Jamalludin MR, Razak NA, Makhtar NL, Ismail RI. Effect of Different Ratios of Biomaterials to Banana Peels on the Weight Loss of Biodegradable Pots. Acta Technol Agric. 2019;22(1):1-4.

8 Saba N, Jawaid M, Sultan MTH, Alothman OY. Green Biocomposites for Structural Applications Green composites. Springer International Publishing; 2017. 1-27 p.

9 Sun E, Liao G, Zhang Q, Qu P, Wu G, Huang H. Biodegradable copolymer-based composites made from straw fiber for biocomposite flowerpots application. Compos Part B Eng [Internet]. 2019;165(November 2018):193-8. Available from: https://doi.org/10.1016/j.compositesb.2018.11.121
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-1010 Seggiani M, Cinelli P, Balestri E, Mallegni N, Stefanelli E, Rossi A, et al. Novel sustainable composites based on poly(hydroxybutyrate-co-hydroxyvalerate) and seagrass beach-CAST fibers: Performance and degradability in marine environments. Materials (Basel). 2018;11(5).]. Various high fiber biomass, such as coconut frond and fiber, wood fiber, paddy husk and straw, mushroom substrates, banana peel, and also cow manure have been studied as reinforcing substances in the production of biopots [33 Postemsky PD, Marinangeli PA, Curvetto NR. Recycling of residual substrate from Ganoderma lucidum mushroom cultivation as biodegradable containers for horticultural seedlings. Sci Hortic (Amsterdam) [Internet]. 2016;201:329-37. Available from: http://dx.doi.org/10.1016/j.scienta.2016.02.021
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,44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,1111 Asmara S, Rahmawati W, Suharyatun S, Kurnia B, Listiana I, Widyastuti RAD. Producing organic pot from cassava stem waste for water spinach (Ipomea reptans Poir) as waste management strategy. Conf Ser Earth Environ Sci. 2021;739:12039.

12 Beeks SA, Evans MR. Physical properties of biocontainers used to grow long-term greenhouse crops in an ebb-and-flood irrigation system. HortScience. 2013;48(6):732-7.

13 Sahari J, Sapuan SM. Natural fibre reinforced biodegradable polymer composites. Rev Adv Mater Sci. 2012;30(2):166-74.

14 Zhang Y, Zhu Q-J, Gao S, Liu S, Li L-H, Chen H-T. Optimization of Technological Parameters of Straw Fiber-Based Plant Fiber Seedling Pot Raw Materials. Appl Sci 2021, Vol 11, Page 7152 [Internet]. 2021 Aug 3 [cited 2021 Nov 1];11(15):7152. Available from: https://www.mdpi.com/2076-3417/11/15/7152/htm
https://www.mdpi.com/2076-3417/11/15/715...
-1515 Zhang X, Wang C, Chen Y. Properties of selected biodegradable seedling plug-trays. Sci Hortic (Amsterdam) [Internet]. 2019;249:177-84. Available from: https://doi.org/10.1016/j.scienta.2019.01.055
https://doi.org/10.1016/j.scienta.2019.0...
]. Oil palm empty fruit bunch (OPEFB) is one of the interesting and potential material for biopot reinforcement due to its high content of fibers (72%).

As the world's largest palm oil producer, Indonesia produce more than 50 million tons of crude palm oil (CPO) in 2020 and simultaneously generates the same amount of OPEFB as the waste of the CPO production process [1616 Haryanti A, Norsamsi, Sholiha PSF, Putri NP. Study of Palm Oil Solid Waste Utilization (in Indonesian). J Konversi. 2014;3(2):20-2.,1717 Erwinsyah, Afriani A, Kardiansyah T. Potential and Opportunities of Oil Palm Empty Fruit Bunches as Raw Material for Pulp and Paper: A Case Study in Indonesia (in Indonesian). J Selulosa. 2015;5(02):79-88.]. Comparing to other biomass, OPEFB seems to have a good potential to be utilized as reinforcing material in the production of planting container due to its abundance, low price, and high fiber content. OPEFB has been reported to contains good nutrient composition that potential to be used for improvement of soil structure and reduction of the uses of chemical fertilizers [1717 Erwinsyah, Afriani A, Kardiansyah T. Potential and Opportunities of Oil Palm Empty Fruit Bunches as Raw Material for Pulp and Paper: A Case Study in Indonesia (in Indonesian). J Selulosa. 2015;5(02):79-88.

18 Trisakti B, Mhardela P, Husaini T, Irvan, Daimon H. Effect of pieces size of Empty Fruit Bunches (EFB) on composting of EFB mixed with activated liquid organic fertilizer. IOP Conf Ser Mater Sci Eng. 2018;309(1).

19 Zahrim AY, Asis T, Hashim MA, Al-Mizi TMTM., Ravindra P. A Review on the Empty Fruit Bunch Composting: Life Cycle Analysis and the Effect of Amendment. Adv Bioprocess Technol. 2015;1-15.
-2020 Jaya JD, Nuryati N, Ramadhani R. Optimasi Produksi Pupuk Kompos Tandan Kosong Kelapa Sawit (TKKS) dan Aplikasinya pada Tanaman. J Teknol Agro-Industri [Internet]. 2015 Mar 22 [cited 2021 Feb 11];1(1):01. Available from: http://jtai.politala.ac.id/index.php/JTAI/article/view/24
http://jtai.politala.ac.id/index.php/JTA...
]. Investigation on the physical and mechanical performance of biopots reinforced with OPEFB has not been performed.

Physical and mechanical properties of biopots are determined by the reinforcement materials and also the matrix. Many natural and synthetic polymers have been used as matrix in the biopot production such as cassava starch, formaldehyde copolymer, polyethylene glycol, polyhydroxy butyrate, paraffin wax, and sodium alginate [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,55 Balestri E, Vallerini F, Seggiani M, Cinelli P, Menicagli V, Vannini C, et al. Use of bio-containers from seagrass wrack with nursery planting to improve the eco-sustainability of coastal habitat restoration. J Environ Manage [Internet]. 2019;251(July):109604. Available from: https://doi.org/10.1016/j.jenvman.2019.109604
https://doi.org/10.1016/j.jenvman.2019.1...
,77 Rafee SNAM, Lee YL, Jamalludin MR, Razak NA, Makhtar NL, Ismail RI. Effect of Different Ratios of Biomaterials to Banana Peels on the Weight Loss of Biodegradable Pots. Acta Technol Agric. 2019;22(1):1-4.,99 Sun E, Liao G, Zhang Q, Qu P, Wu G, Huang H. Biodegradable copolymer-based composites made from straw fiber for biocomposite flowerpots application. Compos Part B Eng [Internet]. 2019;165(November 2018):193-8. Available from: https://doi.org/10.1016/j.compositesb.2018.11.121
https://doi.org/10.1016/j.compositesb.20...
,2121 Seggiani M, Cinelli P, Balestri E, Mallegni N, Stefanelli E, Rossi A, et al. Novel sustainable composites based on poly(hydroxybutyrate-co-hydroxyvalerate) and seagrass beach-CAST fibers: Performance and degradability in marine environments. Materials (Basel). 2018;11(5):1-16.

22 Sartore L, Schettini E, Bignotti F, Pandini S, Vox G. Biodegradable Plant Nursery Containers from Leather Industry Wastes. Polym Compos. 2016;39(8):2743-50.
-2323 Evans MR, Hensley DL, Bailey LH, Star R. Plant Growth in Plastic , Peat , and Processed Poultry Feather Fiber Growing Containers. 2004;39(5):1012-4.]. Sodium alginate has been reported to have appropriate properties as a polymeric matrix because of its abundance, effectiveness in the gel formation, good mechanical performance, and affordable price [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,2424 Hecht H, Srebnik S. Structural Characterization of Sodium Alginate and Calcium Alginate. Biomacromolecules [Internet]. 2016 Jun 13 [cited 2021 Apr 19];17(6):2160-7. Available from: https://pubs.acs.org/doi/10.1021/acs.biomac.6b00378
https://pubs.acs.org/doi/10.1021/acs.bio...
]. This study was aimed to investigate the effects of the application of OPEFB as the reinforcement and various concentration of sodium alginate matrix on the physical, mechanical, structural, and morphological characteristics of the biopots.

MATERIAL AND METHODS

Material Preparation

The material used in this research was Oil Palm Empty Fruit Bunches (OPEFB). OPEFB waste was collected from the Palm Oil Processing Plant in Pelaihari, Indonesia. The material was crushed and sun-dried for 2-3 days to produce OPEFB with a moisture content below 10%. The material was then homogenized in size with a sieve (25 mesh). To get early information regarding the OPEFB material, lipid content, moisture content, and lignocellulose content were analyzed. In the production of biopots, sodium alginate was employed as a matrix that also acts as an adhesive. Prior to use, sodium alginate was combined with distilled water and agitated until a homogenous gel formed.

Production of Biodegradable Pot

Sodium alginate was dissolved in 50 mL of distilled water and stirred for 5 min to form a homogeneous gel. The OPEFB material (10 g) and glycerol (0.5 g) was then added to the adhesive solution and homogenized with a stirrer to create a ready-to-mold paste. Sodium alginate was employed at concentrations of 5% (Biopot-1), 10% (Biopot-2), and 20% (Biopot-3) of the weight of the OPEFB. The formulation of the biopot was put into an iron mold designed to resemble the desired shape of the pot with an upper diameter of 9 cm, a bottom diameter of 6 cm, and a height of 7 cm. The thermopressing process was employed to mold at a temperature of 150ºC for 5 min. Biopot was removed from the mold and stored in a dry container.

Physical Characterization

Moisture Content

The empty cup was dried for 15 min at 105ºC, cooled in a desiccator, and weighed (W 2 ). The weight of the biopot specimen was measured (W) and then put into the cup. Following that, the specimen was placed in a 105ºC oven for 4 hours or until the weight remained steady. The cup containing the sample was cooled in a desiccator and then weighed (W 1 ). The moisture was calculated using the following formula.

M o i s t u r e = W ( W 1 W 2 ) W × 100 % (1)

Water Absorption

Biopot dry specimens were weighed and marked as W 0 . The specimens were then immersed in distilled water for 15 and 30 min at room temperature and weighed. The excess water on the specimen's surface was gently wiped away with a damp cloth/tissue before weighing. W t represented the weight after immersion. Each of these treatments was repeated three times, and the average results were used to determine the water adsorption value (Q) using the equation below:

Q = W H 2 O W 0 × 100 % (2)

Note; WH2O=WtW0

W H 2 O = W e i g h t o f w a t e r a b s o r b e d

Density

The biopot specimens were prepared to a size of 20 mm × 30 mm. Their thickness was measured with a micrometer screw. Volume was calculated by multiplying the area and thickness of the specimen. Furthermore, the specimen was dried in an oven, weighed (W), and measured its density (d) using the following equation:

d = W V (3)

Colorimetric Analysis

A colorimeter (CR-400 Konica Minolta, Japan) was used to determine the color of the biopot. The CIELab color system (L* (a lightness factor); a* (redness factor); and b* (yellowness factor) was used to determine the color difference between biopot samples of various compositions.

Contact Angle Analysis

Contact angle analysis using plug-in drop analysis was used to determine the hydrophobicity of biopot specimens. Furthermore, the contact angle and hydrophobicity were determined. The instrument used in this test is a contact angle goniometer (Dataphysic Instrument, TBU 100).

Mechanical Characterization

Mechanical characteristics of biopot were investigated through the tensile test. Tensile strength, elongation at break, and other tensile properties are critical indicators of a biopot's performance and quality [2525 Castronuovo D, Picuno P, Manera C, Scopa A, Sofo A, Candido V. Biodegradable pots for Poinsettia cultivation: Agronomic and technical traits. Sci Hortic (Amsterdam). 2015;197:150-6.]. The test was carried out with three replications using prepared specimens of the biopot (25 mm ×30 mm) with a 2 mm/min extension rate. The following formulas were used to determine the tensile characteristics of the biopots:

T e n s i l e s t r e n g t h = s t r e s s = F A (4)

E l o n g a t i o n ( % ) = s t r a i n = Δ L L 0 × 100 % (5)

Note; F = Force; A = cross-sectional area;ΔL= length extension;L0= initial length

Structural and Morphological Characterization

Fourier Transform Infra-Red (FTIR) Analysis

The functional groups of the chemical components in the biopot composite mixture were qualitatively analyzed using FTIR. The samples were dried, pulverized, and pelletized with KBr before being examined by FTIR using the Shimadzu IR Prestige 21 instrument. Spectra were obtained in the wavelength range of 4000-600 cm-1 with 40 scans at a resolution of 4 cm-1.

X-ray Diffraction (XRD) Analysis

X-ray Diffraction (XRD) analysis aimed to identify the crystalline phase in the biopot sample. The test was carried out with the X-ray Diffractometer PANAanalytical-E'xpert Pro equipped with High Score Plus Software. The instrument was run with a Cu radiation source at a range of 2θ from 10º to 90º.

Scanning Electron Microscopy (SEM) Analysis

SEM analysis using the FEI Inspect-S50 SEM instrument was used to determine the surface of the biopot sample microscopically, which includes the material's surface topography and appearance. Micrographs obtained with magnifications of 2500×.

RESULTS AND DISCUSSION

OPEFB was the primary material used in the production of biopots. Drying, refining, and size sorting were carried out at this initial stage to obtain OPEFB fibers with homogeneous sizes. Additionally, OPEFB fiber was tested for moisture, lipid, and lignocellulose content in order to acquire uniform and suitable raw materials. Table 1 showed the initial characteristics of OPEFB material which were then used for further study.

In this study, biopots were made by combining OPEFB natural fiber with sodium alginate. In this mixture, the fiber functions as a reinforcement, while the sodium alginate acts as a matrix and adhesive. A total of 10 g of OPEFB was mixed with sodium alginate with variations of 5%, 10%, and 15% and then formed using the thermopressing method at a temperature of 150ºC for 5 min. The thermopressing process was chosen due to its simple technology, ease of use, and timeliness of application [2626 Abba HA, Nur IZ, Salit SM. Review of Agro Waste Plastic Composites Production. J Miner Mater Charact Eng. 2013;01(05):271-9.]. Figure 1 shows the biopots produced using this method.

Table 1
Physical and chemical characteristics of OPEFB fiber used in biopot production.

Figure 1
Physical appearance of the produced biopots - Biopot-1 (5% sodium alginate); Biopot-2 (10% sodium alginate); Biopot-3 (15% sodium alginate).

Furthermore, biopots were characterized to determine their suitability for use as an alternative planting container. Comprehensive characterization of biopots was then performed, including physical, mechanical, structural (chemical), and morphological characterization.

Physical Characteristics

Moisture content, water absorption, density, colorimetric and contact angle were the physical properties examined in this study. The moisture analysis revealed that the more sodium alginate in the biopot, the higher the moisture. Biopot-3 containing 15% sodium alginate showed the highest moisture of 8.18%. Meanwhile, Biopot-1 containing 5% sodium alginate showed the lowest moisture of 6.81% (Table 2). It is critical to understand the moisture of biopots in order to predict their susceptibility to damage caused by organisms such as bacteria and fungi, particularly during storage [1212 Beeks SA, Evans MR. Physical properties of biocontainers used to grow long-term greenhouse crops in an ebb-and-flood irrigation system. HortScience. 2013;48(6):732-7.,2727 Siwek P, Domagala-Swiatkiewicz I, Bucki P, Puchalski M. Biodegradable agroplastics in 21st century horticulture. Polimery. 2019;64(07/08):480-6.,2828 Kasirajan S, Ngouajio M. Polyethylene and biodegradable mulches for agricultural applications: A review. Agron Sustain Dev. 2012;32(2):501-29.]. On the other hand, the moisture of biopots could be allowed because it will contact with water while watering or when transferred to the soil in agricultural application.

Table 2
Physical properties of the examined biopots

The water absorption test was used to ascertain the specimen's interaction with the water. The application of biopots for planting containers will undoubtedly contact with water molecules in the environment. The material was immersed in distilled water for 15 and 30 min to determine its water absorption capacity. Biopot’s specimens with higher sodium alginate concentrations had higher water absorption than specimens with lower sodium alginate concentrations. Biopot-3 with 15% sodium alginate content showed highest water absorption of 236.74% at 15 min of immersion and 401.80% at 30 min of immersion, respectively. While, Biopot-1 containing 5% sodium alginate showed the lowest water absorption of 146.88% at 15 min of immersion and 300.87% at 30 min of immersion (Table 2). This finding is almost the same as the water absorption capacity of biopot made of tomato, hemp fiber, and cow manure which showed values of 190 % and 476% [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,1515 Zhang X, Wang C, Chen Y. Properties of selected biodegradable seedling plug-trays. Sci Hortic (Amsterdam) [Internet]. 2019;249:177-84. Available from: https://doi.org/10.1016/j.scienta.2019.01.055
https://doi.org/10.1016/j.scienta.2019.0...
]. The longer it is immersed, the higher the moisture in the biopot. The water absorption capacity of the biopot is determined by the constituent materials and is closely related to the porosity and density of the biopot [1515 Zhang X, Wang C, Chen Y. Properties of selected biodegradable seedling plug-trays. Sci Hortic (Amsterdam) [Internet]. 2019;249:177-84. Available from: https://doi.org/10.1016/j.scienta.2019.01.055
https://doi.org/10.1016/j.scienta.2019.0...
]. On the other hand, the ability to absorb water could also be an advantages to biopot, since it can be employed as a water reservoir when used in agricultural application [66 Calcagnile P, Sibillano T, Giannini C, Sannino A, Demitri C. Biodegradable poly(lactic acid)/cellulose-based superabsorbent hydrogel composite material as water and fertilizer reservoir in agricultural applications. J Appl Polym Sci. 2019;136(21):1-9.].

Another physical property observed in this study was density. Density indicates the compactness of the biopot’s ingredients. Density values are strongly dependant on fiber density and the degree of compression used during processing. In general, fiber composites have a relatively low density [33 Postemsky PD, Marinangeli PA, Curvetto NR. Recycling of residual substrate from Ganoderma lucidum mushroom cultivation as biodegradable containers for horticultural seedlings. Sci Hortic (Amsterdam) [Internet]. 2016;201:329-37. Available from: http://dx.doi.org/10.1016/j.scienta.2016.02.021
http://dx.doi.org/10.1016/j.scienta.2016...
,44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,99 Sun E, Liao G, Zhang Q, Qu P, Wu G, Huang H. Biodegradable copolymer-based composites made from straw fiber for biocomposite flowerpots application. Compos Part B Eng [Internet]. 2019;165(November 2018):193-8. Available from: https://doi.org/10.1016/j.compositesb.2018.11.121
https://doi.org/10.1016/j.compositesb.20...
]. Biopots made of OPEFB with sodium alginate had a density of 0.177-0.264 g/cm3 (Table 2). The higher the sodium alginate level, the higher the density, as alginate works as both a matrix and an adhesive in the mixture [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
]. Due to the high concentration of sodium alginate, the component materials' cohesiveness is increased, resulting in an increase in density. When compared with similar products from previous studies made from waste of tomato-hemp fibers [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
] and straw fibres [99 Sun E, Liao G, Zhang Q, Qu P, Wu G, Huang H. Biodegradable copolymer-based composites made from straw fiber for biocomposite flowerpots application. Compos Part B Eng [Internet]. 2019;165(November 2018):193-8. Available from: https://doi.org/10.1016/j.compositesb.2018.11.121
https://doi.org/10.1016/j.compositesb.20...
] as raw materials, which showed densities of 0.43 g/cm3 and 0.81 g/cm3, respectively, the biopots produced from this research were lighter, so that expected to be simpler in transportation and storage.

Colorimetric analysis was carried out to see the difference in the color and appearance of each biopots, as done in several studies [2929 Kaisangsri N, Kerdchoechuen O, Laohakunjit N. Biodegradable foam tray from cassava starch blended with natural fiber and chitosan. Ind Crops Prod. 2012 May;37(1):542-6.,3030 Sunardi S, Istikowati WT, Ishiguri F, Yokota S. FTIR spectroscopy and color change of wood for assessment and monitoring of softwood degradation by white-rot fungus Porodaedalea pini. AIP Conf Proc. 2018;2026(2018).]. Color values were expressed in lightness (L), redness (a), and yellowness (b) measured using a colorimeter. The lightness (L) of the combination tends to increase as the sodium alginate concentration in the mixture increases. Meanwhile, Yellowness (b) tends to decrease with the increasing concentration of sodium alginate. Similarly, as the concentration of alginate in the mixture increases, the redness (a) decreases slightly. The color of biopots is determined by two critical factors: the composition and the heating technique during thermopressing.

Figure 2
Colorimetric value of the tested biopots.

Another physical property analyzed in this study was the contact angle. In principle, the contact angle indicates the surface's wettability. Hydrophilic liquids have a contact angle of less than 90° with the solid surface, whereas hydrophobic (non-wetting) liquids have a contact angle of 90-180°. In this study, the contact angle of the examined biopot ranged from 81.67-103.72o . Biopot-3, which contained 15% sodium alginate, was hydrophilic based on the contact angle value, whereas Biopot-1 and Biopot-2 were classified as hydrophobic (non-wetting). The contact angle is further influenced by the material's porosity, roughness, and heterogeneity of the surface topography.

Figure 3
Contact angle of the examined biopots.

Figure 4
Contact angle of Biopot-3 with hydrophobic angle of <90o (a) and Biopot-2 with hydrophilic angle of >90o (b).

Mechanical characteristics

Mechanical characteristics of biopot were investigated through tensile test. Tensile properties are critical characteristics of biopots. The tensile properties studied were ultimate tensile strength (UTS), elongation at break, and stress-strain curve. UTS is the maximum stress that a specimen can withstand when stretched. Biopot-1, Biopot-2 and Biopot-3 had a UTS value of between 0.617 and 1.290 MPa. Increasing the sodium alginate content resulted in a rise in the biopot's UTS value. This value is almost similar to that of biopots originating from wood fiber of 0.1 M.Pa [1515 Zhang X, Wang C, Chen Y. Properties of selected biodegradable seedling plug-trays. Sci Hortic (Amsterdam) [Internet]. 2019;249:177-84. Available from: https://doi.org/10.1016/j.scienta.2019.01.055
https://doi.org/10.1016/j.scienta.2019.0...
]; tomatoes and hemp fiber of 0.46 MPa [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
]. In several studies, adding plasticizers such as polyester and polyethylene glycol to the biopots resulted in higher UTS values as shown in previous studies [2222 Sartore L, Schettini E, Bignotti F, Pandini S, Vox G. Biodegradable Plant Nursery Containers from Leather Industry Wastes. Polym Compos. 2016;39(8):2743-50.,2525 Castronuovo D, Picuno P, Manera C, Scopa A, Sofo A, Candido V. Biodegradable pots for Poinsettia cultivation: Agronomic and technical traits. Sci Hortic (Amsterdam). 2015;197:150-6.].

The elongation value ranged between 4.79% and 6.77% during cracking, with the maximum value occurring at Biopot-3. The relationship between tensile strength and elongation is illustrated on a stress-strain graph that showed a similar pattern for all biopots. When the curve reaches the peak point (UTS), there is a decrease in stress due to cracks in the test specimen. In general, all test specimens exhibited the same pattern, with a broad peak indicating that the test specimen was elastic (ductile fracture), as opposed to non-elastic specimens, which had sharper peaks (Figure 6) [1515 Zhang X, Wang C, Chen Y. Properties of selected biodegradable seedling plug-trays. Sci Hortic (Amsterdam) [Internet]. 2019;249:177-84. Available from: https://doi.org/10.1016/j.scienta.2019.01.055
https://doi.org/10.1016/j.scienta.2019.0...
].

The performances of the biopots were relatively better compared to other related or similar products of the previous research, such as biopot, biocontainer, and green polybag [33 Postemsky PD, Marinangeli PA, Curvetto NR. Recycling of residual substrate from Ganoderma lucidum mushroom cultivation as biodegradable containers for horticultural seedlings. Sci Hortic (Amsterdam) [Internet]. 2016;201:329-37. Available from: http://dx.doi.org/10.1016/j.scienta.2016.02.021
http://dx.doi.org/10.1016/j.scienta.2016...
,44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,99 Sun E, Liao G, Zhang Q, Qu P, Wu G, Huang H. Biodegradable copolymer-based composites made from straw fiber for biocomposite flowerpots application. Compos Part B Eng [Internet]. 2019;165(November 2018):193-8. Available from: https://doi.org/10.1016/j.compositesb.2018.11.121
https://doi.org/10.1016/j.compositesb.20...
,1515 Zhang X, Wang C, Chen Y. Properties of selected biodegradable seedling plug-trays. Sci Hortic (Amsterdam) [Internet]. 2019;249:177-84. Available from: https://doi.org/10.1016/j.scienta.2019.01.055
https://doi.org/10.1016/j.scienta.2019.0...
,2222 Sartore L, Schettini E, Bignotti F, Pandini S, Vox G. Biodegradable Plant Nursery Containers from Leather Industry Wastes. Polym Compos. 2016;39(8):2743-50.]. Table 3 shows the comparison of the physical and mechanical properties of the tested biopots with other related products. As shown, the tested biopots were better in three parameters of biopot quality (water adsorption, density, and tensile strength).

The biopot is also economically reliable because of its low production cost, either the material price or the processing cost. OPEFB is the waste of CPO production process and generally worthless. Sodium alginate is also can be obtained at the affordable price and it is only used in a small quantity of around 1 g for each single biopot. In addition, in term of time efficiency, thermopressing method is more preferable than the cold process which takes up to 3 days [44 Schettini E, Santagata G, Malinconico M, Immirzi B, Scarascia Mugnozza G, Vox G. Recycled wastes of tomato and hemp fibres for biodegradable pots: Physico-chemical characterization and field performance. Resour Conserv Recycl [Internet]. 2013;70:9-19. Available from: http://dx.doi.org/10.1016/j.resconrec.2012.11.002
http://dx.doi.org/10.1016/j.resconrec.20...
,3131 Jaya JD, Darmawan MI, Ilmannafian AG, Sanjaya L. Quality Green Polybag from Palm Oil Empty Fruit Bunch and Fiber Waste as Palm Oil Pre Nursery Media. Teknol Agro-Industri. 2019;6(2):127-40.,3232 Jaya JD, Ilmannafian AG, Maimunah. Utilization of Palm Oil Waste Fiber in Making Organic Pot. J Sains dan Teknol Lingkung. 2019;11(1):1-10.]. This is essential in efforts to save the storage space and working hour.

Figure 5
Ultimate tensile strength (UTS) and elongation at break of the examined biopots.

Figure 6
Curve of stress-strain of the examined biopots.

Table 3
Comparison of the physical and mechanical properties of the tested biopots with other related products

Structural and Morphological Characteristics

FTIR spectra

The FTIR test was performed to understand about the chemical linkages found in the biopot sample, which the different peaks indicate the typical chemical bonds. A biopot is a composite consisting of OPEFB fiber as reinforcement and sodium alginate as a matrix. The results showed that the spectra of Biopot-1, Biopot-2, and Biopot -3 were similar. Most of the peaks showed the characteristics of cellulose, hemicellulose, and alginate. Only the transmittance intensity was slightly different at certain peaks, indicated the difference in quantity of each functional groups. The infrared spectrum revealed a strong broad absorption band at 3321 and 3344 cm-1. It indicated the presence of stretching OH groups in cellulose and alginate compounds, which are associated with a high number of hydrogen bonds. Absorption bands at wavelengths 2945, 2943, and 2941 cm-1 were asymmetric stretching of CH, CH2, and CH3 (methylene and methyl group) in cellulose. The absorption bands at 1168 and 1166 cm-1 indicated the presence of C-O-C stretching vibration in cellulose and alginate. Similarly, the bands at 820 and 817 cm-1 showed a C-H deformation of the β-(1,4) glycosidic linkage in cellulose, as well as a C-H deformation of the linkage in alginate [3030 Sunardi S, Istikowati WT, Ishiguri F, Yokota S. FTIR spectroscopy and color change of wood for assessment and monitoring of softwood degradation by white-rot fungus Porodaedalea pini. AIP Conf Proc. 2018;2026(2018).,3333 Franco TS, Amezcua RMJ, Rodrìguez AV, Enriquez SG, Urquíza MR, Mijares EM, et al. Carboxymethyl and Nanofibrillated Cellulose as Additives on the Preparation of Chitosan Biocomposites: Their Influence Over Films Characteristics. J Polym Environ [Internet]. 2020;28(2):676-88. Available from: https://doi.org/10.1007/s10924-019-01639-0
https://doi.org/10.1007/s10924-019-01639...
].

Figure 7
FTIR Spectra of the examined biopots.

X-ray Diffraction (XRD) Analysis

X-ray diffraction (XRD) analysis was aimed to identify the crystalline phase in the biopot from OPEFB with the different content of sodium alginate. Diffraction patterns of Biopot-1, Biopot-2 and Biopot-3 can be seen in Figure 8, showing that the biopot material has an amorphous structure with 2θ angles being 21.69º, 22.01º and 22.03º, respectively. The peak intensity of the tested biopot showed a slight increase with increasing sodium alginate [(C6H7NaO6)n] in samples. Lignocellulosic fiber and sodium alginate are the main constituents of the biopots. Those materials are organic that naturally are irregular (amorphous) [3434 Kane SN, Mishra A, Dutta AK. Characterization and properties of sodium alginate from brown algae used as an ecofriendly superabsorbent. J Phys Conf Ser. 2016;755(1):1-6.

35 Zakaria S, Hamzah H, Murshidi JA, Deraman M. Chemical modification on lignocellulosic polymeric oil palm empty fruit bunch for advanced material. Adv Polym Technol. 2001 Dec 1;20(4):289-95.

36 Zhang J, Wang Y, Zhang L, Zhang R, Liu G, Cheng G. Understanding changes in cellulose crystalline structure of lignocellulosic biomass during ionic liquid pretreatment by XRD. Bioresour Technol. 2014;151:402-5.

37 Lai LW, Ibrahim M, Md Rahim N, Hashim EF, Ya'cob MZ, Idris A, et al. Study on composition, structural and property changes of oil palm frond biomass under different pretreatments. Cellul Chem Technol. 2016;50(9-10):951-9.
-3838 Lacerda VDS, Sotelo JBL, Correa-Guimarães A, Ramos PM, Navarro SH, Bascones MS, et al. Efficient Microwave-Assisted Acid Hydrolysis of Lignocellulosic Materials Into Total Reducing Sugars in Ionic Liquids. Cellul Chem Technol. 2016;50(7-8):761-70.]. This condition will affect the results of the XRD analysis of the biopots which are also amorphous as indicated by the absence of crystalline peaks.

Figure 8
X-ray diffractogram of the examined biopots.

Scanning Electron Microscope (SEM)

The morphology of the biopot, which was composed of fiber and sodium alginate, was examined using SEM analysis. On the surface of the Biopot-1 containing 5% sodium alginate (the smallest sodium alginate content), several porous cavities formed, indicating that the matrix could not completely fill the space between the fibers. It contrasts with Biopot-2 and Biopot-3, which contain higher sodium alginate (10% and 15% sodium alginate), showing denser morphology. A sodium alginate matrix strongly influences the level of porosity of the biopot. Additionally, biopots containing a higher concentration of sodium alginate (Biopot-3) had a smoother surface than biopots containing a lower concentration of sodium alginate (Biopot-1). The matrix acts as a filler, transferring tension to the fiber, forming a coherent link between the fiber and matrix surface, and protecting the fiber.

Figure 9
SEM micrograph of the examined biopots with 2500x magnification.

CONCLUSION

Biopots made of oil palm empty fruit bunches (OPEFB) and sodium alginate have the potential to be an environmentally friendly alternative to conventional planting containers. The quality of biopots is determined by product characteristics such as the material's physical, mechanical, structural (chemical), and morphological properties. The final characteristics of the biopot are primarily determined by the type of filler and matrix used, and this study used OPEFB and sodium alginate. The development and application of biodegradable containers are intended to be a novel method to achieve the sustainable agricultural objective of balancing productivity and environmental concerns.

Acknowledgments

The authors would like to acknowledge the Ministry of Education, Culture, Research and Technology of the Republic of Indonesia and Doctoral Program of Agricultural Science, Lambung Mangkurat University for supporting the research.

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  • Funding:

    This research was funded by Ministry of Education, Culture, Research and Technology of the Republic of Indonesia through a Doctoral Dissertation Research Grant (031/E4.1/AK.04.PT/2021).

Edited by

Editor-in-Chief:

Alexandre Rasi Aoki

Associate Editor:

Alexandre Rasi Aoki

Publication Dates

  • Publication in this collection
    27 June 2022
  • Date of issue
    2022

History

  • Received
    07 Dec 2021
  • Accepted
    09 May 2022
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