Over the past 20 years, global plastic production has increased by around 260 million tons, ultimately reaching 359 million tons annually (PlasticsEurope 2021). Disposal of these materials is an increasing environmental challenge. During plastic waste decomposition, many toxic compounds migrate into the soil and groundwater, contaminating them and eventually killing the ecosystems that live there (Vethaak and Leslie 2016; Haider et al 2019). When plastics are used for food packaging, the harmful compounds can be released into food, and hence, into consumer organisms, where they can bioaccumulate (Vethaak and Leslie 2016). Despite the negative aspects of using plastic, there are also many advantages of these materials, such as the resistance to mechanical damage, the low water vapor permeability, and the easy and cheap production. It is difficult to obtain a competitive biodegradable material with such good performance characteristics as synthetic materials.
The raw materials for the production of biodegradable materials can be proteins and polysaccharides, including protein- and polysaccharide-rich biomass resources (Schrooyen et al. 2000). For example, feathers from the poultry industry which account for ca. 10% of the total weight of a mature chicken, are 90% keratin (Cameron et al. 2003; Singh et al. 2017; Ciechanska et al. 2014). According to the periodic report published by the United States Department of Agriculture, in the April 2021, over 100 million chickens were slaughtered annually, resulting in about 100 million tons of problematic feather waste (USDA, 2021). Thus, the use of waste biomass for the production of biodegradable materials is beneficial from both an economic and an environmental point of view (Singh et al. 2017; Ciechanska et al. 2014).
Keratin is a natural polymer with a structure and properties strikingly similar to synthetic polymers (Hill et al. 2010). Due to a high number of hydrophobic amino acids and a highly cross-linked structure, keratin-based materials can not only be biodegradable but can also exhibit low water vapor permeability, low water absorption and high resistance to mechanical damage, which has been difficult to achieve so far in the production of materials from raw materials of natural origin (Schrooyen 2000; Dou et al. 2016; Reddy et al 2013). Such keratin materials can contribute to the elimination of disadvantages of currently produced biodegradable protein-based materials (Schrooyen et al. 2000; Dou et al. 2016; Reddy et al 2013), and, due to their similarity to some synthetic polymeric materials, to lower the use of the latter and, consequently, to reduce the amount of problematic non-biodegradable waste.
Keratin belongs to a heterogenous group of hydrophilic proteins insoluble in neither polar nor non-polar solvents, which are made in vertebral epithelial cells, forming animal fibers. Keratin products are durable and resistant to both physicochemical, biological, and mechanical external factors. These unique properties are related to the high content of cysteine, a sulfur amino acid, which allows the formation of intra- and intermolecular disulfide bridges between amino acids located in two different peptide chains, giving the keratin materials a hard and cross-linked structure (Cameron et al. 2003; Singh et al. 2017; Wang et al. 2016). Feather keratin, with a molecular weight of ca. 10 kDa, consisting of 70–75% α-helix and 25–30% β-sheet structure, is classified as β-keratins characterized by a higher sulfur content than keratin from other sources due to a large proportion of cysteine residues in their primary sequences (Cameron et al. 2003; Singh et al. 2017; Ciechanska et al. 2014; Schrooyen et al. 2001]. This increases the frequency of cross-linking keratin via disulfide linkages, thereby enhancing the hardness, toughness, and strength of the feather structure (Cameron et al. 2003; Singh et al. 2017; Wang et al. 2016).
Due to a high content of hydrophobic amino acids, a large number of intermolecular disulfide bridges, and a densely packed structure, keratin raw materials are insoluble in traditional protein solvents. However, the key aspect of keratin isolation is to bring it into the dissolved form (Singh et al. 2017; Schrooyen et al. 2001). Redox reactions, and hydrolysis with both acid and alkaline reagents belong to the main chemical methods of keratin dissolution. The reduction method with the use of 2 mercaptoethanol and urea allows for a high degree of keratin isolation from the raw materials, while limiting hydrolysis degree of peptide bonds. However, reducing reagents are highly toxic to the environment and human health, and they are too expensive to be used on a technical scale (Schrooyen et al. 2001; Nakamura et al. 2002). The properties of keratin hydrolysates depend on the pH, temperature and reaction time (Coward-Kelly et al. 2006a, b). The use of acid hydrolysis allows to a high protein extraction yield, but can result in the strong hydrolysis of peptide bond which lead to high protein fragmentation and loss of some amino acids such as tryptophan, methionine, and histidine (Liu et al. 1989). Although disulfide bridges and peptide bonds are also broken during alkaline hydrolysis, it can result in a mixture of all amino acids present in the native protein (Singh et al. 2017; Coward-Kelly et al. 2006a, b; Gousterova et al. 2005; Nagai and Nishikawa 1970; Song et al. 2013; Tsuda and Nomura 2014). An increased reaction temperature and a high concentration of alkali used lead to an increased protein yield but cause its strong fragmentation, bringing about low-molecular-weight protein fractions. Unfortunately, such proteins do not show film-forming properties, unlike e.g. collagen and gelatin characterized by a high molecular weight, ca. 150–300 kDa (Abraham et al. 2008; Gómez-Guillén et al. 2009). Therefore, it is important to select conditions of alkaline hydrolysis that will yield the high-molecular-weight protein fractions, capable of film formation (Singh et al. 2017).
The aim of the study was to assess the statistically significant effect of input variables in the alkaline hydrolysis of keratin from white chicken feathers, carried out at room temperature using sodium hydroxide, on the process yield, molecular weight of the peptides obtained. The effects of the volume ratio of 1M NaOH to the feather mass, the hydrolysis time and the shaking speed of the reaction mixture were statistically analyzed. The pre-treatment process of feathers and the purification process of hydrolysates obtained were carried out according to typical methods reported by other authors (Schrooyen 2000; Singh et al. 2017; Nakamura et al. 2002; Sinkiewicz et al. 2017); however, with some modifications. Namely, the processes of degreasing feathers with organic solvents, a grinding feathers, as well as dialysis and freeze-drying of hydrolysates obtained were omitted. Skipping these processes allowed to eliminate the use of environmentally harmful reagents, to shorten the processing time, and to reduce energy consumption. All these steps together have contributed to making the process more environmentally friendly.
To the best our knowledge, no research has been conducted so far on a statistical analysis of the process conditions of alkaline hydrolysis of keratin from white chicken feathers. In our opinion, this allow for a precise optimization of the method in the context of obtaining protein fractions useful for the formation of biodegradable films.