Isolation of Microcrystalline Cellulose (MCC) from Rice Husk: A Review
Sylma Dhini Avitra1, David Fernando2, Marlyn Dian Laksitorini1,
Teuku Nanda Saifullah Sulaiman1*
1Department of Pharmaceutics, Faculty of Pharmacy, Universitas Gadjah Mada,
Daerah Istimewa Yogyakarta 55281, Indonesia.
2Department of Pharmaceutical Chemistry, Faculty of Pharmacy, Universitas Gadjah Mada,
Daerah Istimewa Yogyakarta 55281, Indonesia.
*Corresponding Author E-mail: tn_saifullah@ugm.ac.id
ABSTRACT:
Rice husk (RH) is a by-product of the rice milling process and is regarded as agricultural waste if not utilized properly. RHs are recognized to contain significant nutritional benefits, including cellulose, hemicellulose, lignin, hydrated silica, organic carbons, and potassium. One of the most often used cellulose derivatives in the food and pharmaceutical business is microcrystalline cellulose (MCC). MCC's isolation process consists of four stages, which are delignification, bleaching, hydrolysis, and drying. These steps are linked to various crucial reactions, including cellulose yield (%wt/wt), MCC yield (%wt/wt), and crystallinity index (%CrI). This review aims to identify the ideal parameters for the delignification, bleaching, hydrolysis, and drying processes involved in the extraction of MCC from RH. The effects of these parameters on the yield of cellulose, MCC, and CrI are also discussed. The result shows that alkaline pulping is usually utilized to treat 100% of the delignification process. MCC yield is negatively correlated with the number of delignification processes, with one step being the ideal amount. The cost-effective reagent for the bleaching process is NaClO, which also reduces CrI compared to samples that have not been bleached. For hydrolysis, HNO3 is utilized to provide higher yields of MCC. There is no association between the drying process and the three dependent variables, which is at odds with the current theory. Further investigation is required to ascertain the impact of the drying process's time, temperature, and technique in addition to the previously listed factors.
KEYWORDS: Delignification, Bleaching, Hydrolysis, Drying, Excipient.
INTRODUCTION:
RH, as a by-product of the shelling process, accounts for about 20% of total rice weight1. Despite its reputation as an environmental hazard2, it is known to have critical nutritional values, including cellulose, hemicellulose, lignin, hydrated silica, organic carbons, and potassium1,3–7. MCC is a naturally formed polymer that is made up of units of glucose linked to one another (see Figure 1).
Figure 1. Structure of Microcrystalline Cellulose
MCC is mainly made in four steps: delignification, bleaching, acid hydrolysis, and drying8,9. The advancements in various production, modification, and advanced applications of both MCC and NCC were reviewed by Haldar and Purkait, 202010. Another review, conducted by Belali et al., 201911, focused on the isolation of MCC and how it affects the post-compression properties of the material. However, neither the RH nor the optimization of the MCC separation method are highlighted in either Furthermore, Trache et al., 201612 covered the utilization of MCC in biocomposites as well as its characterization and separation. Apart from that, this review does not emphasize the improvement of MCC made with RH. The preparation and techniques used to characterize MCC for pharmaceutical excipients are also covered in a review by Cahyani et al., 20228. Unlike the prior review, this review does not focus on the characterization and optimization of MCC's isolated from RH.
To the author's knowledge, no other reviews have addressed this subject, particularly the improvement of MCC isolation from RH. A wide range of circumstances influences the efficiency of these stages, and this subject has been the subject of extensive optimization research. An evaluation is crucial to ascertain the ideal conditions for extracting MCC from RH, particularly about the solvents or methodologies employed in each processing stage. This review aimed to emphasize the application of solvents and procedures in optimizing the production of MCC from RH. The features of MCC generated by various isolation techniques using RH (particularly %CrI) are also examined in this research.
METHODS:
Several databases (Scopus, Google Scholar, and Pubmed) were used to extract potential articles. Boolean instructions were used to remove pointless journals from the search. (MCC or microcrystalline cellulose) AND “rice husk” AND isolation is included in the keyword search. After duplicates were removed, articles were rejected during each screening stage. There are 406 articles in all that have been collected that could be useful. Publications that focus on MCC isolation, provide data on the proportion of MCC yield, and were conducted within the last ten years (2013–2023) are included in this evaluation; other publications are disregarded. Following that, the articles are subjected to an abstract screening procedure before undergoing a second examination by two researchers. To be included, both researchers must approve an article; if one of them rejects it, a third party will be consulted. Eligible articles are also manually extracted using the snowballing process.
RESULTS AND DISCUSSION:
The stages of MCC’s isolation are associated with several essential responses, such as cellulose yield (% wt/wt), MCC yield (% wt/wt), and %CrI. Cellulose is typically acquired post-delignification, and MCC is generally derived via hydrolysis. CrI is employed to assess the degree of crystallinity in cellulose, indicating the proportion of crystalline vs amorphous cellulose in the sample13. Figure 2 provides a summary of each step's optimization parameter. Each phase and associated optimization parameter will be further highlighted.
Figure 2. Optimization of MCC Isolation from Rice Husk
Figure 3. MCC production from rice husk through delignification and hydrolysis process
Delignification:
The process of delignification is to separate lignocellulose into cellulose, hemicellulose, and lignin14. To optimize the process, lignin characteristics must be exploited during pre-treatment to produce pure cellulose. Phenylpropane molecules joined by many bonds to form a polymer with an aromatic structure is what makes up lignin12,15. Figure 4 is an illustration of the lignin structure which physically encloses microfibrils in a hydrophobic matrix and is covalently bound to hemicellulose so as to prevent hydrolysis of the cellulose polymer.
Several pulping sequences and techniques can be used to achieve RH delignification in various situations, including chemical, mechanical, and biological pulping. Table 3 provides a summary of these strategies' benefits and drawbacks. This finding is consistent with Tables 1 and 3, which demonstrate that alkaline pulping (NaOH) is typically used to treat 100% of the delignification process. It is also customary to experiment with various steps of delignification, time used, temperature ranges, stirring speeds, and NaOH concentrations in order to determine the optimal delignification procedure. The delignification method is assumed to be more optimal when cellulose or MCC is achieved. According to Table 1, the best conditions for the delignification process are NaOH 1M at 80°C for 1.5 hours without stirring; this results in an overall MCC of 83.5% and a CrI of 52.4%. However, as the data sets contain a variety of optimization parameters, this result does not demonstrate that a particular parameter or the use of stirring correlates with the yield of MCC.
Table 1. Delignification stage of rice husk microcrystalline cellulose extraction
|
Label |
ΣRH (g) |
Delignification 1x or 2x |
Washing |
Bleaching |
Hydrolysis |
Drying |
Yield Cellulose (%) |
References |
|||
|
Solvent |
T (⁰C) |
Duration |
Stirring |
||||||||
|
A1 |
100 |
NaOH 10% |
55 |
1.5 h |
Yes |
Yes |
Yes |
Yes |
Yes |
38.35 |
|
|
A2 |
36.14 |
||||||||||
|
A3 |
36.65 |
||||||||||
|
A4 |
10 |
NaOH 12% |
80 |
3 h |
Yes |
Yes |
Yes |
No |
No |
52.3 |
|
|
A5 |
10 |
NaOH 1M |
80 |
1.5 h |
Yes |
Yes |
Yes |
Yes |
Yes |
- |
|
|
A6 |
400 |
NaOH 5% |
120 |
0.75 h |
No |
Yes |
No |
Yes |
Yes |
- |
|
|
A7 |
- |
||||||||||
|
A8 |
400 |
NaOH 5% |
120 |
0.75 h |
No |
Yes |
Yes |
No |
Yes |
68.96 |
|
|
A9 |
10 |
NaOH 1M |
80 |
1.6 h |
No |
No |
Yes |
Yes |
Yes |
- |
|
|
A10 |
- |
||||||||||
|
A11 |
- |
||||||||||
|
A12 |
- |
||||||||||
|
A13 |
10 |
NaOH 1M |
80 |
1.5 h |
No |
Yes |
Yes |
Yes |
Yes |
- |
|
|
A14 |
- |
||||||||||
|
A15 |
- |
||||||||||
|
A16 |
200 |
NaOH 4M |
80 |
24 h |
Yes |
No |
Yes |
Yes |
Yes |
- |
|
|
A17 |
1500 |
NaOH 2% |
100 |
3 h |
No |
No |
Yes |
No |
Yes |
33.33 |
|
|
NaOH 17.5% |
80 |
1 h |
No |
Yes |
|||||||
|
A18 |
450 |
NaOH 2% |
100 |
3 h |
No |
No |
Yes |
Yes |
Yes |
- |
|
|
NaOH 17.5% |
80 |
1 h |
No |
Yes |
|||||||
|
A19 |
350 |
NaOH 4% |
80 |
2 h |
No |
Yes |
Yes |
No |
Yes |
15.2 |
|
|
NaOH 17.5% |
80 |
1 h |
No |
Yes |
|||||||
|
A20 |
350 |
HNO3 3% |
90 |
2 h |
No |
Yes |
No |
Yes |
Yes |
- |
|
|
NaOH 2% and Na2SO3 2% |
50 |
1 h |
No |
Yes |
Yes |
||||||
|
NaOH 17.5% |
80 |
0.5 h |
No |
Yes |
Yes |
||||||
Notes : Different labels represent samples that are treated in a different way according to the reference.
Table 2. The process of bleaching, hydrolysis, and drying of rice husk microcrystalline cellulose extraction
|
Label |
Bleaching |
Hydrolisis |
Drying |
Yield MCC (%) |
CrI (%) |
Ref. |
|||||
|
Solvent |
T (⁰C) |
Duration |
Acid |
T (⁰C) |
Duration |
Stirring |
|||||
|
A1 |
NaClO2 0.5% |
85 |
90 min |
HCl 2.5N |
105 |
20 min |
Yes |
Oven, 40⁰C at 20 h |
25.05 |
- |
|
|
A2 |
NaClO2 0.7% |
23.25 |
- |
||||||||
|
A3 |
NaClO2 1.0% |
22.75 |
64.74 |
||||||||
|
A4 |
NaClO 2.5% |
80 |
60 min |
- |
- |
- |
- |
- |
- |
58.73 |
|
|
A5 |
NaClO 5% |
80 |
18 min |
HNO3 1M |
80 |
30 min |
Yes |
Oven, 100⁰C constant weight |
- |
42 |
|
|
A6 |
- |
- |
- |
H2SO4 5%, CH3COOH 25%, H2O2 5% |
120 |
120 min |
No |
60⁰C at 24 h |
63.38 |
72.88 |
|
|
A7 |
HNO3 10%, CH3COOH 25%, H2O2 5% |
120 |
120 min |
No |
60⁰C at 24 h |
65.51 |
79.29 |
||||
|
A8 |
NaClO2 8g and CH3COOH 1.47% |
70 |
300 min |
- |
- |
- |
- |
60⁰C at 24 h |
- |
61.86 |
|
|
A9 |
NaClO 5% |
80 |
18 min |
HNO3 1M |
25 |
30 min |
Yes |
Dried, Not specified |
80.64 |
42.0 |
|
|
A10 |
HCl 1M |
60.58 |
37.0 |
||||||||
|
A11 |
HNO3 2M |
83.26 |
63.9 |
||||||||
|
A12 |
HCl 2M |
69.24 |
52.2 |
||||||||
|
A13 |
NaClO 5% |
80 |
18 min |
HNO3 0.5M |
80 |
30 min |
Yes |
Oven, 70⁰C at 24 h |
83.5 |
52.4 |
|
|
A14 |
H2SO4 0.5M |
80.6 |
49.7 |
||||||||
|
A15 |
HCl 0.5M |
81.8 |
54.2 |
||||||||
|
A16 |
NaClO 12.5% |
40 |
60 min |
H2SO4 98% |
60 |
60 min |
Yes |
Oven, 40⁰C at 24 h |
- |
47.6 |
|
|
A17 |
NaClO 3.2% |
40 |
120 min |
- |
- |
- |
- |
Oven, 60⁰C at 16 h, sifted, 60⁰C at 1 h |
- |
- |
|
|
A18 |
NaClO 3.2% |
40 |
120 min |
HCl 2.5N |
100 |
30 min |
No |
60⁰C |
17.11 |
- |
|
|
A19 |
NaClO |
40 |
40 min |
- |
- |
- |
- |
60⁰C at 1 h |
- |
- |
|
|
NaClO |
80 |
20 min |
|||||||||
|
A20 |
NaClO 3.5% |
Boiling |
20 min |
HCl 2.0 N |
Boiling |
15 min |
Yes |
Fluidized bed, 57-60⁰C at 1 h |
11.7 |
50 |
|
|
NaClO 1.75% |
100 |
5 min |
|||||||||
Notes : Different labels represent samples that are treated in a different way according to the reference.
Table 3. Comparison of Different Delignification Process14,15,26,27
|
Type |
Treatment |
Pros |
Cons |
|
Chemical Pulping |
Kraft/ Sulfate |
Variety of wood usage, efficient usage and recovery of product, requires less time |
High residual lignin, high energy usage, environmentally damaging, higher cost |
|
Neutral Sulfite |
Brighter pulp that is easy to bleach, higher yield (8-10%) than alkaline pulping, less time required |
Resinous softwoods, tannin-bearing hardwoods, and supplies containing bark are not tolerated, higher cost |
|
|
Acidic Sulfite |
Overcome low lignin and hemicelluloses pulp, less time required |
Emission of SO2 causes air pollution, higher cost |
|
|
Alkaline |
Odorless gas (environmentally friendly), less time required, high efficiency |
Higher cost |
|
|
Mechanical Pulping |
Size reduction, Temperature, Stirring and Pressure |
Cheaper to produce (about half the cost of chemical pulping), Higher accessibility to matrix |
High energy demand, weaker than chemical pulping, high lignin residual |
|
Semi-Chemical Pulping |
Mechanical and Chemical |
Higher accessibility to matrix, high efficiency and less time required |
High energy demand, high cost |
|
Biological Pulping |
Bacteria or fungi |
Low cost and energy demand |
Low efficiency and slower rate of lignin degradation (depends on microorganism used) |
The amount of delignification operations is found to have a negative correlation with the MCC yield. Single-step delignification produces a higher overall percentage of MCC (63.17% and 17.11%, respectively) than two-step delignification processes (Figure 5). Frequent use of these compounds produce byproducts that impede cellulose hydrolysis even more, lowering the process's yield28,29. It is impossible to determine a correlation between these factors and the yield percentage of cellulose, MCC, or CrI using the data set in Table 1. This is a result of the several studies that were conducted with varying sets of methods and report parameters (many of which are not reported based on Figure 5). More research is needed to discover how the solvent content, sample-to-solvent ratio, temperature, delignification time, and stirring technique affect the percentage yield of MCC, cellulose, and CrI from RH.
Bleaching:
In conjunction with delignification, bleaching processes use chemicals to increase the purity of cellulose30 and dissolve lignin from fibrous materials31. Oxidators, such as hydrogen peroxide (H2O2), sodium hypochlorite (NaClO), sodium chlorite (NaClO2), chlorine (Cl2), and ozone (O3) are frequently utilized in this bleaching process. The benefits and drawbacks of each bleaching chemical for enhancing pulp color are listed in Table 4. NaClO is the most commonly utilized (as seen in Table 2) in the bleaching process compared to NaClO2 and H2O2. This is due to its ease of acquisition and application, as well as its comparatively lower cost.
Table 4. Comparison of Different Bleaching Reagents26,32-34
|
Bleaching Phase |
Bleaching Treatment |
Molecular Formula |
Pros |
Cons |
|
Liquid phase bleaching |
Sodium Hypochlorite |
NaClO |
Cheaper than NaClO2, cost-effective, easy to obtain and use |
Unstable solution, degrade under sunlight |
|
Sodium Chlorite / Chlorine Dioxide |
NaClO2 / ClO2 |
Stable solution, longer shelf life |
More expensive than NaClO, ClO2 released is environmentally damaging |
|
|
Hydrogen Peroxide |
H2O2 |
Environmentally friendly, Surface friendly and widely used for dental bleaching |
Less aggressive (Compared to NaClO, and NaClO2), Less favorable in bleaching wood/ porous materials |
|
|
Gas phase bleaching |
Chlorine |
Cl2 |
Low cost (Compared to O3) |
Environmentally damaging to ozone layer |
|
Ozone |
O3 |
Environmentally friendly, Faster and stronger oxidation (Compared to Cl2) |
High cost (Compared to Cl2), Complicated equipment setups |
Lower levels of biochemical and chemical oxygen demand, color, adsorbable organic halides, and the formation of chlorophenolic compounds have been found when ozone is added, followed by ClO2 and hydrogen peroxide35. Table 2, however, illustrates that gas phase bleaching is not commonly utilized in laboratory settings for the purpose of whitening RH. This might be caused by the difficult standard conditions (such as the temperature and pressure), the high cost, the advanced materials, and the difficult equipment setup that must be completed in the laboratory. Surprisingly, the unbleached samples (Figure 4) have the highest %CrI, suggesting that the bleaching procedure has a negative correlation with the rise of %CrI of the samples.
Figure 4. Output visualization of %Cellulose, %MCC, and %CrI from various treatment (A1-A20 represent the data label obtained from Table 2 & 3, while any unavailable data were represented as 0)
These results also agree with those of Gümüşkaya (2002), who found that lignin removal using bleaching techniques might lead to an increase in the %CrI36. When comparing unbleached to bleached Eucalyptus pulps, higher intensity of X-ray diffraction patterns is also seen37, further indicating that the bleaching process may have a major influence on reducing the %CrI of RH. Meanwhile, it is impossible to draw conclusions about the link between different bleaching chemicals, concentration, temperature, and duration to %cellulose and %MCC. This is because the independent variables in the research that was included in this study are not evenly controlled, which leads to their unpredictability. Further research is required to conclude if these parameters have an impact on the yield of cellulose, MCC, and CrI.
Hydrolysis:
Various methods can be employed to extract and purify MCC, such as enzymatic hydrolysis38,39, acid hydrolysis40-42, and steam explosion43. Enzymatic hydrolysis yields a higher purity of MCC in comparison to acid hydrolysis. Nevertheless, the process of breaking down enzymes like cellulase is associated with significant expenses and limited effectiveness in the MCC synthesis44. The acid hydrolysis procedure is preferred over others because of its shorter time. In this degradation condition, the yield produced by H2SO4 could be less than HCl. This can be seen in Table 2 (A13-A15) which reported that the lowest yield of hydrolysis results was using H2SO4 compared to HCl and HNO3. HCl and H2SO4 are extremely corrosive45,46, so their utilization is taken into consideration during the development of MCC extraction. Alternatively, other weaker acids can be utilized, such as nitric acid.
HNO3 is a strong acid that is slightly weaker than HCl and H2SO4 based on its pKa value47. However, HNO3 is able to hydrolyze lignocellulose with lower cellulose degradation than HCl and H2SO4. This is proven by the fact that HNO3 preserves higher cellulose or MCC in several studies19-21. Studies using HNO3 for this process generate larger yields of %MCC (A9, A11, and A13) than other studies, as shown in Table 3 and Figure 5. In contrast, the majority of research with the lowest %MCC uses HCl to carry out the hydrolysis process (A1, A2, A3, and A18). The oxidative capacity of nitric acid, as opposed to HCl, likely facilitates the conversion of nitriles into carboxylic acids, hence increasing the yield of MCC from RH21. No research using phosphoric and citric acids to extract MCC from RH has come to our attention. Although phosphoric and citric acids haven't been employed as frequently as the previous acids to create MCC, they have been combined with strong acids to create Nanocrystalline Cellulose (NCC)48,49. More research needs to be done to determine whether employing these acids is feasible and cost-effective.
Table 5. Comparison of Different Hydrolysis Treatments21,44,50-53
|
Type of Treatment |
Hydrolysis Treatment |
Molecular Formula |
Pros |
Cons |
|
Acid Treatment |
Sulfuric Acid |
H2SO4 |
Cost-effective, most effective acid hydrolysis agent |
Extremely corrosive and hazardous, high energy usage, high sugar yield |
|
Hydrochloric Acid |
HCl |
Less aggressive, lower sugar yield, corrosive and hazardous than H2SO4 |
Lower efficiency and reaction time |
|
|
Nitric Acid |
HNO3 |
Produces the highest yield compared to H2SO4 and HCl |
Hazardous and high energy usage, not suitable in glucose production, more expensive compared to H2SO4 and HCl |
|
|
Enzymatic Treatment |
Cellulase |
Eco-friendly, high specificity, high efficiency, high purity MCC output |
Expensive, not effective, slow reaction rate |
|
|
Combined Treatment |
Cellulase and Acid Treatment |
High specificity, high efficiency, high purity output |
Expensive |
|
|
Steam Explosion / Autohydrolysis |
High pressure and temperature |
Applicable to various starting materials, high efficiency |
Not applicable as a pretreatment for acid hydrolysis, high energy usage |
|
Drying:
It has been demonstrated that the drying process significantly affects the MCC's porosity, morphology, form, aggregation, and CrI54,55. In order to create dry solids, the process of drying involves eliminating water and other liquids. Increasing or maintaining the material's qualities (such as its flowability) and material preservation are some of the process' goals56,57. Some technologies that can be used are spray drying58, freeze-drying/lyophilization, fluidized bed drying54, microwave-aided drying59, and oven drying16. Microwaves and ovens are the least expensive of the aforementioned solutions57-59.
Acid hydrolysis is not necessary when drying using microwaves during the delignification and bleaching processes. According to the findings of FTIR and XRD examinations, this is because amorphous non-cellulose chemicals have been eliminated59. However, this method has a drawback; namely, it is not easy to set the right temperature in its optimization60. This is evidenced by the absence of significant differences in particle size and CrI in three different temperature settings in the microwave method61. In addition, the oven method is the least expensive on a small scale when compared to other drying techniques. On a laboratory scale, this approach is frequently utilized to dry MCCs despite its lengthy duration. This is due to the fact that, in addition to its cost, it is the simplest to operate when compared to other drying techniques57. Table 3 illustrates this pattern as well. In this table, oven drying is used for the majority of the experimental processes, with temperature ranges of 40°C to 100°C and durations ranging from 1 to 24 hours.
The yield of MCC and cellulose is unaffected when the drying process alters the CrI, per theory. However, if the drying procedure is not adjusted, the water content may increase the MCC or cellulose yield unintentionally. Cellulosic fibers shrink during the drying process, which results in semi-irreversible pore closure and decreased fiber performance62. Because there are fewer amorphous patches as a result of this pore collapse, CrI is enhanced. A higher increase in the CrI is typically the result of more rigorous drying techniques. Products that are spray-dried, for instance, have more CrI than those that are not63,64. The data collected (Table 3 and Figure 5) do not display this pattern; in fact, it was not discovered that the CrI of the undried (or rather, that information was not available for A4) samples was lower than that of the dried ones. This is explained by the fact that the experiment ended at the bleaching stage, indicating that when discussing CrI, the bleaching stage is more important than the drying stage. Based on the currently available data, further research is necessary to accurately evaluate the impact of the drying process (temperature, duration, and method) on CrI.
CONCLUSION:
RH is one of the materials that has the potential to be isolated into MCC through delignification, bleaching, acid hydrolysis, and drying processes. To achieve the highest possible MCC, optimizing many factors at each stage of the process is necessary. The delignification method yielded the maximum percentage of MCC (83.5%) and a CrI of 52.4% while using a 1M NaOH solution at 80°C for 1.5 hours without stirring. Furthermore, it was shown that an increase in the number of delignification repetitions decreased the %MCC production. During the acid hydrolysis process, it was noted that HNO3 is preferable due to its ability to generate a substantial amount of cellulose and MCC yield. The final step, drying, impacts the physical properties of MCC. Although bleaching reduces the %CrI of samples, further study is needed because it is impossible to infer a relationship between the amount of cellulose and MCC and the various bleaching chemicals, concentrations, temperatures, and bleaching treatment times. This is because different research backgrounds were used to collect the independent variables, resulting in uneven control over them.
ABBREVIATIONS:
Cl2 = Chlorine
CrI = Crystallinity Index
H2O2 = Hydrogen Peroxide
MCC = Microcrystalline Cellulose
RH = Rice Husk
NaClO2 = Sodium Chlorite
NaClO = Sodium Hypochlorite
O3 = Ozone
ACKNOWLEDGEMENTS:
We especially acknowledge the Indonesia Endowment Fund for Education Agency (LPDP) from the Ministry of Finance of the Republic of Indonesia for supporting the publication of this paper.
REFERENCES:
1. Singh B. Rice husk ash. In: Waste and Supplementary Cementitious Materials in Concrete. Elsevier. 2018: 417-460. doi:10.1016/B978-0-08-102156-9.00013-4
2. Satbaev B, Yefremova S, Zharmenov A, et al. Rice Husk Research: From Environmental Pollutant to a Promising Source of Organo-Mineral Raw Materials. Materials. 2021; 14(15): 4119. doi:10.3390/ma14154119
3. Kolar P, Jin H. Baseline Characterization Data for Raw Rice Husk. Data Brief. 2019; 25: 104219. doi:10.1016/j.dib.2019.104219
4. Kordi M, Farrokhi N, Pech-Canul MI, Ahmadikhah A. Rice Husk at a Glance: From Agro-Industrial to Modern Applications. Rice Sci. Published online September 2023: S1672630823000963. doi:10.1016/j.rsci.2023.08.005
5. Phonphuak N, Chindaprasirt P. Types of Waste, Properties, and Durability of Pore-Forming Waste-Based Fired Masonry Bricks. In: Eco-Efficient Masonry Bricks and Blocks. Elsevier; 2015: 103-127. doi:10.1016/B978-1-78242-305-8.00006-1
6. Hayatun A, Jannah M, Ahmad A, Taba P. Synthetic Bioplastic Film from Rice Husk Cellulose. J Phys Conf Ser. 2020; 1463(1): 012009. doi:10.1088/1742-6596/1463/1/012009
7. Gao Y, Guo X, Liu Y, et al. A Full Utilization of Rice Husk to Evaluate Phytochemical Bioactivities and Prepare Cellulose Nanocrystals. Sci Rep. 2018; 8(1): 10482. doi:10.1038/s41598-018-27635-3
8. Cahyani I, Lukitaningsih E, Adhyatmika A, Sulaiman T. Preparation and Characterization of Microcrystalline Cellulose for Pharmaceutical Excipient: A Review. Trop J Nat Prod Res. 2022; 6(10): 1570-1575. doi:10.26538/tjnpr/v6i10.3
9. Sutiya B, Istikowati WT, Rahmadi A. Kandungan Kimia dan Sifat Serat Alang-alang (Imperata cylindrica) Sebagai Gambaran Bahan Baku Pulp dan Kertas. Published online 2012.
10. Haldar D, Purkait MK. Micro and Nanocrystalline Cellulose Derivatives af Lignocellulosic Biomass: A Review on Synthesis, Applications and Advancements. Carbohydr Polym. 2020; 250: 116937. doi:10.1016/j.carbpol.2020.116937
11. Belali NG, Chaerunisaa AY, Rusdiana T. Isolation and Characterization of Microcrystalline Cellulose Derived from Plants as Excipient in Tablet : A Review. Indones J Pharm. 2019; 1(2). doi:10.24198/idjp.v1i2.21515
12. Trache D, Hussin MH, Hui Chuin CT, et al. Microcrystalline cellulose: Isolation, characterization and bio-composites application—A review. Int J Biol Macromol. 2016; 93: 789-804. doi:10.1016/j.ijbiomac.2016.09.056
13. Queiroz ALP, Kerins BM, Yadav J, et al. Investigating Microcrystalline Cellulose Crystallinity Using Raman Spectroscopy. Cellulose. 2021; 28(14): 8971-8985. doi:10.1007/s10570-021-04093-1
14. Wool RP. 16 - Lignin Polymers and Composites. In: Wool RP, Sun XS, eds. Bio-Based Polymers and Composites. Academic Press; 2005: 551-598. doi:10.1016/B978-012763952-9/50017-4
15. Permata DA, Kasim A, Asben A, Yusniwati. Delignification of Lignocellulosic Biomass. World J Adv Res Rev. 2021; 12(2): 462-469. doi:10.30574/wjarr.2021.12.2.0618
16. Bhandari K, Roy Maulik S, Bhattacharyya AR. Synthesis and Characterization of Microcrystalline Cellulose from Rice Husk. J Inst Eng India Ser E. 2020; 101(2): 99-108. doi:10.1007/s40034-020-00160-7
17. Yunus MA, Raya I, Tuara ZI. Synthesis Cellulose From Rice Husk. Published online 2019.
18. Zuliahani A, Hanani ASN, Nadhirah RN, Hazirah A. Isolation and Characterization of Microcrystalline Cellulose (MCC) From Rice Husk (RH) and Kenaf : A Comparison Study. Solid State Sci Technol. 2017; 25(2).
19. Hafid HS, Omar FN, Zhu J, Wakisaka M. Enhanced Crystallinity and Thermal Properties of Cellulose From Rice Husk Using Acid Hydrolysis Treatment. Carbohydr Polym. 2021; 260: 117789. doi:10.1016/j.carbpol.2021.117789
20. Ahmad Z, Roziaizan NN, Rahman R, Mohamad AF, Ismail WINW. Isolation and Characterization of Microcrystalline Cellulose (MCC) from Rice Husk (RH). Abd Rahman N, Mohd Jaini Z, Yunus R, Rahmat SN, eds. MATEC Web Conf. 2016; 47: 05013. doi:10.1051/matecconf/20164705013
21. Hanani ASN, Zuliahani A, Nawawi WI, Razif N, Rozyanty AR. The Effect of Various Acids on Properties of Microcrystalline Cellulose (MCC) Extracted from Rice Husk (RH). IOP Conf Ser Mater Sci Eng. 2017; 204: 012025. doi:10.1088/1757-899X/204/1/012025
22. Sim B, Bae DH, Choi HJ, Choi K, Islam MdS, Kao N. Fabrication and Stimuli Response of Rice Husk-Based Microcrystalline Cellulose Particle Suspension Under Electric Fields. Cellulose. 2016; 23(1): 185-197. doi:10.1007/s10570-015-0836-3
23. Uwaezuoke O, Bamiro O, Ngwuluka N, Ajalla O, Okinbaloye A. Comparative Evaluation of the Disintegrant Properties of Rice Husk Cellulose, Corn Starch and Avicel in Metronidazole Tablet Formulation. J Appl Pharm Sci. Published online December 30, 2014. doi:10.7324/JAPS.2014.41219
24. Ce U, Sa C, Ce I. Evaluation of Excipient Potentials of Alpha Cellulose Extracted from Rice Husk in Metronidazole Compressed Tablets: Colon Targeted Drug delivery and In vitro Characterizations. Published online 2019.
25. Ohwoavworhua FO, Mitchell JW, Okhamafe AO. Rice Husk As a Sustainable Source of Microcrystalline cellulose: pharmacopoeial, crystalline and spectroscopic characteristics. Drug Discov. 2019; 13: 79-87.
26. Bajpai P. Green Chemistry and Sustainability in Pulp and Paper Industry. Springer International Publishing; 2015. doi:10.1007/978-3-319-18744-0
27. Tanis MH, Wallberg O, Galbe M, Al-Rudainy B. Lignin Extraction by Using Two-Step Fractionation: A Review. Molecules. 2023; 29(1): 98. doi:10.3390/molecules29010098
28. Park J, Shin H, Yoo S, Zoppe JO, Park S. Delignification of Lignocellulosic Biomass and Its Effect on Subsequent Enzymatic Hydrolysis. BioResources. 2015; 10(2): 2732-2743. doi:10.15376/biores.10.2.2732-2743
29. Tocco D, Garucci C, Monduzzi M, Salis A, Sanjust E. Recent Developments in the Delignification and Exploitation of Grass Lignocellulosic Biomass. ACS Publ. 2021; 9(6): 2412-2432. doi:https://doi.org/10.1021/acssuschemeng.0c07266
30. Susi S, Ainuri M, Wagiman W, Falah MAF. Effect of Delignification and Bleaching Stages on Cellulose Purity of Oil Palm Empty Fruit Bunches. IOP Conf Ser Earth Environ Sci. 2022; 1116(1): 012018. doi:10.1088/1755-1315/1116/1/012018
31. Irawan B, Darmawan A, Roesyadi A, Hari Prajitno D. Improving Reaction Selectivity with NaOH Charges and Reaction Time in The Medium Consistency Oxygen Delignification Process. Int J Technol. 2020; 11(4): 764. doi:10.14716/ijtech.v11i4.3499
32. Supian MAF, Mohamad S, Amin KNM, et al. Effect of Different Bleaching Reagents and Process Sequences on The Properties of Steam-Exploded Empty Fruit Bunch (EFB) Fiber. IOP Conf Ser Mater Sci Eng. 2020; 778(1): 012015. doi:10.1088/1757-899X/778/1/012015
33. Agnihotry A, Gill KS, Singhal D, Fedorowicz Z, Dash S, Pedrazzi V. A Comparison of the Bleaching Effectiveness of Chlorine Dioxide and Hydrogen Peroxide on Dental Composite. Braz Dent J. 2014; 25: 524-527. doi:10.1590/0103-6440201300098
34. Vitasari D. The Effect of Ozone Concentration on The Bleached Pulp Properties. Published online 2008.
35. Kaur D, Bhardwaj NK, Lohchab RK. Effect of Incorporation of Ozone Prior to ECF Bleaching on Pulp, Paper and Effluent Quality. J Environ Manage. 2019; 236: 134-145. doi:10.1016/j.jenvman.2019.01.089
36. Gümüşkaya E, Usta M. Crystalline Structure Properties of Bleached and Unbleached Wheat Straw (Triticum Aestivum L.) Soda-Oxygen Pulp. Turk J Agric For. 2002; 26(5): 247-252.
37. Santos SF, Tonoli GHD, Mejia JEB, Fiorelli J, Jr HS. Non-Conventional Cement-Based Composites Reinforced with Vegetable Fibers: A Review of Strategies to Improve Durability. Mater Constr. 2015; 65(317). doi:10.3989/mc.2015.05514
38. Mangunwardoyo W, Lestari YPI, Suryadi H, Yanuar A, Suryadi H. Characterization of Kapok Pericarpium Microcrystalline Cellulose Produced of Enzymatic Hydrolysis Using Purified Cellulase From Termite (Macrotermes Gilvus). Int J Pharm Pharm Sci. Published online 2020: 7-14.
39. Monschein M, Reisinger C, Nidetzky B. Enzymatic Hydrolysis of Microcrystalline Cellulose and Pretreated Wheat Straw: A Detailed Comparison Using Convenient Kinetic Analysis. Bioresour Technol. 2013; 128: 679-687. doi:10.1016/j.biortech.2012.10.129
40. Raudhatussyarifah R, Sediawan WB, Azis MM, Hartati I. Microcrystalline Cellulose Production by Acid Hydrolysis of Hydrotropic Rice Straw Pulp. IOP Conf Ser Earth Environ Sci. 2022; 963(1): 012055. doi:10.1088/1755-1315/963/1/012055
41. Karim MdZ, Chowdhury ZZ, Abd Hamid SB, Ali MdE. Statistical Optimization for Acid Hydrolysis of Microcrystalline Cellulose and Its Physiochemical Characterization by Using Metal Ion Catalyst. Materials. 2014; 7(10): 6982-6999. doi:10.3390/ma7106982
42. Prayoga WNA, Aziz AA, Syahrir A, Pitaloka AB. Optimization of Microcrystalline Cellulose from Bagasse (Saccharum officinarum) by Acid Hydrolysis. World Chem Eng J. 2023; 7(2): 61-64. doi:10.36055/wcej.v7i2.23125
43. Prosvirnikov D, Safin R, Zakirov SR. Microcrystalline Cellulose Based on Cellulose Containing Raw Material Modified by Steam Explosion Treatment. Solid State Phenom. 2018; 284: 773-778. doi:10.4028/www.scientific.net/SSP.284.773
44. Ren H, Shen J, Pei J, et al. Characteristic Microcrystalline Cellulose Extracted by Combined Acid and Enzyme Hydrolysis of Sweet Sorghum. Cellulose. 2019; 26(15): 8367-8381. doi:10.1007/s10570-019-02712-6
45. PubChem. Hydrochloric Acid. 2024. Accessed May 25, 2024. https://pubchem.ncbi.nlm.nih.gov/compound/313
46. PubChem. Sulfuric Acid. 2024. Accessed May 25, 2024. https://pubchem.ncbi.nlm.nih.gov/compound/1118
47. Wiyantoko B, Rusitasari R, Putri RN. Study of Hydrolysis Process from Pineapple Leaf Fibers using Sulfuric Acid, Nitric Acid, and Bentonite Catalysts. Bull Chem React Eng Catal. 2021; 16(3): 571-580. doi:10.9767/bcrec.16.3.10281.571-580
48. Amin KNM, Hosseinmardi A, Martin DJ, Annamalai PK. A Mixed Acid Methodology to Produce Thermally Stable Cellulose Nanocrystal at High Yield Using Phosphoric Acid. J Bioresour Bioprod. 2022;7(2):99-108. doi:10.1016/j.jobab.2021.12.002
49. Cen Y, Xiang Z, Han T, Long Y, Song T. Effect of Microfluidizing Cycles After Citric Acid Hydrolysis on The Production Yield and Aspect Ratio of Cellulose Nanocrystals. Cellulose. 2022; 29(13): 7193-7209. doi:10.1007/s10570-022-04725-0
50. Hutomo GS, Rahim A, Kadir S. The Effect of Sulfuric and Hydrochloric Acid on Cellulose Degradation from Pod Husk Cacao. Int J Curr Microbiol Appl Sci. 2015; 4(10): 89095.
51. Kassaye S, Pant KK, Jain S. Synergistic Effect of Ionic Liquid and Dilute Sulphuric Acid in the Hydrolysis of Microcrystalline Cellulose. Fuel Process Technol. 2016; 148: 289-294. doi:10.1016/j.fuproc.2015.12.032
52. Ndé HS, Tamfuh PA, Clet G, Vieillard J, Mbognou MT, Woumfo ED. Comparison of HCl and H2SO4 for The Acid Activation of a Cameroonian Smectite Soil Clay: Palm Oil Discolouration and Landfill Leachate Treatment. Heliyon. 2019; 5(12): e02926. doi:10.1016/j.heliyon.2019.e02926
53. Prosvirnikov DB, Safin RG, Zakirov SR. Microcrystalline Cellulose Based on Cellulose Containing Raw Material Modified by Steam Explosion Treatment. Solid State Phenom. 2018; 284: 773-778. doi:10.4028/www.scientific.net/SSP.284.773
54. Nwachukwu N, Ofoefule SI. Effect of Drying Methods on The Powder and Compaction Properties of Microcrystalline Cellulose Derived from Gossypium herbaceum. Braz J Pharm Sci. 2020; 56: e18660. doi:10.1590/s2175-97902020000118060
55. Belali NG, Chaerunisaa AY, Rusdiana T. Isolation and Characterization of Microcrystalline Cellulose Derived from Plants as Excipient in Tablet : A Review. Indones J Pharm. 2019; 1(2). doi:10.24198/idjp.v1i2.21515
56. Sahoo S. Pharmaceutical Engineering. Institute of Pharmaceutical Science; 2020.
57. Anthony JH, Ganderton D. Pharmaceutical Process Engineering. In: Vol 195. 2nd ed. Informa Healtcare; 2010:68-86.
58. Nguyen X. Process for Preparing Microcrystalline Cellulose. Published online April 22, 2004. Accessed July 5, 2024. https://patents.google.com/patent/US20040074615A1/en
59. Debnath B, Duarah P, Purkait MK. Microwave-Assisted Quick Synthesis of Microcrystalline Cellulose from Black Tea Waste (Camellia sinensis) and Characterization. Int J Biol Macromol. 2023; 244: 125354. doi:10.1016/j.ijbiomac.2023.125354
60. Snehal W, Nitiin K. Microwave and Its Role in Pharmaceutical Sector : A Review. Int J Res Dev Pharm Life Sci. 2014; 3(5): 1128-1135.
61. Al-Ali M, Salih KI, Alsamarrae A. Microwave Heating Temperatures and Pharmaceutical Powder Characteristics. Mater Today Proc. 2020; 20: 583-587. doi:10.1016/j.matpr.2019.09.193
62. Mo W, Kong F, Chen K, Li B. Relationship Between Freeze-Drying and Supercritical Drying of Cellulosic Fibers With Different Moisture Contents Based On Pore And Crystallinity Measurements. Wood Sci Technol. 2022; 56(3): 867-882. doi:10.1007/s00226-022-01387-w
63. Peng Y, Gardner DJ, Han Y, Kiziltas A, Cai Z, Tshabalala MA. Influence of drying method on the material properties of nanocellulose I: thermostability and crystallinity. Cellulose. 2013; 20(5): 2379-2392. doi:10.1007/s10570-013-0019-z
64. Mo W, Li B, Chen K. Low-Temperature Thermal Drying-Induced Pore Expansion Effects of Cellulosic Fibers. Cellulose. 2023; 30(6): 3441-3453. doi:10.1007/s10570-023-05103-0
|
Received on 09.09.2024 Revised on 21.01.2025 Accepted on 12.04.2025 Published on 02.08.2025 Available online from August 08, 2025 Research J. Pharmacy and Technology. 2025;18(8):3979-3986. DOI: 10.52711/0974-360X.2025.00572 © RJPT All right reserved
|
|
|
This work is licensed under a Creative Commons Attribution-NonCommercial-ShareAlike 4.0 International License. Creative Commons License. |
|