Abstract
During harvesting of mangroves, biomass waste such as mangrove barks are left unused. The study aims to valorize this waste by determining its chemical properties. Mangrove barks from the Rhizophora apiculata, Rhizophora mucronata, Bruguiera gymnorhiza, Bruguiera parviflora and Ceriops tagal were studied through Fourier transform infrared (FT-IR) spectroscopy and proximate, calorific, phenolic & tannin contents analysis. Bruguiera gymnorhiza has the highest calorific value and carbon content of all five varieties of bark, which can substitute as material for fuel and can be planted in deforested areas for it can absorb the most CO2. On the other hand, Rhizophora apiculata and Rhizophora mucronata have the highest ash content in all mangrove barks, which can be a good source of minerals for the soil. Ceriops tagal has the highest lignin, cellulose, hemicellulose, phenolic and tannin contents, which can be used as a fuel substitute and raw material source for biomass and bio-active compounds.
Introduction
The mangrove areas of Indonesia spans to 3.1 million hectares in total. On average, a primary forest can have 440–750 adult mangrove trees (yield) in a hectare (Giri et al. 2011). Mangrove forest area has a big role in protecting the environment as home to a diverse species of animals, coastal protection for fishery and decreasing the effect of climate change through its vast forest cover (Alongi 2008). In the last 50 years, Indonesia has lost a million hectares of mangrove forests due to deforestation and conversion of mangrove areas to shrimp ponds (Ilman et al. 2016; Paw and Chua 1991). Currently, the system has been changed and only concessions are allowed to sustainably harvest mangroves for its timber which is used in construction and paper industry. Around 80,000 hectares are being granted to PT Bintuni Utama Murni Wood Industries (BUMWI) in Bintuni Bay, West Papua, Indonesia. The company harvests mangrove trees at a rate of about 800–1000 hectares a year and converts its harvested wood into wood chips. Sixty-five per cent of the harvested trees are Rhizophora apiculata and Rhizophora mucronata variants, while the rest are Bruguiera gymnorhiza (15%), Bruguiera parviflora (10%) and Ceriops tagal (5%) mangrove species (Sillanpää et al. 2017).
During wood chip production, mangrove trees would undergo debarking prior to the chipping process. Currently, the debarking of wood is done on the forest site. Mangrove bark that is left in the area can reach between 1840 and 4490 kg per hectare (Lacerda et al. 2013). These waste materials are left on the harvested areas to enrich the soil, providing an avenue for secondary mangroves to grow on (Nordhaus et al. 2011). However, this becomes a problem because mangrove barks continue to pile up on site since debarking in the forest takes a longer time to finish than in the production area. Hence, there is a significant excess of these waste materials which poses environmental risks. In a study by Özgenç et al. (2017) and Pandey (2004), it was found via Fourier transform infrared (FT-IR) analysis that most tree barks contain cellulose, hemicellulose and lignin which provides an avenue for fuel applications and production of other value-added products.
In this work, the chemical properties of mangrove barks belonging to Rhizophora apiculata, Rhizophora mucronata, Bruguiera gymnorhiza, Bruguiera parviflora, and Ceriops tagal species in terms of their surface functional groups, proximate composition, calorific value and phenolic and tannin content were determined. The methods of analysis employed were: FT-IR spectroscopy (to obtain functional groups profile), standard gravimetric method (to determine proximate composition), bomb calorimetry (to measure calorific value) and colorimetric methods (to obtain phenolic and tannin contents). The chemical properties of each bark species then were used to identify and infer the potential uses of each variety of mangrove bark in various applications.
Materials and methods
Chemicals and raw materials
The bark of five mangrove species, namely Rhizophora apiculata, Rhizophora mucronata, Bruguiera gymnorhiza, Bruguiera parviflora and Ceriops tagal, were harvested along Bintuni Bay, West Papua, Indonesia. Samples were collected from three different locations and were harvested from an adult tree ready for harvesting, approximately 30–40 years of age. Bark of the same species was combined, dried for 5 days and powdered using a hand-operated blender. Folin-Ciocalteau phenol reagent, benzoic acid, gallic acid, methanol, anhydrous sodium carbonate (Na2CO3), polyvinylpolypyrrolidone (PVPP) were purchased from Sigma-Aldrich (St. Louis, MO,U.S.A.).
Proximate analysis
In the evaluation of biomass for its potential in fuel application, proximate analysis is usually done to measure the gross composition of the biomass in terms of moisture, ash, volatile matter and fixed carbon content (Basu and Basu 2013). The determination of proximate analysis is standardized through the American Society for Testing and Materials D3172-13 (ASTM D3172-13 2002). In this standard test, the order of determination is as follows: moisture, followed by volatile matter and finally ash and this is shown in Figure 1. The fixed carbon is computed by difference.
Sequence of steps for the determination of proximate composition.
In determining the %moisture of mangrove bark powders, about 2 g of sample was oven-dried at 105°C to constant weight. The %moisture of the sample was calculated based on the loss in weight of the powders. The dried sample obtained after this analysis was subjected to volatile matter content determination. For this analysis, the furnace was initially heated to 950°C. Then, the dried sample was covered and placed in the outer ledge of the furnace for 2 min with the furnace open. Afterwards, the sample was transferred to the edge of the furnace and heated for 3 min with the furnace open. Finally, the sample was moved to the rear of the furnace for 6 min with the furnace closed. The samples were then cooled and weighed. The %volatile matter of the sample was also calculated based on the loss in weight of the powders.
The sample obtained after analysis of volatile matter content was then subjected to ash content determination. The sample was heated to 750°C in the furnace for 6 h to constant weight. Similar to the prior analyses, the %ash of the samples was computed based on the loss of weight of the sample. Finally, the %fixed carbon of the sample was computed using Equation (1).
Fourier transform infrared spectroscopy
FT-IR spectroscopy is employed to examine the chemical structure of the wood bark for its reliability (Özgenç et al. 2017; Pandey 2004). It has been used to identify the presence of certain functional groups in a molecule, and the collection of absorption bands can confirm the identity of compounds and specific impurities in the sample. FT-IR spectroscopy was used to determine the presence of cellulose, hemicellulose and lignin on the surface of bark samples. The FT-IR spectra were generated using Cary 600 FT-IR spectrometer (Agilent Technologies) in attenuated total reflectance (ATR) mode. A total of 128 scans were obtained under ambient conditions within the frequency bands ranging from 380 to 4000 cm−1 for each mangrove bark sample. The differences in the functional groups and fingerprint bands for each sample were noted using Origin software.
Calorific value content
The gross calorific values of the mangrove bark samples were determined based on American Society for Testing Materials (ASTM D5865-13 2013) Standard Test Method for Gross Calorific Value of Coal and Coke Designation: D5865 – 10a using Parr 1108 oxygen bomb calorimeter. During the analysis, the pressure inside the calorimeter was maintained at 25 atm and less than 1 gram of sample was used. The computation of calorific value was based on the residual fuse wire after the analysis. Benzoic acid was used as a standard. Data correlation were noted using SPSS software.
Total polyphenol content
About 1 g of the sample was mixed with 50 mL methanol and was shaken at 40°C for 18 h until fully dissolved. An aliquot of the solution (about 1 mL) was diluted with water to 7 mL and was added with 0.5 mL of Folin-Ciocalteau phenol reagent. Exactly 5 min later, 1.0 mL of saturated sodium carbonate solution was added. The mixture was then diluted to 10 mL with water. The sample was incubated for 2 h at room temperature and the absorbance was determined at 765 nm using a spectrophotometer (UV-1700, Shimadzu Corp.). A standard calibration curve using gallic acid was also prepared to obtain the total polyphenol concentration as gallic acid equivalence (GAE) per amount of powder(Swain and Hillis 1959; Vieira et al. 2011).
Total tannin content
In determining the total tannin content of the sample, PVPP was used to precipitate the phenolic groups in tannins from solutions. The amount of PVPP used for this analysis was based on a mass ratio equal to 100:1 (PVPP: total polyphenol content). About 1 g of the sample was mixed with 50 mL methanol and was shaken at 40°C for 18 h until fully dissolved. The extract was diluted with water and the total phenolic content was determined. PVPP was then added to the solution, mixed and then the pH was adjusted to 3. The total phenolic content of the resulting mixture was again determined. The total tannin content (expressed as mg GAE per gram sample) was calculated as the difference between the initial and final total polyphenol content.
Results and discussion
Proximate composition of mangrove bark
It is presented in Figure 2 is the proximate composition of the mangrove bark. The proximate composition of each variety of mangrove bark has notable differences. The mangrove bark is largely composed of volatile matter across varieties, which is around 60% of the proximate composition of the samples. Volatile matter can comprise carbon oxides, hydrogen and traces of nitrogen compounds and it dictates ignition, flame stability and the mass of unburned carbon in the fly ash. The amount of volatile matter impacts fuel application of specific biomass, particularly its combustion characteristics (Miller 2013). A comparison of volatile matter content of some biomass shows that mangrove bark has relatively higher value, and is similar to lithotype coals (Brockway and Higgins 2013). This implies further that mangrove bark can be used as fuel substitute since coal is commonly used with volatile matter equal to 40%. In most practice, wood is usually used as fuel having a volatile matter ranging from 50% to 80% (White 1987).
Proximate composition of the bark of five mangrove species (values represent average for three trials; error bars represent standard deviation).
In terms of fixed carbon content, Bruguiera gymnorhiza has the highest fixed carbon content (18%), followed by Bruguiera parviflora (17%) among the mangrove bark species. The carbon content of the material is expressed in its fixed carbon amount. Fixed carbon content of mangrove bark is important as it signifies char yield after devolatilization (Zhang et al. 2009) and is dependent on mangrove habitat and species (Sudirman et al. 2014). Char yield refers to the remaining mass after complete degradation of the sample including residual carbon. This could mean that Bruguiera gymnorhiza and Bruguiera parviflora mangrove barks can retain high amounts of char when used as fuel or fuel substitute.
On the other hand, ash represents the total amount of mineral nutrients in the form of inorganic residue that is left after water and organic matter has been removed by heating. The ash content is an indicator for a raw material to be considered in fertilizer and composts applications (Petrovský et al. 2018). The ash content of Rhizophora apiculata (8.91%) and Rhizophora mucronata (8.41%) are much higher among the mangrove bark species.
FTIR spectra of mangrove bark
The infrared spectra of the mangrove bark samples of various species are characterized by the absorption peaks between 1030 and 3332 cm−1 regions as shown in Figure 3. The occurrence of peaks in the spectra of the mangrove bark are all similar but with differences in intensities. Each peak represents functional groups that are attributed to the presence of cellulose, hemicellulose and lignin in the bark samples. This is summarized in Table 1.
FR-IR spectrum of the bark of five mangrove species. Characteristic FT-IR bands of Mangrove Bark Components (Özgenç et al. 2017).
The peaks at 1232 cm−1 (C–O stretching) and the region between 1448 and 1606 cm−1 (C = C stretching, C – H bond, O –H in plane deformation and C = O stretch vibration) are attributed to the lignin content of the bark samples. On the other hand, the absorption peak at 1030 cm−1 corresponds to C–O stretching and this is attributed to the presence of hemicellulose. The bands at 2917 cm−1 (C–H stretching) and 3332 cm−1 (O–H stretching) were attributed to the cellulose content of the sample.
In all the observed peaks, Ceriops tagal species imparts the strongest intensities. This is followed by Bruguiera gymnorhiza, Rhizophora mucronata, Rhizophora apiculata and finally Bruguiera parviflora. These results would indicate that Ceriops tagal contains the highest cellulose, hemicellulose and lignin contents among the mangrove species. In a study by Demirbaş (2001), a direct relationship was established between the lignin content and higher heating value (HHV) of biomass fuels. A material with high lignin content would also have higher HHV.
Calorific values of mangrove bark
Basically, the heating value is the amount of heat produced by complete combustion of a material and it is measured as a unit of energy per unit mass or volume of a sample. The heat of combustion of a material is expressed by the higher and lower heating values. HHV is the gross calorific value, and it is defined as the amount of heat released when a material is combusted and the products have returned to a temperature of 25oC (ÖzyuǧUran and Yaman 2017).
The calorific values (kJ g sample−1) of mangrove bark are shown in Figure 4. Bruguiera gymnorhiza has the highest calorific value (65 kJ g−1) followed by Rhizophora mucronata (47 kJ g−1) and Ceriops tagal (37 kJ g−1). Both Rhizophora apiculata and Bruguiera parviflora have the lowest gross calorific value among the samples tested. These results indicate that Bruguiera gymnorhiza can be the best alternative for solid fuel among the mangrove species studied as it has the highest heating value.
Calorific values (kJ/g sample) of the bark of five mangrove species (values represent average for three trials; error bars represent standard deviation).
A comparison of Figures 2 and 4 reveals that Bruguiera gymnorhiza has the highest fixed carbon (18%) and has the highest calorific value among the mangrove species. Materials with high fixed carbon were found to have high HHV (Pérez-Arévalo et al. 2015). Bruguiera parviflora has the highest volatile matter (63%) and Rhizophora apiculata has the lowest (57%). The role of volatile matter in combustion is high, accounting from 70% to 80% of the energy created (White 1987). However, a comparison of Figures 3 and 4 shows that Ceriops tagal has a relatively low HHV even if it contains the highest lignin. In a study by White (1987), it was found that extractives (non-chemically bound components like sucrose, protein, ash, chlorophyll and waxes) in biomass samples could also affect the HHV of a material even at high lignin content.
Total phenolic and tannin content of mangrove bark
The total polyphenol contents of the mangrove bark expressed as GAE are shown in Figure 5. Ceriops tagal had the highest phenolic content at 140.78 GAE, followed by Bruguiera gymnorhiza (119.14) and Bruguiera parviflora (87.47). The difference in total polyphenol contents between the variety of both Bruguiera spp. and Rhizophora spp. is significant. Between the same species, Rhizophora apiculata has 12 times the amount of polyphenol compared to Rhizophora mucronata while Bruguiera gymnorhiza has 38% more polyphenol compared to Bruguiera parviflora.
Total Phenolic Content of Mangrove Bark (values represent average for three trials; error bars represent standard deviation).
Total tannin contents of mangrove bark are shown in Figure 5. The total tannin contents of the mangrove bark samples are also expressed in mg GAE per gram sample. Among the barks, Ceriops tagal had the highest tannin content of 125.64 GAE, followed by Bruguiera gymnorhiza (124.13) and Bruguiera parviflora (85.4). The difference in tannin contents between the variety of both Bruguiera spp. and Rhizophora spp. is significant. Between the same species, Rhizophora apiculata has twice the amount of polyphenol compared to Rhizophora mucronata while Bruguiera gymnorhiza has 45% more tannin content compared to Bruguiera parviflora. Figure 5 also shows that phenolic content and tannin content of the different mangrove bark are correlated as there is negligible difference per variety.
Ceriops tagal bark may be processed further to get valuable chemical compounds like tannin that will serve as another product from mangroves. A study by Tan and Kassim (2011) has shown that the choice of extraction solvents greatly affects the phenolic and tannin contents extracted from mangrove bark. Using alcohol, the total phenolic content of the Rhizophora apiculata bark is at 8.57 GAE but using 70% acetone and 30% water, its total phenolic content is at 191.82 GAE while its tannin content remains the same. As the study used methanol as the main extraction solvent, total phenolic content may differ if it were to use other solvents; in this way, other phenolic compounds may be extracted.
Conclusions and recommendations
The current work describes the chemical properties of different waste mangrove bark in Bintuni Bay, West Papua, Indonesia in terms of functional groups, proximate and chemical composition. The proximate composition and high heating values of mangrove bark indicate that this material can be utilized for fuel and fuel-substitute applications. This is also supported by the functional groups present in the bark, in which these groups are attributed to the presence of cellulose, hemicellulose and lignin in the samples. The phenolic and tannic compounds content of the bark signifies that they can be exploited for bio-compounds production such as tannins and natural colourants.
Further studies should focus on the elucidation of other chemical properties, as well as mechanical and functional properties, in order to explore other possible applications of the mangrove bark. This would lead then to the proper utilization of these waste materials. Since mangrove bark is found to have potential in fuel applications, future researches should also be geared towards developing fuel products from these materials. Moreover, extraction of bio-compounds should also be proceeded coupled with optimization experiments.
Conflict of interest
On behalf of all authors, the corresponding author states that there is no conflict of interest.
Footnotes
Acknowledgements
We would like to thank the management BUMWI for providing data and the accommodation while the study is being conducted in the mangrove area of Bintuni Bay, West Papua, Indonesia. We also like to thank the Chemical Engineering Laboratories of the University of San Carlos where experimental analysis was conducted. We acknowledge the Department of Science and Technology-Engineering Research and Development for Technology Philippines for the research and the scholarship grant of Rocky Marius Q. de Ramos.
Disclosure statement
No potential conflict of interest was reported by the authors.
