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Article

Development of a Binderless Particleboard from Brown Seaweed Sargassum spp.

by
Jérôme Bauta
1,
Guadalupe Vaca-Medina
1,
Christine Delgado Raynaud
1,2,
Valérie Simon
1,
Virginie Vandenbossche
1 and
Antoine Rouilly
1,*
1
Laboratoire de Chimie Agro-Industrielle (LCA), Université de Toulouse, INRAE, Toulouse INP, 31030 Toulouse, France
2
Centre d’Application et de Traitement des Agro-Ressources (CATAR), Toulouse-INP, 4 allée Emile Monso, 31030 Toulouse, France
*
Author to whom correspondence should be addressed.
Materials 2024, 17(3), 539; https://doi.org/10.3390/ma17030539
Submission received: 22 December 2023 / Revised: 17 January 2024 / Accepted: 20 January 2024 / Published: 23 January 2024
(This article belongs to the Special Issue Recent Developments in Bio-Based Particleboards and Fiberboards)

Abstract

:
Since 2010, huge quantities of Sargassum spp. algae have been proliferating in the Atlantic Ocean and stranding on Caribbean beaches, causing major economic, environmental, and health problems. In this study, an innovative high-density binderless particleboard was developed using uniaxial thermo-compression coupled with a cooling system. The raw material consisted of ground Sargassum seaweeds pre-treated by twin-screw extrusion with water to remove sea salt. The raw material and the particleboards were produced by using various analytical techniques such as Dynamic Vapor Sorption (DVS), Differential Scanning Calorimetry (DSC), Dynamic Mechanical Analysis (DMA), or Thermogravimetric Analysis (TGA). The experimental conditions for thermo-compression (temperature, pressure, time) were evaluated. The best thermo-compression conditions tested were 200 °C, 40 MPa pressure for 7.5 min. This resulted in a particleboard with high density (up to 1.63 ± 0.02 g/cm3) and high flexural strength/modulus (up to 32.3 ± 1.8 MPa/6.8 ± 0.2 GPa, respectively), but a low water contact angle of 38.9° ± 3.5°. Thermal analyses revealed the effect of alginates on the mechanical properties of particleboards. This work opens the door to a new way of adding value to Sargassum seaweed, using the whole algae with minimal pre-treatment.

1. Introduction

For the past decade, Sargassum spp. seaweeds have been a major problem for the Caribbean coastline. Originally restricted to the Sargasso Sea, since 2011, they have colonized a large part of the Atlantic Ocean, forming a belt between West Africa and South America, more than 8000 km long [1]. Every year, the Caribbean coasts experience massive strandings between January and September. In the record year of 2018, for example, more than 3.2 × 103 m3/km·month washed up on the Mexican coast [2]. Similarly, the island of Guadeloupe has estimated that between 20,000 and 50,000 tons (dry matter basis) of seaweeds are deposited on its coasts every year [3].
These strandings cause health, economic, and environmental problems for local populations. Beach-cast seaweeds start to decompose, releasing sulphurous gases (H2S in particular) and ammonia [3]. Local residents are exposed both acutely and chronically, which can sometimes lead to serious symptoms such as abdominal pain, respiratory problems, eye and skin disorders, or headaches [4].
The decomposition of algae in the water releases particles of organic matter and leachates, leading to a series of harmful effects. These include reduced luminosity under Sargassum mats, increased turbidity, changes in water color, and hypoxia [5]. These effects lead to the death of fish, crustaceans, seagrasses, and corals, as well as to a reduction in their biodiversity [5,6,7]. The strandings themselves lead to accelerated beach erosion, accentuated by the mechanical gathering of beach-cast seaweed [8].
The impact of seaweed collection is significant in financial terms: some of the areas affected are heavily dependent on tourism. Mexico, for example, has invested 17 million dollars in the collection of seaweed [9]. Some hotels are also spending large sums to install barriers, purchase machinery and boats, and transport them by truck [2]. Studies have also shown the impact of the gases emitted by Sargassum algae on metal corrosion, a phenomenon which may affect household appliances of local residents [10].
A number of studies have been conducted to find ways of using this humongous mass of Sargassum seaweeds in the agricultural, construction, and energy sectors [11,12,13]. However, there are a number of problems associated with the seaweed composition, the most challenging being their heavy metal content [14,15]. In fact; alginates, one of the main structural polysaccharides of brown algae, are known to chelate heavy metals, particularly arsenic [16,17]. This property could be useful in the treatment of polluted water [18,19], but it also makes other valorization pathways, where heavy metals are proscribed, more complex.
Biopolymer-based materials constitute one possible way to recover the material. However, most studies into the conversion of Sargassum seaweeds into materials focus on using only certain components of the plant. Examples include the use of alginates for biodegradable films [20,21,22], which can be used in the packaging sector, cellulose and alginates for biocomposites [23], and the transformation of Sargassum into char for soil decontamination [24] or into ash for use as pozzolanic material [25]. In addition to collection, transport, and packaging, the extraction of compounds of interest may require numerous physical and chemical processing stages. Other studies or commercial products use whole algae as fillers in biocomposites to modulate their properties: in shoe soles [26], building blocks [27], paper [28], or asphalt [29], for example.
No work on the manufacture of rigid materials solely made from algae appears to have been published. In this study, the first example of rigid binderless particleboard composed exclusively of Sargassum was developed by uniaxial thermo-compression coupled with a cooling device that improves the overall properties of such materials. This method has already been used to produce films from minimally processed red algae [30] and has been used extensively to develop panels from a variety of lignocellulosic materials. However, it has yet to be used to produce dense thick materials from biomasses based on alginate and cellulose such as brown algae. The raw material was processed by twin-screw extrusion to remove most of its bound sea salt and heavy metals. The solid residue obtained was then physically processed by Dynamic Vapor Sorption (DVS) and Thermogravimetrical Analysis (TGA) in order to study its capacity to be transformed into a bio-based material. The operating conditions for thermo-compression were studied in terms of temperature, mold pressure, and compression time in order to maximize flexion modulus and flexural strength. The mechanical properties of the particleboards were measured by three-point flexural tests. In order to investigate the impact of alginates on the mechanical properties of particleboards, thermal analyses (DMA, DSC) were conducted. This study could represent a first step toward the usage of whole seaweed specimens to produce 100% Sargassum materials for a wide range of applications (construction, design, etc.).

2. Materials and Methods

2.1. Sample Preparation

Sargassum seaweeds were collected on a beach in Punta Cana, Dominican Republic, then roughly washed with fresh water and sundried before shipping. The raw seaweeds were then coarsely ground using an Electra VS 1 hammer mill (Electra, Poudenas, France), then sieved on a TN1800 screening machine (Ritec, Saint-Paul-Trois-Châteaux, France) with a 1 mm sieve size to remove the excess sand. Their dry matter, mineral matter, and alginate contents were determined in a previous work [31]. Commercial sodium alginates were purchased from Sigma-Aldrich (Saint-Louis, MO, USA) and used as received.
The raw material used for thermo-compression was obtained after the pre-treatment of raw seaweeds by twin-screw extrusion with an Evolum 25 Lab Extruder (Clextral, Firminy, France). This treatment was used to wash the seaweeds with water and take away as much sea salt and heavy metals as possible. The screw profile used in this study is presented in Figure S1 and is composed of three main zones: the feeding, mixing, and pressing zones. First, Sargassum seaweeds were added to the feeding zone at a rate of 1.40 ± 0.04 kg/h DW (Dry Weight), followed by the injection of water at a Liquid/Solid ratio of 2.0. The temperature was kept constant inside the extruder at 30 °C. In the mixing zone, the seaweeds and solvent were intimately mixed by two series of bilobed paddles. Finally, in the pressing zone, reverse pitched screws exerted a strong compression and shearing force, leading to the separation of a liquid phase by filtration. Both the bilobes and reverse pitched screws helped reduce and homogenize the size of the Sargassum particles.
This process also allowed to recover a solid residue referred to as the “extrudate”. The extrudate was then dried at 50 °C for 24 h and then equilibrated under controlled conditions (25 °C and a relative humidity (RH) of 50%) for at least 2 weeks until a constant weight was achieved.

2.2. Thermo-Compression

The materials specimens were obtained by uniaxial compression of the extrudate (or commercial alginate powder) using a MAPA50 PEI hydraulic press (Pinette Emideceau, Chalon sur Saône, France) equipped with induction-heating plates and a water-cooling system (Roctool, Le-Bourget-du-Lac, France). This system enabled the press to be heated and cooled quickly. A total of 20 g of extrudate were loaded without any additive into a room temperature, three-piece 7 cm × 7 cm square steel mold. The temperature, pressure applied to the mold, and compression time were evaluated as shown in Table 1, while a cooling time of 10 min was kept constant. The resulting binderless plate was then cut into 1 cm × 5 cm specimens which were equilibrated under controlled conditions as described above for at least 1 week for further analyses. Two plates were obtained for each experimental condition tested, making it possible to obtain at least 10 specimens for the mechanical tests.

2.3. Characterization of Extrudate and Materials

Physicochemical and thermal analyses were performed on both the Sargassum extrudate and the particleboards. The moisture and ash contents of the extrudate were determined following the French standards NF EN ISO 18134-2 and NF EN ISO 18122, respectively [32,33]. The particle size of the extrudate was determined with an AS 200 Basic vibratory sieve shaker (Retsch, Haan/Duesseldorf, Germany) equipped with different sieves (mesh sizes: 2000–1000–800–500–200–125 µm). Its apparent and tapped density were measured with a Densitap ETD-20 (Granuloshop, Chatou, France).
An elemental analysis was performed on the raw material and extrudate using the AETE-ISO platform (OSU OREME/Université de Montpellier, Montpellier, France) with an iCAP Q ICP-MS (Thermo Scientific, Waltham, MA, USA).
An adsorption isotherm for the extrudate was conducted with a DVS Advantage System (Surface Measurement System, Alperton, UK) using 15 different RH steps (from 0 to 95%), with a dm/dt of 2 × 10−3%/min.
A Thermogravimetric Analysis (TGA) of the extrudate was performed using a TGA 2 Star System (Mettler-Toledo, Columbus, OH, USA) under 20 mL/min nitrogen flow using the following cycle: from 25 °C to 500 °C at 5 °C/min, then from 500 °C to 900 °C at 20 °C/min. A Derivative Thermogravimetry Analysis (DTGA) was then conducted using the TGA curve. A Dynamic Mechanical Analysis (DMA) was performed on the extrudate, sodium alginate powder, and materials in single cantilever mode using a Tritec 2000 (Triton Technology, Nottinghamshire, UK) equipped with a liquid nitrogen cooling system. Measurements were performed from −50 °C to 150 °C at a heating rate of 2 °C/min, with a displacement of 50 μm and at oscillation frequencies of 1 Hz and 10 Hz. For powder samples, steel pockets were used to perform the DMA analysis. A Differential Scanning Calorimetry (DSC) analysis was performed on the extrudate, sodium alginate, and particleboards using a DSC 1 (Mettler-Toledo, Columbus, OH, USA) and 40 µL aluminum capsules. The temperature gradients were as follows: from 25 °C to 80 °C, from 80 °C to 25 °C, and from 25 °C to 150 °C at 20 °C/min under a 50 mL/min nitrogen flow.
Optical images of the extrudate and materials were obtained with a SMZ1500 binocular loupe (Nikon, Tokyo, Japan), a Hirox HRX01 digital optical microscope (Hirox, Tokyo, Japan), and a Redmi Note 9 pro phone (Xiaomi, Beijing, China). Scanning Electron Microscopy (SEM) images of particleboards were obtained with a Quanta 450 (FEI, Hillsboro, OR, USA), with a 130 Pa water vapor partial pressure in the chamber and a high voltage of 12.50 kV. The SE microscope was equipped with a 30 mm2 silicone drift detector for elemental analysis.
A three-point flexion test was performed on the specimens using a H5KT Benchtop tester (Tinius Olsen, Horsham, PA, USA). A one-way Analysis of Variance (ANOVA) was performed on the results using the XLSTAT 2014.5.03 software, associated with a Shapiro–Wilk test (α = 0.05) to check the normality of residual data, a Levene’s test on the median (α = 0.05) to assess homoscedasticity, and a Tukey’s HSD (Honestly Significant Difference) test for multiple comparisons. The density of the material was obtained by buoyancy in cyclohexane. A specimen was weighted in air and in cyclohexane and its density dspecimen was calculated using Formula (1):
d s p e c i m e n = W a × d c d a W a W c × c o r r + ρ a
where da and dc are the densities of air and cyclohexane, respectively, Wa and Wc are the weights of the specimen in air and immerged in cyclohexane, respectively, corr is a corrective coefficient for hydrostatic thrust due to the device being equal to 0.99983, and ρa is the density of air. Five specimens were weighed for each experimental condition.
Finally, the wettability of particleboards was estimated by measuring the water contact angles with a DGD-MCAT-V8 (GBX Scientific LTD., Tallaght, Ireland) by averaging 10 measurements.

3. Results and Discussion

3.1. Characterization of the Raw Seaweeds and Extrudate

The extrudate obtained by twin-screw extrusion was a solid fraction made up of inhomogeneous particles, as seen on Figure 1. Macroscopically, it showed no traces of sand or salt stuck to the particles. Its mineral content decreased from 36.5 ± 0.1 %DW to 26.5 ± 0.2 %DW. The ICP-MS analysis showed that the twin-screw extrusion extracted between 12.0% (Pb) and 51.1% (Na) of the elements analyzed, and, in particular, 25.0% of the cobalt, 25.9% of the cadmium, and 37.5% of the arsenic initially present in the algae (Figure S2). The apparent density of the extrudate was 0.39 ± 0.03 g/cm3, while its tapped density was 0.48 ± 0.03 g/cm3.
Extrusion has allowed a reduction in the granulometry of the seaweed: most of the raw seaweed was a few millimeters to a few centimeters in size, while the particles of extrudate were almost all less than 2 mm long. (Figure S3). Almost half of the particles were larger than a millimeter, while the other half were evenly distributed between 200 µm and 1000 µm. Visually, the largest particles appeared to be composed exclusively of blade and thallus fragments, while the finest fractions also included floats. For this study, the extrudate was not ground after extrusion in order to eliminate as many steps as possible in the development of the material. However, a review from Pintiaux et al. in 2015 showed that a fine and homogeneous particle size, generally, has a positive effect on mechanical properties of binderless particleboards [34].
The sorption and desorption isotherms of water vapor for the extrudate are shown in Figure 2. The high hydrophilicity of the extrudate is immediately apparent. At 90% relative humidity, a mass gain of 64.2% is observed. By way of comparison, Simo-Tagne and coworkers showed that, for four types of exotic wood, the mass gain was only 16% to 18% at a relative humidity of 90% [35]. This tendency to uptake water may be linked to its alginate content: it has been shown that calcium alginates, for example, can uptake up to 200% of their initial weight in water at 90% RH [36]. Under the conditioning conditions applied to the Sargassum extrudate in this study prior to the thermo-compression (50% RH), a moisture content of 14.8% was reached.
Figure 3 represents the thermogravimetric analysis conducted on the extrudate. The result obtained is in agreement with the thermograms obtained by López-Aguilar et al. in 2020 on Sargassum spp. [37]. There are four peaks at 112 °C, 260 °C, 312 °C, and 735 °C for DTAG. The first peak corresponds to the volatilization of the water present in the extrudate. The second peak can be attributed to the decomposition of alginates, confirmed by numerous TGA and DSC studies of purified alginates [38] (Table 3), [39] (Tables 2 and 3). In particular, Soares et al. (2004) [40] noted an endothermic peak around 248 °C in a DSC analysis of sodium alginates. The third peak may be linked to the major devolatilization step in fucoidans described by Matusiak et al. [41]. Kristanto et al. also showed, using DSC and TGA, that cellulose exhibited a degradation peak at around 330 °C [42]. The loss of mass at higher temperatures can be attributed to the decarbonation of alginates forming different species (Na2CO3, CaCO3…) and, then, to their own decarbonation, leaving ashes rich in Na2O, CaO, and metals [37,39].

3.2. Study of Thermo-Compression Experimental Parameters of Sargassum Extrudate

For the thermo-compression stage, the compression temperature and duration ranges were chosen to ensure the homogeneity of the particleboard obtained. With temperatures and times outside these ranges, the boards were visually undercooked or overcooked, and their structural integrity was not maintained during demolding or handling. The materials obtained by thermo-compression were, for the most part, smooth and homogeneous, as shown in the photographs in Figure 4. No particles were discernible either on the surface or on the edge of the materials, except for under the mildest applied conditions. The plates were between 2.5 mm and 3.0 mm thick in all conditions. The particles observed on the surface by MEB were grains of potassium chloride KCl, as shown in Figure S4. High levels of KCl have already been reported by Milledge et al. in the ashes of Sargassum samples [43]. However, no explanation was given in this study for these high levels. The presence of KCl crystals on the surface of the sample could itself be explained by the evaporation of the water contained in the extrudates on the surface of the material during compression [34].
Figure 5 represents the flexion modulus and flexural strength of the specimens obtained while varying the temperature (a), applied pressure (b), and compression time (c). The results obtained ranged from 1.9 ± 0.5 GPa/6.8 ± 1.7 MPa for flexion modulus/flexural strength (conditions: 180 °C, 25 MPa of pressure, 5 min) to a maximum of 6.8 ± 0.2 GPa/32.3 ± 1.8 MPa (conditions: 180 °C, 100 MPa of pressure, 10 min).
With regard to temperature, there was an increase in flexural modulus up to 200 °C and an increase in flexural strength up to 220 °C, reaching 5.6 ± 0.5 GPa and 30.1 ± 1.7 MPa, respectively. The results obtained are consistent with the thermogravimetric analyses conducted on the extrudate. Indeed, alginates, one of the main structural polymers present in algae, begin to degrade at around 200 °C, with a peak at 260 °C. An excessive degradation of the alginate matrix above 220 °C could explain the reduction in the mechanical properties of particleboard above this temperature. However, the partial degradation of alginates and other seaweed polysaccharides can lead to the formation of simple sugars and short-chain carbohydrates [44,45]. These sugars and carboxylic acids could both recombine under high temperatures and pressures and act as intrinsic binders between biopolymers, in particular by hydrogen bonding. This phenomenon has already been described as “self-bonding” by others [44,46].
Regarding the applied pressure, a large difference was visible between the low values at 25 MPa and the plateau reached from 40 MPa, resulting in a flexural modulus between 4.5 ± 0.7 GPa and 5.1 ± 0.3 GPa and a flexural strength between 21.4 ± 1.4 MPa and 27.1 ± 3.1 MPa. The mechanical properties also increased with the compression time, reaching 6.8 ± 0.2 GPa and 32.3 ± 1.8 MPa of flexural modulus/flexural strength for 10 min of compression. However, there was no clear difference between 7.5 min and 10 min of compression. Thus, a sufficiently high compression temperature seems necessary in order to activate the “self-bonding” mechanism and to allow the mobility of the carbohydrate chains, although an excessively elevated temperature would be detrimental on account of the degradation of the carbohydrate matrix of the Sargasso algae.
The materials obtained in this study generally exhibited flexural moduli and flexural strengths in the upper range of those obtained with other biomasses using the same molding process, although they have a different type of polysaccharide matrix than the common lignocellulosic system. It is worth mentioning the work of Uitterhaegen et al. on coriander cake resulting in a panel with a flexural modulus and flexural strength of 4.5 ± 0.4 GPa and 27.6 ± 1.3 MPa, respectively (experimental conditions: 205 °C, 21.6 MPa, 5 min) or that of Theng et al. resulting in a panel with higher mechanical characteristics (flexural modulus/flexural strength 8.6 ± 1.5 GPa/50.3 ± 9.0 MPa, experimental conditions: 200 °C, 22.3 MPa, 5 min) [47,48]. In comparison, a commercial pure sodium alginate material obtained in this study following the same process (experimental conditions: 180 °C, 100 MPa, 5 min) showed a higher flexural strength of 52.5 ± 4.2 MPa but a lower flexural modulus of 6.1 ± 0.1 GPa. These slightly weaker mechanical properties of Sargassum-based particleboards compared to boards made with pure alginate may, however, be balanced by the fewer extraction and processing steps required for their manufacture.
The wettability measurement conducted on the particleboard presenting the best mechanical properties in this study (experimental conditions: 200 °C, 100 MPa, 5 min) resulted in a water contact angle of 38.9° ± 3.5° just after the drop had been deposited (t = 0) and in the total disappearance of the drop after 60 s. This value is lower than that recorded for materials obtained from other biomasses. For example, Evon et al. found a water contact angle of between 70° and 90° at t = 0 and an angle of 35° after 160 s for a sunflower cake panel under the best conditions tested [49]. Danish et al. found angles between 90° and 110° at t = 0 and between 60° and 100° at t = 60 s for panels based on oil palm trunk and Acacia mangium wood trunks [50]. However, the low value in this study is consistent with the high water adsorption capacity of Sargassum extrudate reported by the DVS analysis.
The best conditions for thermo-compression of Sargassum extrudates in this study were found: a temperature of 200 °C, a pressure on the mold of 40 MPa, and a compression time of 7.5 min. This takes into account not only the results from the mechanical tests, but also the minimization of energy costs associated with the thermo-compression technique by the selection of milder experimental conditions (40 MPa of pressure instead of 100 MPa and 7.5 min of compression instead of 10 min). These conditions result in a particleboard with a flexion modulus that is equivalent to and a flexural strength that is only 38% inferior to the plate obtained with sodium alginate, even though the algal matrix is far more complex than pure alginates. This may show that it is possible to obtain particleboards based on Sargassum with high mechanical properties without going through a cumbersome, multi-stage alginate extraction process [51].

3.3. Impact of Experimental Conditions on Density

For the three experimental parameters studied, density seems to follow the same trend as that observed for the flexural modulus and maximum stress (Figure S5): with respect to temperature, an increase in density was observed up to 200 °C (reaching a maximum value of 1.63 ± 0.02 g/cm3) before a decrease; with respect to applied pressure, a plateau was reached after 40 MPa, leading to a density between 1.60 ± 0.02 g/cm3 and 1.62 ± 0.01 g/cm3. Finally, with respect to compression time, a plateau was also observed between 7.5 min and 10 min for a maximum density of 1.63 ± 0.01 g/cm3.
The improvement in mechanical properties could be directly related to the increase in material density. Indeed, Pintiaux et al. determined that a higher density within the material led to a higher contact surface between the particles [52]. As a result, more hydrogen bonds and Van der Waals forces can bind the particles together. Similarly, Okuda et al. found that, for lignocellulosic panels, the density influenced the chemical changes within the material (notably, the condensation of lignin in Okuda’s study) and, therefore, the mechanical strength of the binderless particleboard [53]. This could be mitigated by the thickness of the samples: samples obtained from a similar process with cellulose have shown orthotropic internal structures with sides and faces denser than the core of the specimens [54].

3.4. Role of Alginates during Thermo-Compression Process of Sargassum Particleboard

In order to try to explain the transformations within the material leading to the high mechanical properties of Sargassum particleboards, DMA and DSC analyses were conducted. Pure commercial sodium alginate, taken as the main component of the seaweed structural matrix [55], was also analyzed for comparison with Sargassum extrudate and its particleboard. The specimen used in these analyses was the one with the best mechanical properties (thermo-compression conditions: 180 °C, 100 MPa, 10 min).
The results for thermal analyses are shown in Figure 6. In the DMA study (Figure 6a), the evolution in modulus and loss factor Tan(δ) of the particleboard with temperature are also presented in Figure S6. The α-relaxation temperatures (Tα) obtained, indicated by arrows on Figure 6b, were 73.0 °C, 92.2 °C, and 98.1 °C for sodium alginate, Sargassum extrudate, and particleboard, respectively. DMA analyses can provide valuable information to compare α-relaxation temperatures of powders and compressed materials. Powder analysis is specific, as it does not allow to measure modulus, but it is interesting for biopolymer thermal analysis, as it is very sensitive and show clearly the effect of water evaporation in this temperature range through the broadening of the peak in Tan(δ).
For the DSC analysis, only the first heating is presented (25 °C to 80 °C), as the other gradients (80 °C to 25 °C and 25 °C to 120 °C) showed no apparent transition, which means that this transition is non-reversible. The Tg observed was lower than the Tα presented previously, with 49.4 °C, 57.1 °C, and 64.2 °C for sodium alginate, Sargassum extrudate, and particle board, respectively. For sodium alginate, some physical aging is observed on the DSC trace, as it happens when purified biopolymers are stored in the glassy state. α-relaxation temperatures at 1 Hz correspond to the mechanical manifestations of the glass transition and are often observed at higher temperatures relative to Tg measurements by DSC. Also, a slight endothermic peak was observed for sodium alginate, probably corresponding to a relaxation of the polymer chains.
These analyses could demonstrate the impact of alginates as a thermoplastic matrix in the Sargassum seaweed complex structure during the production of binderless particleboards. First, a higher Tg was obtained for the Sargassum extrudate than for sodium alginate. This could indicate a matrix effect on chain mobility. In fact, as alginates interact with other polymer chains in the extrudate, they have less mobility and, therefore, need more energy to rearrange themselves. The Tg of the particleboard was also higher than those of the extrudate. This may be due to compression forcing new inter- and intra-biopolymer interactions that increase density, leading to a decrease in mobility between the chains and, once again, greater energy required to rearrange the polymer chains.

4. Conclusions

This study allowed to obtain the first binder-free particleboard based on whole Sargassum seaweeds by thermo-compression using twin-screw extrusion as a pre-treatment step. Various analytical methods were performed to examine the characteristics of the Sargassum extrudate. The best experimental parameters for thermo-compression in this study were as follows: a temperature of 200 °C, a mold pressure of 40 MPa, and a compression time of 7.5 min. The materials obtained through this process presented a high density and a relatively high flexural strength/modulus, but a low water contact angle explained by its high hydrophilic character due to alginate presence. The different transition temperatures obtained for pure sodium alginate, Sargassum extrudate and the particleboard showed the important role played by the thermoplastic behavior of alginates in the mechanical properties of the materials developed. Seaweed-based materials also showed a lower Tg and Tα than the extrudate and alginate powder because of their complex matrix and the interactions that take place between the different polysaccharides.
For future work, it may be possible to optimize the pre-treatment of the algae in order to influence the chemical form of the polysaccharides (alginate/alginic acid, for example) present in Sargassum, which could improve the mechanical properties of the resulting materials. In addition, these materials were determined to be very hydrophilic; this property may be of interest in applications where rapid degradation of materials is required. Otherwise, work could be conducted to improve the water resistance tests of Sargassum materials by developing treatment before or after thermo-compression, which could widen the possible range of applications. The preparation of materials by thermo-compression could nevertheless constitute an interesting way of using Sargassum seaweed for various industries (construction, design, etc.). As the processing of seaweed into materials presented in this study is fairly straightforward, companies in the areas most affected by strandings could easily develop new products based on this technology, for instance as biodegradable packaging.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/ma17030539/s1, Figure S1: Screw profile used for Sargassum pre-treatment by twin screw extrusion; Figure S2: Elements extracted from raw seaweeds by twin-screw extrusion with water; Figure S3: Particle size distribution in the extrudate; Figure S4: Elemental analysis of the particles observed at the surface of a particleboard by SEM; Figure S5: Influence of Temperature, pressure on the mold and compression duration on the density of Sargassum-based material; Figure S6: DMA analysis of a particleboard obtained with the best experimental conditions.

Author Contributions

J.B.: Conceptualization, Methodology, Formal analysis, Investigation, writing—original Draft, writing—review & Editing, Visualization. G.V.-M.: Conceptualization, Methodology, writing—original Draft, writing—review & Editing, Supervision. C.D.R.: Methodology, writing—review & Editing, Funding acquisition. V.S.: Conceptualization, Methodology, writing—review & Editing, Funding acquisition, Supervision. V.V.: Conceptualization, Methodology, writing—review & Editing, Supervision. A.R.: Conceptualization, Methodology, writing—original Draft, writing—review & Editing, Supervision. All authors have read and agreed to the published version of the manuscript.

Funding

This research received a financial support from ANR Sargassum program for “Holistic approach for Sargassum valorization-SARGOOD” project supported by ANR (N°ANR-19-SARG-0002-02), FAPESP, INTERREG Caraïbes. This work certified EUR BioEco had benefited from the financial support of the French National Research Agency “Investissement d’avenir” Program (N°ANR-18-EURE-0021).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are contained within the article and supplementary materials.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Wang, M.; Hu, C.; Barnes, B.B.; Mitchum, G.; Lapointe, B.; Montoya, J.P. The Great Atlantic Sargassum Belt. Science 2019, 365, 83–87. [Google Scholar] [CrossRef] [PubMed]
  2. López Miranda, J.L.; Celis, L.B.; Estévez, M.; Chávez, V.; van Tussenbroek, B.I.; Uribe-Martínez, A.; Cuevas, E.; Rosillo Pantoja, I.; Masia, L.; Cauich-Kantun, C.; et al. Commercial Potential of Pelagic Sargassum Spp. in Mexico. Front. Mar. Sci. 2021, 8, 768470. [Google Scholar] [CrossRef]
  3. Agence Nationale de Sécurité Sanitaire Alimentation, Environnement, Travail (ANSES). Expositions aux Émanations d’algues Sargasses en Décomposition au Antilles et en Guyane. [PDF online]. 2017. Available online: https://www.anses.fr/fr/system/files/AIR2015SA0225Ra.pdf (accessed on 19 December 2023).
  4. Resiere, D.; Mehdaoui, H.; Florentin, J.; Gueye, P.; Lebrun, T.; Blateau, A.; Viguier, J.; Valentino, R.; Brouste, Y.; Kallel, H.; et al. Sargassum Seaweed Health Menace in the Caribbean: Clinical Characteristics of a Population Exposed to Hydrogen Sulfide during the 2018 Massive Stranding. Clin. Toxicol. 2020, 59, 1789162. [Google Scholar] [CrossRef] [PubMed]
  5. van Tussenbroek, B.I.; Hernández Arana, H.A.; Rodríguez-Martínez, R.E.; Espinoza-Avalos, J.; Canizales-Flores, H.M.; González-Godoy, C.E.; Barba-Santos, M.G.; Vega-Zepeda, A.; Collado-Vides, L. Severe Impacts of Brown Tides Caused by Sargassum Spp. on near-Shore Caribbean Seagrass Communities. Mar. Pollut. Bull. 2017, 122, 272–281. [Google Scholar] [CrossRef] [PubMed]
  6. Hendy, I.W.; Woolford, K.; Vincent-Piper, A.; Burt, O.; Schaefer, M.; Cragg, S.M.; Sanchez-Navarro, P.; Ragazzola, F. Climate-Driven Golden Tides Are Reshaping Coastal Communities in Quintana Roo, Mexico. Clim. Change Ecol. 2021, 2, 100033. [Google Scholar] [CrossRef]
  7. Rodríguez-Martínez, R.E.; Medina-Valmaseda, A.E.; Blanchon, P.; Monroy-Velázquez, L.V.; Almazán-Becerril, A.; Delgado-Pech, B.; Vásquez-Yeomans, L.; Francisco, V.; García-Rivas, M.C. Faunal Mortality Associated with Massive Beaching and Decomposition of Pelagic Sargassum. Mar. Pollut. Bull. 2019, 146, 201–205. [Google Scholar] [CrossRef] [PubMed]
  8. Dolique, F.; Sédrati, M.; Josso, Q. Impact des laisses végétales sur la dynamique des plages sableuses, Martinique, Petites Antilles. VVertigO-La Rev. Électronique En Sci. L’environnement 2021, 21, 1–19. [Google Scholar] [CrossRef]
  9. Chávez, V.; Uribe-Martínez, A.; Cuevas, E.; Rodríguez-Martínez, R.E.; van Tussenbroek, B.I.; Francisco, V.; Estévez, M.; Celis, L.B.; Monroy-Velázquez, L.V.; Leal-Bautista, R.; et al. Massive Influx of Pelagic Sargassum Spp. on the Coasts of the Mexican Caribbean 2014–2020: Challenges and Opportunities. Water 2020, 12, 2908. [Google Scholar] [CrossRef]
  10. Ahmed, M.S.; Lebrini, M.; Lescop, B.; Pellé, J.; Rioual, S.; Amintas, O.; Boullanger, C.; Roos, C. Corrosion of Copper in a Tropical Marine Atmosphere Rich in H2S Resulting from the Decomposition of Sargassum Algae. Metals 2023, 13, 982. [Google Scholar] [CrossRef]
  11. Desrochers, A.; Cox, S.-A.; Oxenford, H.A.; van Tussenbroek, B. Sargassum Uses Guide: A Resource for Caribbean Researchers, Entrepreneurs and Policy Makers; Centre for Resource Management and Environental Studies (CERMES): Bridgetown, Barbados, 2020. [Google Scholar]
  12. Rossignolo, J.A.; Felicio Peres Duran, A.J.; Bueno, C.; Martinelli Filho, J.E.; Savastano Junior, H.; Tonin, F.G. Algae Application in Civil Construction: A Review with Focus on the Potential Uses of the Pelagic Sargassum Spp. Biomass. J. Environ. Manag. 2022, 303, 114258. [Google Scholar] [CrossRef]
  13. Ali, O.; Ramsubhag, A.; Jayaraman, J. Application of Extracts from Caribbean Seaweeds Improves Plant Growth and Yields and Increases Disease Resistance in Tomato and Sweet Pepper Plants. Phytoparasitica 2023, 51, 727–745. [Google Scholar] [CrossRef]
  14. Gobert, T.; Gautier, A.; Connan, S.; Rouget, M.-L.; Thibaut, T.; Stiger-Pouvreau, V.; Waeles, M. Trace Metal Content from Holopelagic Sargassum Spp. Sampled in the Tropical North Atlantic Ocean: Emphasis on Spatial Variation of Arsenic and Phosphorus. Chemosphere 2022, 308, 136186. [Google Scholar] [CrossRef] [PubMed]
  15. Ortega-Flores, P.A.; Serviere-Zaragoza, E.; De Anda-Montañez, J.A.; Freile-Pelegrín, Y.; Robledo, D.; Méndez-Rodríguez, L.C. Trace Elements in Pelagic Sargassum Species in the Mexican Caribbean: Identification of Key Variables Affecting Arsenic Accumulation in S. fluitans. Sci. Total Environ. 2022, 806, 150657. [Google Scholar] [CrossRef]
  16. An, B.; Lee, H.; Lee, S.; Lee, S.-H.; Choi, J.-W. Determining the Selectivity of Divalent Metal Cations for the Carboxyl Group of Alginate Hydrogel Beads during Competitive Sorption. J. Hazard. Mater. 2015, 298, 11–18. [Google Scholar] [CrossRef]
  17. Mohammed, C.; Lalgee, L.; Kistow, M.; Jalsa, N.; Ward, K. On the Binding Affinity and Thermodynamics of Sodium Alginate-Heavy Metal Ion Interactions for Efficient Adsorption. Carbohydr. Polym. Technol. Appl. 2022, 3, 100203. [Google Scholar] [CrossRef]
  18. Coração, A.C.d.S.; dos Santos, F.S.; Duarte, J.A.D.; Lopes-Filho, E.A.P.; De-Paula, J.C.; Rocha, L.M.; Krepsky, N.; Fiaux, S.B.; Teixeira, V.L. What Do We Know about the Utilization of the Sargassum Species as Biosorbents of Trace Metals in Brazil? J. Environ. Chem. Eng. 2020, 8, 103941. [Google Scholar] [CrossRef]
  19. Saldarriaga-Hernandez, S.; Nájera-Martínez, E.F.; Martínez-Prado, M.A.; Melchor-Martínez, E.M. Sargassum-Based Potential Biosorbent to Tackle Pollution in Aqueous Ecosystems—An Overview. Case Stud. Chem. Environ. Eng. 2020, 2, 100032. [Google Scholar] [CrossRef]
  20. Bi, D.; Yang, X.; Yao, L.; Hu, Z.; Li, H.; Xu, X.; Lu, J. Potential Food and Nutraceutical Applications of Alginate: A Review. Mar. Drugs 2022, 20, 564. [Google Scholar] [CrossRef] [PubMed]
  21. Mohammed, A. Sargassum Inspired, Optimized Calcium Alginate Bioplastic Composites for Food Packaging. Food Hydrocoll. 2023, 135, 108192. [Google Scholar] [CrossRef]
  22. Santana, A.A.; Kieckbusch, T.G. Physical Evaluation of Biodegradable Films of Calcium Alginate Plasticized with Polyols. Braz. J. Chem. Eng. 2013, 30, 835–845. [Google Scholar] [CrossRef]
  23. Doh, H.; Dunno, K.D.; Whiteside, W.S. Preparation of Novel Seaweed Nanocomposite Film from Brown Seaweeds Laminaria japonica and Sargassum natans. Food Hydrocoll. 2020, 105, 105744. [Google Scholar] [CrossRef]
  24. Ranguin, R.; Delannoy, M.; Yacou, C.; Jean-Marius, C.; Feidt, C.; Rychen, G.; Gaspard, S. Biochar and Activated Carbons Preparation from Invasive Algae Sargassum Spp. for Chlordecone Availability Reduction in Contaminated Soils. J. Environ. Chem. Eng. 2022, 9, 105280. [Google Scholar] [CrossRef]
  25. Bilba, K.; Onésippe Potiron, C.; Arsène, M.-A. Invasive Biomass Algae Valorization: Assessment of the Viability of Sargassum Seaweed as Pozzolanic Material. J. Environ. Manag. 2023, 342, 118056. [Google Scholar] [CrossRef] [PubMed]
  26. Morgan, M.; Mexico Pioneers Recycled Seaweed Shoes. BBC 2019. Available online: https://www.bbc.com/news/blogs-news-from-elsewhere-47745641 (accessed on 10 January 2024).
  27. Programa e las Naciones Unidas Para el Desarrollo (PNUD) en América Latina y el Caribe. Sea Change—How Local Innovation in the Riviera Maya Is Turning an Invasion into an Industry. 2020. Available online: https://undplac.exposure.co/sea-change (accessed on 10 January 2024).
  28. Sargasse Project. Available online: https://sargasseproject.com/en/sargasse-project-add-value-to-the-seaweed-by-transforming-it/ (accessed on 10 January 2024).
  29. Salazar-Cruz, B.A. Investigation of the Performance of Asphalt Binder Modified by Sargassum. Constr. Build. Mater. 2021, 271, 121876. [Google Scholar] [CrossRef]
  30. Cebrián-Lloret, V. Sustainable Bio-Based Materials from Minimally Processed Red Seaweeds: Effect of Composition and Cell Wall Structure. J. Polym. Environ. 2023, 31, 886–889. [Google Scholar] [CrossRef]
  31. Bauta, J.; Calbrix, E.; Capblancq, S.; Cecutti, C.; Peydecastaing, J.; Raynaud, C.; Rouilly, A.; Simon, V.; Vaca-Medina, G.; Vandenbossche, V.; et al. Global Chemical Characterization of Sargassum spp. Seaweeds from Different Locations on Caribbean Islands: A Screening of Organic Compounds and Heavy Metals Contents. Algal Research, Unpublished work.
  32. International Organization for Standardization Solid Biofuels. Determination of Ash Content. Available online: https://www.iso.org/fr/standard/83190.html (accessed on 2 July 2023).
  33. International Organization for Standardization Solid Biofuels. Determination of Moisture Content—Oven DryMethod—Part 2: Total Moisture—Simplified Method. Available online: https://www.iso.org/fr/standard/71536.html (accessed on 2 July 2023).
  34. Pintiaux, T.; Viet, D.; Vandenbossche, V.; Rigal, L.; Rouilly, A. Binderless Materials Obtained by Thermo-Compressive Processing of Lignocellulosic Fibers: A Comprehensive Review. BioRes 2015, 10, 1915–1963. [Google Scholar] [CrossRef]
  35. Simo-Tagne, M.; Rémond, R.; Rogaume, Y.; Zoulalian, A.; Bonoma, B. Sorption Behavior of Four Tropical Woods Using a Dynamic Vapor Sorption Standard Analysis System. Maderas. Cienc. Y Tecnol. 2016, 18, 403–412. [Google Scholar] [CrossRef]
  36. Mignon, A. Alginate Biopolymers: Counteracting the Impact of Superabsorbent Polymers on Mortar Strength. Constr. Build. Mater. 2016, 110, 169–174. [Google Scholar] [CrossRef]
  37. López-Aguilar, H.; Kennedy-Puentes, G.; Gómez, J.; Huerta-Reynoso, E. Practical and Theoretical Modeling of Anaerobic Digestion of Sargassum Spp. in the Mexican Caribbean. Pol. J. Environ. Stud. 2020, 30, 1–11. [Google Scholar] [CrossRef]
  38. Sarmento, B.; Ferreira, D.; Veiga, F.; Ribeiro, A. Characterization of Insulin-Loaded Alginate Nanoparticles Produced by Ionotropic Pre-Gelation through DSC and FTIR Studies. Carbohydr. Polym. 2006, 66, 1–7. [Google Scholar] [CrossRef]
  39. Zohuriaan, M.J.; Shokrolahi, F. Thermal Studies on Natural and Modified Gums. Polym. Test. 2004, 23, 575–579. [Google Scholar] [CrossRef]
  40. Soares, J.P.; Santos, J.E.; Chierice, G.O.; Cavalheiro, E.T.G. Thermal Behavior of Alginic Acid and Its Sodium Salt. Ecl. Quim. 2004, 29, 57–63. [Google Scholar] [CrossRef]
  41. Matusiak, J.; Maciołek, U.; Kosińska-Pezda, M.; Sternik, D.; Orzeł, J.; Grządka, E. Textural and Thermal Properties of the Novel Fucoidan/Nano-Oxides Hybrid Materials with Cosmetic, Pharmaceutical and Environmental Potential. Int. J. Mol. Sci. 2022, 23, 805. [Google Scholar] [CrossRef] [PubMed]
  42. Kristanto, J.; Azis, M.M.; Purwono, S. Multi-Distribution Activation Energy Model on Slow Pyrolysis of Cellulose and Lignin in TGA/DSC. Heliyon 2021, 7, e07669. [Google Scholar] [CrossRef] [PubMed]
  43. Milledge, J.J.; Maneein, S.; Arribas López, E.; Bartlett, D. Sargassum Inundations in Turks and Caicos: Methane Potential and Proximate, Ultimate, Lipid, Amino Acid, Metal and Metalloid Analyses. Energies 2020, 13, 1523. [Google Scholar] [CrossRef]
  44. Diakite, M.-S. Influence des Paramètres de Prοcédés de Transfοrmatiοn Subis par la Matière Végétale: Fοcus sur les Fοnctiοnnalités Appοrtées par la Température et le pH. Thèse de Doctorat, Université de Rouen Normandie, Mont-Saint-Aignan, France, 2022. [Google Scholar]
  45. Holme, H.K.; Lindmo, K.; Kristiansen, A.; Smidsrød, O. Thermal Depolymerization of Alginate in the Solid State. Carbohydr. Polym. 2003, 54, 431–438. [Google Scholar] [CrossRef]
  46. Okuda, N.; Sato, M. Manufacture and Mechanical Properties of Binderless Boards from Kenaf Core. J. Wood Sci. 2004, 50, 53–61. [Google Scholar] [CrossRef]
  47. Uitterhaegen, E.; Labonne, L.; Merah, O.; Talou, T.; Ballas, S.; Véronèse, T.; Evon, P. Impact of Thermomechanical Fiber Pre-Treatment Using Twin-Screw Extrusion on the Production and Properties of Renewable Binderless Coriander Fiberboards. Int. J. Mol. Sci. 2017, 7, 1539. [Google Scholar] [CrossRef]
  48. Theng, D.; Arbat, G.; Delgado-Aguilar, M.; Ngo, B.; Labonne, L.; Mutjé, P.; Evon, P. Production of Fiberboard from Rice Straw Thermomechanical Extrudates by Thermopressing: Influence of Fiber Morphology, Water and Lignin Content. Eur. J. Wood Wood Prod. 2017, 77, 15–32. [Google Scholar] [CrossRef]
  49. Evon, P.; VanDenBossche, V.; Pontalier, P.-Y.; Rigal, L. Thermo-Mechanical Behaviour of the Raffinate Resulting from the Aqueous Extraction of Sunflower Whole Plant in Twin-Screw Extruder: Manufacturing of Biodegradable Agromaterials by Thermo-Pressing. AMR 2010, 112, 63–72. [Google Scholar] [CrossRef]
  50. Danish, M. Surface Measurement of Binderless Bio-Composite Particleboard through Contact Angle and Fractal Surfaces. Measurement 2019, 140, 365–372. [Google Scholar] [CrossRef]
  51. Mohammed, A.; Bissoon, R.; Bajnath, E.; Mohammed, K.; Lee, T.; Bissram, M.; John, N.; Jalsa, N.K.; Lee, K.-Y.; Ward, K. Multistage Extraction and Purification of Waste Sargassum natans to Produce Sodium Alginate: An Optimization Approach. Carbohydr. Polym. 2018, 198, 109–118. [Google Scholar] [CrossRef]
  52. Pintiaux, T.; Viet, D.; Vandenbossche, V.; Rigal, L. High Pressure Compression-Molding of α-Cellulose and Effects of Operating Conditions. Materials 2013, 6, 2240–2261. [Google Scholar] [CrossRef]
  53. Okuda, N.; Hori, K.; Sato, M. Chemical Changes of Kenaf Core Binderless Boards during Hot Pressing (II): Effects on the Binderless Board Properties. J. Wood Sci. 2005, 52, 249–254. [Google Scholar] [CrossRef]
  54. Pintiaux, T.; Heuls, M.; Vandenbossche, V.; Murphy, T.; Wuhrer, R.; Castignolles, P.; Gaborieau, M.; Rouilly, A. Cellulose Consolidation under High-Pressure and High-Temperature Uniaxial Compression. Cellulose 2019, 26, 2941–2954. [Google Scholar] [CrossRef]
  55. Li, Y.; Zheng, Y.; Zhang, Y.; Yang, Y.; Wang, P.; Imre, B.; Wong, A.C.Y.; Hsieh, Y.S.Y.; Wang, D. Brown Algae Carbohydrates: Structures, Pharmaceutical Properties, and Research Challenges. Mar. Drugs 2021, 19, 620. [Google Scholar] [CrossRef]
Figure 1. Picture (a) and binocular lens view (b) of the Sargassum extrudate.
Figure 1. Picture (a) and binocular lens view (b) of the Sargassum extrudate.
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Figure 2. Water sorption and desorption isotherm of the Sargassum extrudate.
Figure 2. Water sorption and desorption isotherm of the Sargassum extrudate.
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Figure 3. TGA (orange) and DTGA (blue) of the Sargassum extrudate.
Figure 3. TGA (orange) and DTGA (blue) of the Sargassum extrudate.
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Figure 4. Sargassum particleboards images: photograph of plates (a), binocular lens view (b), SEM image of the surface of a test specimen (c), and digital optical view of its fracture point (d).
Figure 4. Sargassum particleboards images: photograph of plates (a), binocular lens view (b), SEM image of the surface of a test specimen (c), and digital optical view of its fracture point (d).
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Figure 5. Influence of temperature (a), pressure (b), and compression time (c) on the flexion modulus and flexural strength of Sargassum particleboards. The other parameters used in this study are as follows: 100 MPa for 5 min (a), 180 °C for 5 min (b), 100 MPa at 180 °C (c). a–c letters on the graphs letters refer to Tukey’s HSD test.
Figure 5. Influence of temperature (a), pressure (b), and compression time (c) on the flexion modulus and flexural strength of Sargassum particleboards. The other parameters used in this study are as follows: 100 MPa for 5 min (a), 180 °C for 5 min (b), 100 MPa at 180 °C (c). a–c letters on the graphs letters refer to Tukey’s HSD test.
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Figure 6. Evolution of Tan(δ) with temperature at 2 Hz (a) and DSC thermogram (first heating) (b) for sodium alginate powder (green), Sargassum extrudate (blue), and a Sargassum particleboard (orange).
Figure 6. Evolution of Tan(δ) with temperature at 2 Hz (a) and DSC thermogram (first heating) (b) for sodium alginate powder (green), Sargassum extrudate (blue), and a Sargassum particleboard (orange).
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Table 1. Conditions studied for uniaxial thermo-compression of Sargassum extrudate.
Table 1. Conditions studied for uniaxial thermo-compression of Sargassum extrudate.
Temperature (°C)Applied Pressure (MPa)Compression Time (min)
Temperature140–160–180–200–220–2401005
Pressure18025–40–50–75–1005
Duration1801002.5–5–7.5–10
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Bauta, J.; Vaca-Medina, G.; Delgado Raynaud, C.; Simon, V.; Vandenbossche, V.; Rouilly, A. Development of a Binderless Particleboard from Brown Seaweed Sargassum spp. Materials 2024, 17, 539. https://doi.org/10.3390/ma17030539

AMA Style

Bauta J, Vaca-Medina G, Delgado Raynaud C, Simon V, Vandenbossche V, Rouilly A. Development of a Binderless Particleboard from Brown Seaweed Sargassum spp. Materials. 2024; 17(3):539. https://doi.org/10.3390/ma17030539

Chicago/Turabian Style

Bauta, Jérôme, Guadalupe Vaca-Medina, Christine Delgado Raynaud, Valérie Simon, Virginie Vandenbossche, and Antoine Rouilly. 2024. "Development of a Binderless Particleboard from Brown Seaweed Sargassum spp." Materials 17, no. 3: 539. https://doi.org/10.3390/ma17030539

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