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Introduction
Chitin is among the most universal natural occurring polysaccharides, second only to cellulose (El Knidri et al., 2018). It is a biopolymer produced by a large number of terrestrial and aquatic flora and fauna. Its crystalline nature is depicted in the exoskeletal systems of various known insects (Kamal et al., 2020).
Commercially, aquatic life has been the main source of chitin; commonly in the forms of crabs, clams and shrimps (Bernardi et al., 2018). Chitin possesses a structural identity close to that of cellulose, but with a different positioning of the acetamide groups. The main polymer derivative of Chitin is Chitosan, which is a linear polymer (Crini, 2019).
The trend of cellulose being depicted as the landmine of biopolymer resources has been seen to fade, as Chitin is currently championed globally as the “biopolymer of the future”; with an annual global production rate competing with that of cellulose (Rao et al., 2014). It has received the nod globally as the novel biomaterial with near limitless functionality and potentials in various realms of science and technology. This depicts the enormous global significance of Chitin (Islam et al., 2017).
Chitin is an excellent biopolymer due to its superb qualities with respect to its renewability, bio-degradability, adsorption properties, sustainability, reasonable inertness, non-toxicity, and bio-compatibility (Shamshina et al., 2019). It has been demonstrated that Chitin possesses a higher versatility than cellulose due to its polymeric chain arrangements, and the presence of its intrinsic amine groups (Khattak et al., 2019).
Industrially, Chitin undergoes dissolution in the presence of both acid and alkaline solutions respectively in order to dissolve its carbonate and protein groups (Song et al., 2018). Furthermore for aesthetics, a decolourization step is usually undergone (Shamshina, 2019). A major issue in the industrial processing of Chitin is its insolubility as it is seriously hydrophobic and also insoluble in organic solvents (Doan et al., 2019).
Chitin is similar to Cellulose in that complex living organisms find it difficult to digest, ironically it is easily biodegradable which makes it a great material for numerous industrial applications (Yates and Barlow, 2013).
Most aquatic scales contain about chitin within the range of 20-30%, with the remaining composition being protein groups and calcium carbonate (Kaya et al., 2017). The scales also contain lipidic pigments (Moussian, 2019). Chitin undergoes acid treatment to enable dissolution of the Calcium Carbonate, and also alkaline extraction in order to dissolve the protein groups (Antunes-Valcareggi et al., 2017). A depigmentation process is also not neglected in order to attain a product without colour (Lopes et al., 2018).
The extraction of the proteins from Chitin is usually done heterogeneously; this breaks down the chitin biopolymer into lighter chains. This process is usually a difficult one; as it disintegrates the bonds between Chitin and the shells’ intrinsic protein groups (Gadgey and Bahekar, 2017). However, this process is very significant because a total removal of the protein groups is essentially important; the protein-less Chitin finds numerous applications in biomedicine (Hamdi et al., 2017).
Various alkali reagents have been used to carry out the de-proteinization (Mechri et al., 2019). Sodium hydroxide stands out among the alkali reagents, as it can be used at very suitable process conditions; the reaction temperature, reaction time and reagent concentration (Soon et al., 2018).
The acid treatment of the crustacean shells takes place as a form of demineralization (Zhou et al., 2019). Sulphuric acid, nitric acid and hydrochloric acid are among the preferred reagents for acid treatment (Oyekunle and Omoleye, 2019). Dilute hydrochloric acid is mostly used as it has the shortest demineralization reaction time, as seen from literature (Alabaraoye, 2018).
The reagent concentrations are the most important process variables in both the deproteinization and demineralization reaction for obtaining Chitin from aquatic scales, among other process variables (Rasti et al., 2017). Different literature reviews have shown that a reagent concentration above the optimum reagent concentration would bleach the Chitin to be gotten from the feed aquatic scales and also damage the Chitin entirely; thereby not achieving the process aim and also wasting process reagents (Tokatl? and Demirdöven, 2018). A reagent concentration below the optimum point would also not give the optimum yield of Chitin from the aquatic scales. Therefore this is a very important issue in achieving the maximum yield of Chitin from the aquatic scales, this process variable would have to be fine-tuned (Al shaqsi et al., 2020).
Problem Statement
Chitin has been shown to have significant use in the novel areas of science and technology, notably in the area of biomedicine. Hence, its significant production is an essential global need. This need is why the optimal conditions for the production of Chitin industrially have to be taken quite seriously (Duan et al., 2018).
Reagent concentration for the extraction of chitin from fish scales, above the optimum value has been depicted to damage and bleach the required final product (Chitin), while reagent concentration below the optimum value do not give an optimal production of Chitin (Hassainia et al., 2018).
Therefore, the concentration of hydrochloric acid and sodium hydroxide that would give a maximum yield of Chitin from aquatic scales have to be figured out.
Aim and objectives
The aim of this study is to determine the optimum concentrations of both hydrochloric acid and sodium hydroxide that would give a maximum yield of Chitin from fish scales, with the following objectives;
Research Questions
The identified research questions for this project are provided below:
Deliverables
The deliverables of these projects are a project report and attained results. Also, the report should contain a complete documentation of how the laboratory experiment was carried out, how various reagent concentrations affected the Chitin yield, how various process variables were gotten, and how the results were arrived at.
Relevance
This study is majorly focused on obtaining the best concentration of HCl/NaOH needed to get maximum yield of chitin from fish scales at an optimum condition.
Methodology
This project focuses on secondary research, laboratory experiments and process analysis, and they are discussed below:
Secondary research
The secondary research in this project will utilize a systematic approach (Johnson et al., 2016) to review the works of literature. The steps involved in the systematic review of the literature are provided below:
Laboratory experiments
The laboratory experiments would cover a large chunk of this project. They would be carried out in stages, and as such described below;
Process Analysis
The totality of the process reaction would be analyzed and this would also occur in stages;
Evaluation
The risk assessment conducted for this project is provided in the table below:
Table 1: Risk assessment
Risk
Impact
Mitigation Plan
Inability to meet the deadline
Low
Get an extension from the supervisor in due time
Inability to get required process inputs
High
Refer to municipalities, research institutes and laboratory technicians for help
Inability to develop the process set up
Refer to laboratory technicians for help
Insufficient data
Refer to journals and textbooks for help
Schedule
Table 2: Project Plan
Task Name
Start Date
End Date
Duration (Days)
Initial Research
23/09/2021
07/10/2021
14
Proposal
28/10/2021
21
Secondary Research
07/12/2021
40
Introduction Chapter
12/12/2021
5
Literature Review Chapter
05/01/2022
24
Methodology Chapter
17/01/2022
12
Sourcing of Required Feedstock
15/03/2022
60
Presentation 1
23/03/2022
8
Laboratory Experiments
06/04/2022
Evaluation of Gotten Results
13/04/2022
7
Discussion Chapter
23/04/2022
10
Evaluation Chapter
28/04/2022
Conclusion Chapter
30/04/2022
2
Project Management Chapter
01/05/2022
Abstract and Report compilation
03/05/2022
Report Proofreading
13/05/2022
Presentation 2
23/05/2022
References
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Al Shaqsi, N.H.K., Al Hoqani, H.A.S., Hossain, M.A. and Al Sibani, M.A., 2020. Optimization of the demineralization process for the extraction of chitin from Omani Portunidae segnis. Biochemistry and Biophysics Reports, 23, p.100779.
Antunes-Valcareggi, S.A., Ferreira, S.R. and Hense, H., 2017. Enzymatic hydrolysis of blue crab (Callinectes Sapidus) waste processing to obtain chitin, protein, and astaxanthin-enriched extract. International Journal of Environmental and Agriculture Research, 3(1), pp.81-92.
Bernardi, F., Zadinelo, I.V., Alves, H.J., Meurer, F. and dos Santos, L.D., 2018. Chitins and chitosans for the removal of total ammonia of aquaculture effluents. Aquaculture, 483, pp.203-212.
Crini, G., 2019. Historical review on chitin and chitosan biopolymers. Environmental Chemistry Letters, 17(4), pp.1623-1643.
Doan, C.T., Tran, T.N., Vo, T.P.K., Nguyen, A.D. and Wang, S.L., 2019. Chitin extraction from shrimp waste by liquid fermentation using an alkaline protease-producing strain, Brevibacillus parabrevis. International journal of biological macromolecules, 131, pp.706-715.
Duan, B., Huang, Y., Lu, A. and Zhang, L., 2018. Recent advances in chitin based materials constructed via physical methods. Progress in Polymer Science, 82, pp.1-33.
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Hamdi, M., Hammami, A., Hajji, S., Jridi, M., Nasri, M. and Nasri, R., 2017. Chitin extraction from blue crab (Portunus segnis) and shrimp (Penaeus kerathurus) shells using digestive alkaline proteases from P. segnis viscera. International journal of biological macromolecules, 101, pp.455-463.
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Last updated: Dec 01, 2021 05:14 PM
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