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The process of aroma adsorption still could not be visualized which greatly limits our understanding of the adsorption mechanism. Based on the fluorescence principle, the aroma compounds treated with fluorescence treatment revealed that the fluorescent materials competitively combine with the functional groups on the surface of the internal pore structure of the tea, which hinders the absorption of aroma compounds. The bonding process with functional groups on the surface of the internal pore structure cannot be further explored with the principle of functional group bonding. This experimental verification method is complicated to operate and difficult to implement. After long-term scientific research practice, researchers have summed up a variety of mathematical models to describe a certain process and realize its scientific analysis. To describe the process of tea adsorption aroma, the means of adsorption isotherm model and kinetic model analysis are fitted and analyzed, which can also help researchers to further understand the adsorption process. Numerous adsorption isotherm equations have been widely used to explain the occurrence of adsorption equilibrium, while all these equations have advantages and limitations[38].
The adsorption isotherm model can be used to investigate the adsorption mechanism, predict the maximum adsorption capacity of the adsorbent, estimate the affinity between the adsorbent and the adsorbate, and optimize the design of the adsorption system[13], as well as explore the influence of different time, temperatures, humidities, and other conditions on the adsorption of aroma by tea leaves. In a specific environment, the fragrance source of the flower releases aroma compounds, and at the same time, the tea leaves absorb and volatilize the aroma compounds. After reaching equilibrium, the change of aroma compounds in tea leaves was detected by SPME-GC-MS. Then, the adsorption isotherm model was fitted to obtain the change law of aroma compounds and describe the process of tea aroma adsorption. The differences in the making processes of major tea, directly lead to differences in the composition and content of aroma compounds among various types of tea leaves. Obvious differences are found in the process of absorption in tea. These differences can be judged by fitting the adsorption isotherm model. In the process of scenting, the release of aroma compounds changes with the variation of temperature, humidity, equilibrium vapor pressure, etc. The releasing process belongs to non-uniform release[39], and the Toth equation is suitable for systems with such inhomogeneous properties. The Toth equation is as the following Eqn (1):
$ q=\dfrac{{q}_{s}bp}{{[1+{\left(bp\right)}^{t}]}^{1/t}} $ (1) where, q is the adsorption capacity, qs is the saturated adsorption capacity, b is the adsorption affinity constant, and t is the heterogeneity parameter explaining the relationship between the adsorbent and the adsorbate. Additionally, there are still many models used to fit the adsorption equilibrium process, which will not be discussed in detail here, and the list is as Table 1.
Table 1. Adsorption equilibrium process equations.
Adsorption models Equation The main parameters Field of application Ref. Freundlich model $ s={K}_{F}{C}^{N} $ s is the adsorption concentration (μg/g), C is the liquid phase equilibrium solution concentration (μg/mL), KF is the adsorption capacity coefficient [(μg/g)/(μg/mL)],
N (dimensionless) is the description Freundlich exponent of isothermal nonlinearity.Monolayer adsorption and
non-uniform surface adsorption[40] Langmuir model $ \dfrac{{c}_{e}}{Q\mathrm{e}}=\dfrac{{c}_{e}}{{Q}_{max}}+\dfrac{1}{{Q}_{max}{K}_{L}} $ Where Ce is the equilibrium concentration, Qe is the adsorption amount of the dye at equilibrium, Qmax is the maximum adsorption amount of the dye, and
KL is the Langmuir constant.Uniform surface adsorption [14] Freundlich model $ \mathit{ln}{Q}_{e}=\mathrm{ln}{K}_{F}+\dfrac{1}{n}\mathrm{ln}{C}_{e} $ Among them, KF is the Freundlich constant, and
n is the heterogeneity factor.Monolayer adsorption and
non-uniform surface adsorption[41] Dubinin–Radushkevich model $ {l}_{n}{Q}_{e}=\mathrm{ln}{Q}_{m}-K{\varepsilon }^{2} $ In the formula, K is the coefficient related to the free energy of adsorption (mol/kJ2), Qm is the maximum
adsorption capacity (mg/g), ε is the Polanyi adsorption potential.Adsorption behavior of exogenous substances on surfaces [42] Temkin model $ {Q}_{\mathrm{e}}=\dfrac{RT}{{B}_{T}}\mathrm{ln}\left({A}_{T}{C}_{e}\right) $ In the formula, BT is the Temmin constant (J/mol),
AT is the Temkin isotherm equilibrium binding
constant (L/mg).Non-uniform surface adsorption [43] -
The adsorption capacity of the tea residue could be applied with multiple uses, moreover, the modified tea residue has better stable adsorption performance.
As shown in Table 2 and Fig. 3, tea leaves can be prepared as an adsorbent through saponification, high-temperature carbonization, acidolysis, alkali treatment, powderization, etc., for the adsorption of heavy metals and environmental pollutants. Hence, the modified tea leaves play a huge role in purifying wastewater and air. Despite a variety of treatment methods applied to the modification of tea leaves, most of the current methods are based on destroying the original structure of tea leaves. In a recent research on the antibacterial properties of metal-phenolic network nanoparticles, the author used multi-component to mix with metal ions in alkaline water at room temperature and the assembly of nanoparticles was completed within a few seconds[44]. TEM images show regular particle morphology and high stability after long-term storage. The research indicates that polyphenols in tea can stably bind to exogenous substances under the condition of applying weak external force. The X-ray photoelectron spectroscopy results showed that metal ions and polyphenols combined through benzene-O, C-S contact mode. In the future, this stable binding effect between exogenous substances with functional groups like N-C, -OOC-, -C-O-C-, -OC-, HO- and so on, also provides a wider way for the application of adsorption Additionally, adsorbents can be developed for different adsorbates based on this theory.
Table 2. Applications of tea as adsorbent.
Applications Modified tea adsorbent Adsorbate structure Ref. Adsorption of hydrophobic organic compounds by Tea Tea powder Phenanthrene [40] Cd and cadmium by waste tea biochar Continuous high temperature pyrolysis of tea leaves to remove ash and make biochar CdCl2
[33,45] Tea waste removal of heavy
metals in wastewaterPickling, alkali washing, vulcanization, etc. treat overnight wasteto deprotonate the surface of tea waste and activate the adsorption sites Pb, Cu, Zn, Cr, Ni [16] Tea-aluminum biosorbent Preparation of tea-aluminum biosorbent by chemical coprecipitation [15] Removal of methylene blue from aqueous solution by tea residue Deionized water is used to remove ash from the tea waste, and the pigment, the ophylline and caffeine in the tea waste are removed by boiling water, and finally dried.
Methylene Blue[13,14] Adsorption of organic pollutants and polycyclic aromatic hydrocarbons (PAH)
by modified tea leavesTea industry waste is treated by Sohit extraction, saponification and acid hydrolysis PAH [34] Selective adsorption of radioactive cesium by crosslinked tea leaves Fresh tea leaves and discarded tea leaves are stirred in concentrated sulfuric acid at high temperature, and then washed with deionized water until it's neutral CsCl, CsOH [46] Removal of ciprofloxacin from aqueous solution by waste tea biochar Tea biochar was obtained from high temperature pyrolysis of tea by argon gas Ciprofloxacin [32] -
Data availability is not applicable to this article as no new data were created or analyzed in this study.
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Cite this article
Xu L, Ma C, Chen X, Du Q, Song C, et al. 2024. Theories and applications of tea residue adsorbing aroma compounds: a review. Beverage Plant Research 4: e030 doi: 10.48130/bpr-0024-0030
Theories and applications of tea residue adsorbing aroma compounds: a review
- Received: 08 May 2024
- Revised: 01 July 2024
- Accepted: 22 July 2024
- Published online: 14 August 2024
Abstract: Tea leaves have a good natural adsorption capacity due to their numerous pore structures and high specific surface area. Along with the advancement of tea process technology, more and more sites of adsorption and binding have been found in tea leaves, thus further improving the adsorption performance. Based on the original biological structure and internal components of tea leaves, the adsorption mechanism in tea leaves for exogenous compounds is mainly divided into physical adsorption theory and chemical adsorption theory. Compared with original tea leaves, modified tea leaves significantly improve adsorption performance with a specific adsorption function, which could improve the utilization rate of tea leaves and their waste residues. Techniques such as scanning electron microscopy provide basic data support for exploring the adsorption mechanism of tea leaves at the level of material structure and a theoretical basis for the development of specific adsorbents. Additionally, the application of thermodynamic adsorption models and adsorption kinetic equations could help to understand the process of tea adsorbing exogenous compounds and to visualize the adsorption process. The adsorption of exogenous additives by tea residue could make use of the affinity between functional groups. In future, these mechanisms will lay the foundation for its application in the field of substance adsorption and improve the utilization efficiency of renewable resources similar to tea leaves.