Abstract
The search for novel renewable products over synthetics hallmarked this decade and those of the recent past. Most economies that are prospecting on biodiversity for improved bio-economy favor renewable resources over synthetics for the potential opportunity they hold. However, this field is still nascent as the bulk of the available resources are non-renewable based. Microbial metabolites, emphasis on secondary metabolites, are viable alternatives; nonetheless, vast microbial resources remain under-exploited; thus, the need for a continuum in the search for new products or bio-modifying existing products for novel functions through an efficient approach. Environmental distress syndrome has been identified as a factor that influences the emergence of genetic diversity in prokaryotes. Still, the process of how the change comes about is poorly understood. The emergence of new traits may present a high prospect for the industrially viable organism. Microbial enzymes have prominence in the bio-economic space, and proteases account for about sixty percent of all enzyme market. Microbial keratinases are versatile proteases which are continuously gaining momentum in biotechnology owing to their effective bio-conversion of recalcitrant keratin-rich wastes and sustainable implementation of cleaner production. Keratinase-assisted biodegradation of keratinous materials has revitalized the prospects for the utilization of cost-effective agro-industrial wastes, as readily available substrates, for the production of high-value products including amino acids and bioactive peptides. This review presented an overview of keratin structural complexity, the potential mechanism of keratin biodegradation, and the environmental impact of keratinous wastes. Equally, it discussed microbial keratinase; vis-à-vis sources, production, and functional properties with considerable emphasis on the ecological implication of microbial producers and catalytic tendency improvement strategies. Keratinase applications and prospective high-end use, including animal hide processing, detergent formulation, cosmetics, livestock feed, and organic fertilizer production, were also articulated.
Introduction
Keratin, a fibrous and structural polypeptide, is highly recalcitrant to degradation by common proteolytic processes due to its molecular architecture. Putting nature’s biomass abundance into perspective, keratin has been ranked the third most abundant and is only surpassed by chitin and cellulose (Hossain et al., 2007). The orientation and interactions inherent in the bonds found in keratin have been reported to be the leading cause of its recalcitrance to degradation (; ). Keratin is an intrinsic part of the epidermis and appendages, including hair, feathers, nails, horns, hooves, scales, and wool. Mechanical support and functional protection are some of the physiological functions provided by keratin (; Jaouadi et al., 2013). Tight packing of individual α-helix or β-sheet motifs of the polymer chains into a supercoiled strand confers mechanical stability to the resultant structure (Onifade et al., 1998). Also, keratin is categorized as hard or soft in relation to the sulfur group content, site of occurrence, and functional involvement of the polypeptide (Li, 2019). The keratin in nails, feathers, horns, and hooves are said to be hard due to their involvement in structural and protective roles against predation and abiotic factors, hence the toughness (Wang B. et al., 2016). However, soft keratins in the skin and callus have fewer disulfide bonds that allow the pliability of their structures (Schrooyen et al., 2001).
Agro-industrial based keratinous wastes constitute an ecosystem nuisance, and top on the list are feathers and hair arising from poultry and leather processing industries that strive to meet the demand of the burgeoning human population (Kang et al., 2018; Kalaikumari et al., 2019). Degradation of these wastes by classic proteases such as papain, pepsin, and trypsin is considerably tough (Thankaswamy et al., 2018). The molecular conformations of the crude protein contents of the keratinous materials, such as intense disulfide bond cross-linkages, hydrogen bonds and hydrophobic interactions improve the structural stability and prevent the proteolytic hydrolysis (Sangali and Brandelli, 2000). Consequently, the wastes continue to constitute environmental problems, which may pose public health problems (). In the past, keratinous wastes and other animal carcasses were harmoniously baked, pulverized, and subsequently utilized as a nutritional supplement of domestic animal feeds (Sapkota et al., 2007). However, the danger posed by prion disease impeded the use of poultry and animal waste recycling in animal husbandry (Tsiroulnikov et al., 2004).
Microbial proteolytic enzymes capable of effectively degrading keratin are referred to as keratinases (3.4.21/24/99) and are considered highly valuable in many biotechnological processes due to their robustness in management of recalcitrant substrates and appreciable stability under extreme conditions ().
Conventionally processed protein-rich feeds of keratin origin are not typically metabolized by animals due to the absence of the redox system that hydrolyses the disulfide bonds of the polypeptides (Wang et al., 2006; Lange et al., 2016). Hence, the nutritive value of keratin-based feed-products needs to be improved by enhancing protein digestibility and nutrient availability (Nnolim et al., 2020a). Keratinase-mediated keratin solubilization offers a solution toward improving the nutritional qualities of the keratin-based feed-products in the fermentative process, which may be submerged or solid state (Łaba and Szczekała, 2013). Microbial keratinase-assisted solubilization of keratin is important in the bio-economy innovation value chain. It enables a sustainable waste management, while promoting the valorization of intractable waste bio-resources into value-added products for the green economy (). However, the mechanisms of action leading to the complete breakdown of keratinous substrates by keratinolytic proteases are not yet fully elucidated. It is conceived that keratinous materials are enzymatically dismembered through the reduction of the disulfide bridges and cleavage of peptide bonds (Stiborova et al., 2016). This review highlights the keratinase sources and functional properties, ecological implication of keratinase producers, environmental impact of keratinous wastes, keratinase applications, and protein structure modification to enhance the catalytic efficiency of keratinase.
Microbial Keratinase and Functional Properties
Keratinolytic proteases have been reported to be associated with an array of microbes isolated from a diverse milieu of the ecosystem. Essentially, bacteria and fungi have been identified as good decomposers of keratinous substrates, which they accomplish by extracellular production of keratinolytic enzymes.
Bacterial Sources
Keratinase production potential has been reported within the bacterial genus of Bacillus, Vibrio, Chryseobacterium, Brevibacillus, Pseudomonas, Serratia, Fervidobacterium, Microbacterium, Aeromonas, Burkholderia, Stenotrophomonas, Rhodococcus, Geobacillus Amycolatopsis, Meiothermus, and Paenibacillus (Williams et al., 1990; ; Sangali and Brandelli, 2000; Yamamura et al., 2002; Riffel and Brandelli, 2006; ; Kuo et al., 2012; ; Jaouadi et al., 2013; Paul et al., 2014b; Stiborova et al., 2016; ; ; ; Nnolim et al., 2020a,b). Keratinase production by Actinobacteria, particularly Streptomyces, Arthrobacter, Bevibacterium, and Nocardiopsis, have been reported (Mitsuiki et al., 2006; Jaouadi et al., 2010; Pereira et al., 2014; ; ; Thankaswamy et al., 2018).
Fungal Sources
Keratinolytic fungi have been reported as the natural colonizers of keratinous substrates and play a major role in the natural hydrolysis of keratinized tissues (). Aspergillus, Paecilomyces, Doratomyces, Trichoderma, Fusarium, Acremonium, Onygena, Cladosporium, Microsporum, Lichtheimia, Chrysosporium, Aphanoascus, Trichophyton, and Scopulariopsis are among the reported keratinolytic fungi (, ; Sharma et al., 2011; Paul et al., 2014a; Sousa et al., 2015; ; ; ). Among the fungal strains, keratinolytic activity has been extensively reported within the confines of the dermatophytes. Keratinolytic property of this group could represent the pathogenic tendencies and has been implicated in mycosis of human and animal skin (Korniłłowicz-Kowalska and Bohacz, 2011).
Even though keratinase potential has been reported for different microbial species autochthonous to variable ecological niches, the large-scale production has been a challenge from the commercial perspective (). Inherent cell precursors, culture conditions, and nutrient availability are among the significant factors that influence microbial metabolites production (Parra et al., 2005). The genetic diversity of keratinolytic microorganisms affects the arbitrary selection of the physico-chemical fermentation conditions (). Additionally, the prolonged fermentation period for the keratinase production by most wild microbial producers affects keratinase yield and sustainability (). Hence, this demands developing industrially viable strains to enhance productivity beyond the bench scale. The nature of nutrient in the cultivation medium plays important roles in the expression of genes coding for the metabolites of interest. Generally, keratinases are secreted extracellularly by the microbial producer in the presence of keratinous substrate; however, cell-bound (Riessen and Antranikian, 2001; Nam et al., 2002) and internally produced keratinases (Onifade et al., 1998) have also been reported. The expression of keratinase encoding genes and activation of redox systems are thought to be induced by the presence of keratinous substrates, which are bioconverted to essential nutritional factors for maintaining microbial homeostasis (Thankaswamy et al., 2018). Alkalinization of the fermentation medium is a crucial factor in keratinous biomass degradation; it is thought that alkalinization softens the keratinous substrate, thus improving the process of sulfitolysis and proteolysis (Kunert, 2000; Ramnani et al., 2005).
Biochemical Properties of Keratinase
Understanding the biochemical properties of microbial proteases is vital for the potential application of the enzymes in the bio-industry. The properties of keratinolytic proteases are dependent on the producing organism (Selvam and Vishnupriya, 2012). Here, we discuss some of these properties, including pH and temperature optima, molecular weight, substrate specificity as well as the effects of reducing agents, inhibitors, surfactants, metal ions, and chemical solvents on the catalytic properties of keratinases. Some general properties of selected keratinolytic proteases are presented in Table 1. Majority of keratinolytic proteases are catalytically active within neutral to alkaline pH with optima values between pH 7.0 and 9.0 (; ; Kuo et al., 2012; Jaouadi et al., 2013; ; ). However, a few extremely alkalophilic keratinases with optimum pH between 10 and 13 were previously reported (; Letourneau et al., 1998; Mitsuiki et al., 2006; Jaouadi et al., 2008, 2010; Tatineni et al., 2008; ; Paul et al., 2014b; ; Tian et al., 2019). The optimum temperature reported for the activity of several microbial keratinases was between 37 and 65°C (Hossain et al., 2007; ; Jaouadi et al., 2013; Wu et al., 2017; Hassan et al., 2020b), whereas thermophilic keratinolytic proteases already characterized function optimally between 70 and 100°C (Nam et al., 2002; Jaouadi et al., 2010; Kuo et al., 2012; ; Paul et al., 2014b; ). Many keratinases, irrespective of the sources, have been found to be catalytically active and stable over a temperature and pH range of 20 to 100°C, and 4 to 13, respectively (Jaouadi et al., 2008, 2010; Paul et al., 2014b; ; Jin et al., 2019).
TABLE 1
| Microbial source | Protease type | Activity substrate | Optimum temp. (°C) | Optimum pH | #Stabilizer/Promoter | *MW (kDa) | Application | References |
| Bacterial source | ||||||||
| Actinomadura keratinilytica Cpt29 | Serine | Keratin azure | 70 | 10 | Mn2+ | 29.23 | Feather degradation | Habbeche et al., 2014 |
| Bacillus circulans DZ100 | Serine | Keratin azure | 85 | 12.5 | Ca2+, Mn2+, and Mg2+ | 32.02 | Keratin degradation, Detergent formulation | |
| Bacillus tequilensis hsTKB2 | Serine | Keratin azure | 70 | 10.5 | Toluene, Mn2+ | 59.89 | Detergent formulation | Paul et al., 2014c |
| Bacillus pseudofirmus FA30-01 | Serine | Azokeratin | 60 | 8.8–10.3 | Mg2+, Co2+, and Zn2+ | 29.29 | Feather degradation | Kojima et al., 2006 |
| Bacillus licheniformis | Serine | Keratin azure | 60 | 8.5 | Mn2+, Al3+, and Ca2+ | 35 | Keratin hydrolysis | Suntornsuk et al., 2005 |
| Bacillus licheniformis ER-15 | Serine | Feather | 70 | 11 | β-ME | 58 | Feather degradation, Hide dehairing | Tiwary and Gupta, 2010 |
| Bacillus subtilis PF1 | − | Casein | 60 | 9 | Ca2+, Trition X-100, DMSO | − | Detergent formulation | |
| Bacillus sp. CL18 | Serine | Azocasein | 55 | 8 | Ca2+, Mg2+, Trition X-100, DMSO | − | Keratin hydrolysis | Rieger et al., 2017 |
| Bacillus sp. AD-W | Serine | Keratin azure | 50 | 10 | Mn2+, DTT | 39 | Keratin hydrolysis | |
| Bacillus sp. AD-AA3 | Serine | Keratin azure | 50 | 8 | DTT, β-ME | 29 | Keratin hydrolysis | |
| Bacillus subtilis FTC02PR1 | Serine | Azokeratin | 60 | 6–11 | SDS, Mn2+ | 30 | Feather degradation | |
| Bacillus licheniformis ALW1 | − | Keratin | 65 | 8 | − | − | Feather degradation | |
| Bacillus haynesii ALW2 | − | Keratin | 70 | 8–9 | − | − | Hide dehairing | |
| Bacillus amyloliquefaciens S13 | Serine | Keratin azure | 50 | 6.5 | Ca2+, Mg2+, and Zn2+ | 28 | Feather degradation, Hide unhairing | Hamiche et al., 2019 |
| Bacillus amyloliquefaciens S13 | Serine | Keratin azure | 60 | 8 | Ca2+, Mg2+, and Mn2+ | 47 | Feather degradation, Hide unhairing | Hamiche et al., 2019 |
| Bacillus thuringiensis MT1 | Metallo | Keratin | 50 | 9 | Ba2+, Ca2+, Mg2+, and Mn2+ | 80 | Hair degradation | Hassan et al., 2020b |
| Bacillus subtilis SCK6 | Serine | Keratin | 60 | 10 | Cu2+, Co2+ | 30.95 | Skin dehairing | Tian et al., 2019 |
| Brevibacillus brevis US575 | Serine | Keratin azure | 40 | 8 | Ca2+ | 29.12 | Hide dehairing | Jaouadi et al., 2013 |
| Brevibacillus parabrevis | Serine | Keratin | 60 | 8 | Na+, Ca2+, Triton X-100, Tween-40 | 28 | Hide dehairing | Zhang et al., 2016 |
| Brevibacterium luteolum | − | Keratin azure | 30 | 10 | − | − | Hair degradation | Thankaswamy et al., 2018 |
| Caldicoprobacter algeriensis | Serine | Keratin azure | 50 | 7 | Sn2+, Ba2+, Ca2+, Mg2+, and Mn2+ | 33.25 | Hide dehairing | |
| Chryseobacterium L99 sp. nov. | Serine | Keratin azure | 40 | 8 | K+, Zn2+, and Co2+ | 33 | Wool treatment | Lv et al., 2010 |
| Fervidobacterium islandicum | Metallo | − | 80 | 7 | Co2+ | − | Feather degradation | Lee et al., 2015 |
| Fervidobacterium pennavorans | Serine | Casein | 80 | 10 | − | 130 | Feather degradation | |
| Meiothermus sp. 140 | Serine | Keratin azure | 70 | 8 | Ethanol, DMSO | 76 | Feather degradation | Kuo et al., 2012 |
| Meiothermus taiwanensis WR-220 | − | Chicken feather | 65 | 10 | − | 30 | Feather degradation | Wu et al., 2017 |
| Microbacterium sp. kr10 | Metallo | Azocasein | 50 | 7.5 | Zn2+ and Mg2+ | 42 | Feather degradation | Thys and Brandelli, 2006 |
| Serratia marcescens P3 | Metallo | Azokeratin | 40–45 | 6.5 | − | 53 | Skin dehairing | |
| Streptomyces sp.AB1 | Serine | Keratin azure | 75 | 11.5 | Mg2+ | 29.85 | Feather degradation | Jaouadi et al., 2010 |
| Streptomyces sp. S.K1–02 | Serine-metallo | Keratin azure | 70 | 10 | Ca2+ and Mg2+ | − | Keratin hydrolysis | Letourneau et al., 1998 |
| Streptomyces sp. S7 | Serine-metallo | Keratin azure | 45 | 11 | Ca2+ | 44 | − | Tatineni et al., 2008 |
| Streptomyces aureofaciens K13 | Serine-metallo | Keratin | 75 | 12 | Cu2+, Mn2+, and SDS | 46 | Keratin hydrolysis, Detergent formulation | |
| Fungal source | ||||||||
| Aspergillus fumigatus TKF1 | − | Keratin | 50 | 6 | − | 24.3 | Feather degradation | Paul et al., 2014a |
| Aspergillus flavus K-03 | Serine | Keratin azure | 40 | 8 | β-ME, Hg2+, Fe2+, and Mn2+ | 31 | − | Kim, 2007 |
| Aspergillus sulphureus | − | Keratin | 35 | 10 | − | − | − | Sousa et al., 2015 |
| Doratomyces microspores | Serine | Keratin | 50 | 8–9 | − | 33 | − | |
| Microsporum canis | Metallo | Azocoll | 50 | 8 | − | 43.5 | − | |
| Onygena corvina | Serine | Keratin azure | 40–60 | 6–11 | Fe2+ and Ca2+ | 35 | Feather degradation | Huang et al., 2015 |
| Scopulariopsis brevicaulis | Serine | Chicken feather | 40 | 8 | Ca2+ | 75 | Skin dehairing | |
| Trichophyton sp. HA-2 | Serine | Chicken feather | 40 | 7.8 | − | 34 | − |
Summary of biochemical properties of some selected microbial keratinases and their potential applications.
#β-ME, β-mercaptoethanol; DMSO, dimethyl sulfoxide; DTT, dithiothreitol; SDS, sodium dodecyl sulfate. *MW, molecular weight.
An overview of various reports on keratinolytic proteases of microbial sources shows different molecular weight range from 17 to 240 kDa (; ; Nam et al., 2002; ; Mitsuiki et al., 2006; Kim, 2007; Tatineni et al., 2008; ; ; Jaouadi et al., 2013; Hamiche et al., 2019; Hassan et al., 2020b). Keratinases from S. maltophilia BBE11-1 () and S. albidoflavus () have so far been documented to have low molecular weights of 17 and 18 kDa, respectively. In contrast, the keratinase produced by K. rosea was shown to have molecular weight as high as 240 kDa (). Generally, the majority of the documented keratinases are monomeric enzymes with molecular weights of ≤58 kDa (Table 1). However, a novel dimeric keratinolytic protease of 58 kDa with subunit molecular weights of 30 and 28 kDa has been reported (Tiwary and Gupta, 2010). Multimeric microbial keratinases have also been described ().
Keratinolytic proteases generally belong to the serine or metallo class of peptidases regardless of the microbial source. The inhibition by diisopropyl fluorophosphate (DFP) or phenylmethanesulfonyl fluoride (PMSF) indicates their serine protease catalytic mechanism, while inhibition by ethylenediaminetetraacetic acid (EDTA) or 1,10-phenanthroline suggests their type as metalloproteases. EDTA inhibits keratinase of the metalloprotease class through the chelation of the metal ions that are involved in enzyme catalysis (Riffel et al., 2003). Partial inhibition of the keratinolytic enzymes by either EDTA or PMSF was previously reported (Letourneau et al., 1998; Kim, 2007; Tatineni et al., 2008; ), which might be an indication of the presence of mixed keratinolytic proteases.
The importance of cations such as Ca2+, Mg2+, Co2+, Ba2+, K+, Fe2+, Ni2+, Mn2+, and Li+ as stabilizing agents or activators of keratinases has been extensively reported (; Riessen and Antranikian, 2001; Nam et al., 2002; Tatineni et al., 2008; Jaouadi et al., 2010; ; Hamiche et al., 2019). Conversely, the negative impact of some metal ions including Pb2+, Hg2+, Cu2+, Fe3+, Ni2+, and Cd2+ on keratinase activity due to toxic insults has been previously observed (Lin et al., 2009; ; Su et al., 2017; ). Usually, keratinase activities are inhibited, stabilized, or enhanced in a solution that contains surfactants, reducing agents, or solvents. These variable behaviors of keratinases toward chemical agents are attributable to the nature of their side chains/interaction patterns which allosterically regulate the structural orientation and biocatalytic efficiency of the enzymes (). The activity of the alkaline keratinase from S. aureofaciens K13 was enhanced when incubated with SDS, Tween-80 or Triton-X100 (). A similar result was obtained with serine keratinase from B. licheniformis ER-15 where enzymatic activity increased by 6.25 folds when supplemented with 5 mM mercaptoethanol (Tiwary and Gupta, 2010). This stability tendency of keratinolytic proteases in laboratory-based chemical agents has projected their candidacy as robust additives in industrial processes (Reddy et al., 2017; ).
Keratinolytic protease exhibits a broad specificity toward protein-containing natural and synthetic substrates. However, the existence of some discrepancies in substrate specificity for different microbial keratinases may be attributed to the isolation technique and genetic diversity of their sources (Onifade et al., 1998). The specificity of proteases to substrates is proposed to be group dependent, and it is mostly determined by the predominated sequence residues at the C-terminal (P1) and/or N-terminal (P1’) close to the peptide bond to be hydrolyzed (Rawlings, 2016). The insolubility of some proteinaceous substrates could be prompted by inherent inter- or intra-molecular forces such as disulfide bonds that confer mechanical stability to some structural proteins; hence, accessibility of peptide bonds by classical proteases remains impossible (Navone and Speight, 2018). Keratinases, on the other hand, have been naturally endowed with hydrolytic potentials for both soluble and insoluble proteins, and have been adopted, widely as promising candidates in many biotechnological processes (Hassan et al., 2020a). Yamamura et al. (2002) reported that the catalytic efficiencies established for subtilisin Carlsberg and proteinase K toward synthetic substrates were similar to those of protease D-1 from Stenotrophomonas sp. toward the hydrolysis of N-succinyl-L-alanyl-L-alanyl-L-prolyl-L-phenylalanine 4-nitroanilide and N-succinyl-L-alanyl-L-alanyl-L-alanine 4-nitroanilide, respectively. Moreover, Stenotrophomonas sp. protease D-1 hydrolyzed the rigid proteins (keratins, collagen, and elastin) poorly, compared to the soluble proteins (hemoglobin, bovine serum albumin, and casein). Sangali and Brandelli (2000) observed that the keratinase produced by Vibrio sp. kr2 was active toward azokeratin, azocasein, benzoyl-arginine p-nitroanilide, and Alanyl-L-Alanine p-nitroanilide as substrates, and this is an indication that the keratinase produced by strain kr2 may have the potential for different industrial processes and application.
Structural Complexity of Keratin
Epithelial tissues serving structural support functions possess keratin as one of the dominant family of fibrous proteins (Toivola et al., 2015). Keratin, a subtype of intermediate filament (IF) protein, is generally categorized into alpha (α) and beta (β) forms, showing characteristic structural assemblage with diameters of 7 and 3 nm, respectively (Figures 1B, 2B), buried in an amorphous matrix (Wang B. et al., 2016). The α- and β-forms have distinct synthetic pathways, which are reflected in their structures. Nonetheless, keratinocyte localized synthesis of both keratin forms involves coordinated and programmed sequential mechanisms with sets of gene activation and restriction processes (ul Haq and Akram, 2018). In vertebrates, keratins are encoded by 54 conserved genes and are controlled in pairs based on the type of tissues involved (Wang F. et al., 2016). The genes may be grouped into subtypes based on their evolutionary–functional relationship. The molecular architecture of keratin encoding genes in relation to other members of IFs suggests that their emergence was orchestrated by ancestral gene duplication during evolution (Wang F. et al., 2016). Keratinocytes are sites for keratin biosynthesis, and the synthetic processes are prudently coordinated by messenger ribonucleic acid (mRNA). Keratin formation is initiated by mitotic cell division accompany by the keratin proteins biosynthesis. Subsequently, the maturation of keratinocyte potentiates the arrest of cellular protein synthesis and also triggers nucleus degradation; these sequential activities prompt keratin stabilization and cell death (Wang B. et al., 2016). Keratins perform a series of functions in the epithelial tissues, including structural and non-structural cellular functions. However, these properties are conferred during posttranslational modifications, including phosphorylation and glycosylation (Lange et al., 2016), and also by some keratin-linked proteins (). Keratins also possess the tripartite structure uniformly shared among the IF proteins: “a highly conserved central α-helical rod domain flanked by a non-α-helical amino-terminal head domain and carboxy-terminal tail domain” (Nafeey et al., 2016). The unique pliable nature of IFs forms the basis for their role as a mechanical cushion that shields cells from external stressors (Leitner et al., 2012; ). Additionally, keratin may be formed by the aggregation of coiled heterodimers consisting of an acidic and a basic subunit that are organized in an antiparallel manner. The two dimers stagger side by side to form a tetramer, and the tetramers associate in a lateral orientation to constitute a 10 nm diameter filament with a smooth surface and apolar characteristics and approximately made up of a cross-section of 16 coiled coils dimers (Wang F. et al., 2016). The variation in the molecular architecture and synthesis of the filament proteins are the important properties that distinguish α- and β-keratins (Jones et al., 1997), and these are represented in Figures 1, 2.
FIGURE 1
FIGURE 2
Keratin Biodegradation – the Keratinase and Disulfide Reductase Synergy
Keratin mechanical durability is sustained by the inherent disulfide cross-linkages; therefore reduction of the densely populated disulfide bonds (sulfitolysis) in the keratin polypeptide enhances proteolytic cleavage, thus leading to enhanced degradation. As such, the detection of a high amount of thiol groups in the fermentation medium suggests a significant reduction of cysteine disulfide linkages within the α-helix motifs, which exposes the peptide bonds to proteolysis (Nnolim et al., 2020b). Consequently, the complete degradation of keratin may be achieved by the synergistic action of keratinolytic protease and disulfide bond reductase-like protein. There has been an extensive discussion on the mechanisms that bring about complete keratin degradation, which involve the actions of keratinase, disulfide reductase, sulfite or thiosulfate, and redox system (). Scanning electron microscopy showed the effective combinatorial action of keratinolytic protease and disulfide bond reductase from Bacillus sp. on the structural perturbation of native keratin substrate compare to the separate activity of the keratinolytic protease supplemented with reducing agent or proteinase K (Rahayu et al., 2012). Yamamura et al. (2002) characterized two enzymes (keratinase and disulfide bond reductase) from Stenotrophomonas sp. D-1 that completely disintegrated keratin. Similarly, four extracellular keratinases with varying molecular weights, as confirmed by native PAGE zymography, from Pseudomonas stutzeri K4 showed cooperative actions toward the disintegration of keratin (). Furthermore, showed the combined actions of three keratinolytic proteases designated as K1, K2, and K3 from S. maltophilia BB11-1 for keratin hydrolysis after their separation by chromatography. The respective participation of the enzymes in the keratinolytic process revealed K1 to have keratinase properties and to be mainly associated with keratin degradation (Figure 3); K2 possessed peptide bond hydrolysis properties, and K3 was a disulfide reductase involved in sulfitolysis.
FIGURE 3
The media nitrogen and carbon quotient influence microbial protease secretion and, keratinous proteins are inassimilable to microbial cells due to their structural complexity; therefore, production of elaborate keratinolytic enzymes may be regulated in response to media constituents (Riffel et al., 2011; Nnolim et al., 2020a). Worthy of note is the fact that several reports attributed unitary secreted enzymes to the complete degradation of keratin, thus controverting the position of cooperative enzyme actions. A comprehensive understanding of the mechanism behind keratinolysis still requires further studies, and the nature of individual keratinase should be put into perspective when defining the activity and potential application of the enzyme mixture.
Keratinase Catalytic Efficiency Enhancement – a Protein Engineering Approach
Limitations associated with proteases derived from wild-type microbial species in industrial applications include low tolerance to some industrial operations and processing conditions such as pH, temperature, presence of organic solvents, salt, detergent, and oxidative agents. These factors drastically diminish the catalytic performance and applicability of the enzymes (
Modification for Improved Catalytic Efficiency
A study based on recombinant strains with a higher enzyme functionality using chemical mutagen gave a modified KD-N2 with enzyme activity that was 2.5 folds higher than the unmodified strain (
Modification to Switch Substrate Specificity
Keratinases producing microbes are limited, and the enzymes show a wide spectral distribution of molecular weight. Keratinases with relatively low molecular weight may solely have the catalytic part, while the medium to high molecular weight keratinases contain multi-domain structural assemblies that determine their substrate specificities (Kim et al., 2004). A conserved Gly166, situated beneath the active site of subtilisin BPN, was interchanged with the non-ionic residue to alter its specificity to other hydrophobic substrates (
Collagen-degrading keratinase has limited application in the bioprocessing of leather products. However, substrate specificity alteration by protein engineering may pave the way for their potential application in the leather industry. Previously, it was reported that PPC domain of KerSMD presented sequence homology with vEP C-ter 100 that has a high affinity for collagen substrate (
Modification for Chemical and pH Tolerance
Protease inclusion in modern laundry detergent as a major additive is essential for enhanced cleaning performance (Vojcic et al., 2015; Hammami et al., 2018). Keratinases are increasingly replacing the classic proteases in laundry detergent formulation because of their ability to hydrolyze an array of proteinaceous compounds and their relative stability with surfactants and organic solvents that are utilized in the detergent formulation (Paul et al., 2014c; Reddy et al., 2017). The impact of some chemical agents such as chaotropic agents and surfactants on protein structure may be an important parameter for assessment of the commercial value of a protein (Li et al., 2014). The C-terminus truncation greatly enhanced the tolerance of the keratinase from S. maltophilia to detergents and improved its enzymatic activity (
The PPC domain removal from V355 of KerSMD promoted the alkalinity – a 40% enhancement of enzyme activity was observed at pH 12 (
Modification for Halophilicity and Thermostability
Halo-tolerance is an important property of industrial enzymes (Yan et al., 2009; Takenaka et al., 2015). Halophilicity may be attributed to the ability of the protein amino acid residues to resist the destabilizing effect of surrounding electrolytes, and most of the halo-tolerant proteins have been described to have similar sequences dominated by acidic residues (
Environmental Impact of Keratinous Waste and the Ecological Implications of Keratinase Producing Microbes
The exponential increase in the global population is associated with pressure on agro-industries to increase production toward meeting the demand of the teeming population. Consequently, there is an increased generation of agro-industrial wastes, including keratinous wastes from the poultry processing farms, leather industry, and slaughterhouse (Tesfaye et al., 2017; Srivastava et al., 2020). Efficient management of the by-products, through recycling into value-added products and proper disposal of unusable waste, is of vital importance. In some instances, associated costs in the waste disposal process may be high if the known efficient means are applied to avert the detrimental effects of these wastes on the environment (Jaouadi et al., 2009). Lack of waste management regulatory measures and the non-adherence to the regulatory standard, where it exists, leave the environment littered with keratinous wastes, which in turn culminate in environmental pollution (Verma et al., 2017;
For instance, huge amount of hairs generated during leather processing as by-products are mostly landfilled or composted (Thankaswamy et al., 2018); with high tendency of exuding noxious gases that instigate air pollution due to the load of chemical constituents and microbial activity on the nitrogen-rich biomass (
The low economic importance and high mechanical stability of feathers result in their indiscriminate disposal and accumulation in the environment (
The myriad of attributes for which microbes are endowed with play a significant role in the bio-geo-chemical processes in the environment. The maintenance of homeostatic balance in extreme situations, utilization of all known material (macro and micro), and elements as sources of energy and, or cellular building tools, are attributable to the diversity of the genome and the complexity of the microbial expression systems (
Conversely, indiscriminate damage to proteinaceous component of cells and tissues by exuded keratinase may constitute another form of bio-hazard if it occurs in an unprecedented manner. However, limited manifestations have been reported on some pathogenic fungi that inhabit skin, causing mycosis and fur or hair grass-roots removal; and some dermatophytes including Arthroderma, Microsporum, Trichophyton, and Chrysosporium group have been in the fore (Huang et al., 2015;
Application of Microbial Keratinolytic Proteases
Keratinolytic proteases are incrementally gaining traction in industrial processes as an alternative to the classic chemical agents currently used. The invaluable potentials embedded in microbial keratinases are continuously evolving and are exploited in different bioprocesses (Figure 4), including but not limited to feed production, organic fertilizer production, detergent formulation, leather production, cosmetics, as well as in medicine and nanotechnology.
FIGURE 4

A flow chart of microbial keratinase application potential.
Livestock Feed
The use of feather meal in supplementation of livestock feed has been in practice for decades; however, there has been concern about the nutritive value of the meal due to the unavailability of the utilizable protein in the feed. Keratins proteins in feathers and other keratinous resources are mostly inaccessible if the structural orientation contributed by different chemical groups is not significantly dismembered, because they are not digestible by ruminants or any other livestock (Williams et al., 1991;
Leather Production
Leather production is one of the highest-ranked socio-economic activities for many countries in the world. Because of the routine use of relatively toxic chemicals in leather processing, there has been a lot of health risk and ecological challenges associated with this practice (Hammami et al., 2018). Processing of animal hides entails various steps from the skin to the processed leather, which involves soaking, dehairing, bating, and tanning (Hamiche et al., 2019). Agents that could digest the protein-rich matter in the hides or skins are also applied in these rigorous operations, and one of the most polluting processes in leather making operations is the dehairing step (
Detergent Formulation
In contemporary times, using detergents formulated from bio-additives is preferred over the typical synthetic-based detergents. This is attributed to their effective cleaning attributes such as low-temperature washing compatibility, recalcitrant dirt removal properties, cloth fiber friendliness, and biodegradability (Jaouadi et al., 2009). The general performance of proteolytic enzymes in detergent is determined by several factors, including the washing medium pH, temperature, and component of the detergent (Reddy et al., 2017; Hammami et al., 2018). Ideally, proteases that are applied in the detergent making process must possess excellent activities and remain sufficiently stable within an increased spectrum of pH and temperatures, and also show a high degree of compatibility with other detergent ingredients, such as oxidizing and sequestering agents (Kumar and Takagi, 1999). Previously, the predominantly used detergent proteases in commercial products included Subtilisin Carlsberg (SC), Subtilisin Novo, Alcalase, Esperase, and Savinase (Outtrup et al., 1995). These proteases showed some levels of stability at conditions of elevated temperature and pH. During the preparation of bleach-based detergent, some active constituents like peroxide agents (H2O2), optical fiber brighteners, non-ionic surfactants (Tween-80), and anionic surfactant (SDS) are included, with the proteases usually showing a high level of inconsistency in the presence of these agents. Hence, such properties compromise their involvement in the present-day detergent formulation (Paul et al., 2016; Reddy et al., 2017). Therefore, there is a need to discover microbial enzymes that can function in the stipulated harsh conditions.
Microbial keratinases, on the other hand, is not hampered by surface-active agents, making it a good candidate for the formulation of both the liquid and solid detergents (
Organic Fertilizer and Cosmetic Production
Keratin-rich wastes are known to have little or no application. Nonetheless, bioconversion of these high content keratin wastes may be an attractive approach toward valorization into cost-effective and eco-friendly resources for potential use as a slow-releasing nitrogen source for soil amendment (
In the cosmetic sector, keratinases have been included as an active constituent in the preparation of topical products used as hair removals (
Other Potential Keratinase Applications
Keratinases have been reported to effectively destroy infective prion protein, and this might be due to the common similarities in the architecture of prion and keratin, such as fibrous and β-sheet-dominated proteins (Xia et al., 2012). Keratinase PWD-1 effectively degraded diseased prion protein (Langeveld et al., 2003). Mitsuiki et al. (2006) reported absolute decomposition of highly infective prion protein in 3 min by novel alkaline keratinolytic protease (NAPase) at pH 11 and 60°C. A study by Okoroma et al. (2013) implicated keratinase from keratinolytic B. licheniformis N22 coupled with bio-surfactant in complete degradation of the prion protein that causes scrapie after 10 min at 65°C.
Eco-friendly waste management is at the core of environmental sustainability. Bioenergy is often produced from an array of agro-industrial wastes with significant saccharide contents and requires basic construction technology, making it a sustainable fuel from both the economic and ecological points of view. The production involves a consolidated process that is initiated by biomass depolymerization; hence keratinase action on fibrous and intractable keratinous residues provides a starter material for this process. Chicken feathers pretreatment with recombinant keratinase from B. megaterium was reported to enhance biogas production (
Keratinase may also find application in the treatment of industrial wastewater. On that note, keratinase from Meiothermus taiwanensis WR-220 immobilized on cheap support; modified bagasse cellulose efficiently decolorized molasses wastewater with percentage decolorization that ranged from 84.7 to 90.2% (Zhang et al., 2019). The melanoidins removal performance of the keratinase was superior to other commercial immobilized enzymes tested, and this would open a new vista for yet another sustainable application of keratinase (Zhang et al., 2019).
Bio-digested avian feathers have shown more consistent results during analysis of non-protein biomolecules, including corticosterone when compare to other mechanical methods that present some limitations and technical concerns (Romero and Fairhurst, 2016). Consequently, keratinase from Bacillus sp. C4 promoted the extraction of glucocorticoids from chicken feather biomass (
Future Recommendation
This study presented comprehensive progress in the field of microbial keratinase research. Efforts have been made to expand the applicability of keratinase because of its multifaceted application potentials for the implementation of green technological processes. However, one of the bottlenecks facing keratinase research is low yield even though many researchers have explored different yield enhancement strategies, at laboratory scale, to upgrade extracellular keratinase production by wild microorganisms. Importantly, molecular optimization (turning off some unnecessary metabolic pathways that compete with keratinase gene upregulation) of keratinase production could be combined with fundamental physico-chemical conditions construction if industrial-scale availability of the enzyme is envisaged. The development of such robust microbial strain would imperatively potentiate volumetric keratinase productivity. Furthermore, various microbial enzymes have been identified during the bio-decomposition of keratinous biomass by keratinolytic microbes. However, little is known about the action of these non-keratinase metabolites (lipase, cellulase, etc.) in mechanistic keratin degradation. Therefore, research into investigating the role of these enzymes in the biodegradation of keratinous materials portends a viable approach worthy of exploitation, as it may hold some potentialities for keratin-rich agroindustrial wastes valorization via microbial enzyme cocktail strategy. Additionally, a few keratinase-based formulations prepared predominantly from B. licheniformis, useful for improving the nutritional values of livestock feeds, have been commercialized so far. The commercialization of more products of similar nature would guarantee cheap livestock production; also, their preparation using microbial consortium could provide better feedstuffs laced with bioavailable nutrients. Lastly, microbial keratinase, at bench scale, has shown immense potential as a sustainable substitute for chemical dehairing agents used in leather processing. However, no known product is available in the market for the green processing of hide and skins at an industrial scale. Therefore, if put into perspective, the formulation of efficient keratinase-based unhairing products for industrial processing of hides would significantly reduce the environmental pollution and health hazard instigated by the fundamentally used chemical counterparts.
Conclusion
Proteases have remarkably gained recognition as green catalysts with many prospects, with potential applications in several biotechnological and industrial processes. Keratinases, a group of proteases that effectively disintegrate the recalcitrant and insoluble keratin, has been gaining attention due to their many benefits. Microbial keratinase-mediated degradation of keratin-rich substrates has potentiated the sustainable valorization and bio-cycling of agro-industrial wastes in cost-effective and eco-friendly ways. The discovery of keratinases has significantly changed the technological processes for processing complex materials; from classic approaches to more sustainable bio-based methods.
Future investigation is needed to elucidate the mechanisms of keratinolysis since the process can be catalyzed by a single keratinase or in synergy with other enzymes. The robustness of keratinases has made it a highly important enzyme that would play a vital role in the present and future dynamics of the bio-economy. Besides, advances in technology can be used to improve the properties of microbial keratinases, potentially leading to new functionalities and applications in the future.
Statements
Author contributions
NN and UN contributed to conceptualization. UN contributed to the resources and funding acquisition. NN contributed to data curation, software, formal analysis, writing – original draft. CU contributed to writing – review and editing. UN and AO contributed to supervision, writing – review, and editing. All authors read and approved its final version.
Funding
The Department of Science and Innovation (DSI) and the Technology Innovation Agency (TIA) supported this work under SIIP enzyme and microbial technologies (Grant Number: DST/CON/0177/2018). We also acknowledge the support of the South African Medical Research Council (SAMRC).
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
References
1
Abdel-FattahA. M.El-GamalM. S.IsmailS. A.EmranM. A.HashemA. M. (2018). Biodegradation of feather waste by keratinase produced from newly isolated Bacillus licheniformis ALW1.J. Genet. Eng. Biotechnol.16311–318. 10.1016/j.jgeb.2018.05.005
2
Abdel-fattahA. M.NashyE. S. H.SabielE. T. A.HussienM. M.AttiaA. S. (2015). Novel keratinolytic activity of Cyberlindnera fabianii Nrc3 aza as a plant growth promoting agent (PGPA).Int. J. Appl. Sci. Biotechnol.3609–618. 10.3126/ijasbt.v3i4.13683
3
AbiramiS.RagaviR.AntonyV. S. (2020). Utilization of keratinolytic Lichtheimia corymbifera AS1 for degradation of cattle hoove–a slaughter house waste to use in plant growth.Biointerface Res. Appl. Chem.106417–6426. 10.33263/briac105.64176426
4
AdelereI. A.LateefA. (2016). Keratinases: emerging trends in production and applications as novel multifunctional biocatalysts.Kuwait J. Sci.43118–127.
5
AdetunjiC. O.AdejumoI. O. (2018). Efficacy of crude and immobilizedenzymes from Bacillus licheniformis for production of biodegraded feather meal and their assessment on chickens.Environ. Technol. Innov.11116–124. 10.1016/j.eti.2018.05.002
6
AdigüzelA. C.BitlisliB. O.YasaI.EriksenN. T. (2009). Sequential secretion of collagenolytic, elastolytic, and keratinolytic proteases in peptide limited cultures of two Bacillus cereus strains isolated from wool.J. Appl. Microbiol.107226–234. 10.1111/j.1365-2672.2009.04200.x
7
AkhterM.Wal MarzanL.AkterY.ShimizuK. (2020). Microbial bioremediation of feather waste for keratinase production: an outstanding solution for leather dehairing in tanneries.Microbiol. Insights13:1178636120913280. 10.1177/1178636120913280
8
AlahyaribeikS.SharifiS. D.TabandehF.HonarbakhshS.GhazanfariS. (2020). Bioconversion of chicken feather wastes by keratinolytic bacteria.Process Saf. Environ Prot.135171–178. 10.1016/j.psep.2020.01.014
9
AlbaA. C.StrauchT. A.KeislerD. H.WellsK. D.KeslerD. C. (2019). Using a keratinase to degrade chicken feathers for improved extraction of glucocorticoids.Gen. and Comp. Endocrinol.27035–40. 10.1016/j.ygcen.2018.10.002
10
AmmasiR.VictorJ. S.ChellanR.ChellappaM. (2019). Amino acid enriched proteinous wastes: Recovery and reuse in leather making.Waste Biomass Valor.115793–5807. 10.1007/s12649-019-00912-6
11
AnbuP.GopinathS. C. B.HildaA.AnnaduraiG. (2005). Purification of keratinase from poultry farm isolate-Scopulariopsis brevicaulis and statistical optimization of enzyme activity.Enzyme Microb. Technol.36639–647. 10.1016/j.enzmictec.2004.07.019
12
AnbuP.HildaA.SurH. W.HurB. K.JayanthiS. (2008). Extracellular keratinase from Trichophyton sp. HA-2 isolated from feather dumping soil.Int. Biodeterior. Biodegradation62287–292. 10.1016/j.ibiod.2007.07.017
13
ArokiyarajS.VargheseR.AhmedB. A.DuraipandiyanV.Al-DhabiN. A. (2019). Optimizing the fermentation conditions and enhanced production of keratinase from Bacillus cereus isolated from halophilic environment.Saudi J. Biol. Sci.26378–381. 10.1016/j.sjbs.2018.10.011
14
AshrafN. M.KrishnagopalA.HussainA.KastnerD.SayedA. M. M.MokY. K.et al (2019). Engineering of serine protease for improved thermostability and catalytic activity using rational design.Int. J. Biol. Macromol.126229–237. 10.1016/j.ijbiomac.2018.12.218
15
BachE.DaroitD. J.CorrêaA. P. F.BrandelliA. (2011). Production and properties of keratinolytic proteases from three novel Gram-negative feather-degrading bacteria isolated from Brazilian soils.Biodegradation221191–1201. 10.1007/s10532-011-9474-0
16
BachE.Sant’AnnaV.DaroitD. J.CorrêaA. P. F.SegalinJ.BrandelliA. (2012). Production, one-step purification, and characterization of a keratinolytic protease from Serratia marcescens P3.Process Biochem.472455–2462. 10.1016/j.procbio.2012.10.007
17
BagewadiZ. K.SikandarI. M.HarichandraZ. N. (2018). Response surface methodology based optimization of keratinase production from Trichoderma harzianum isolate HZN12 using chicken feather waste and its application in dehairing of hide.J. Environ. Chem. Eng.64828–4839. 10.1016/j.jece.2018.07.007
18
BarbaC.MéndezS.Roddick-LanzilottaA.KellyR.ParraJ. L.CoderchL. (2008). Cosmetic effectiveness of topically applied hydrolysed keratin peptides and lipids derived from wool.Skin Res. Technol.14243–248. 10.1111/j.1600-0846.2007.00280.x
19
BarmanN. C.ZohoraF. T.DasK. C.MowlaM. G.BanuN. A.SalimullahM.et al (2017). Production, partial optimization and characterization of keratinase enzyme by Arthrobacter sp. NFH5 isolated from soil samples.AMB Express7:181. 10.1186/s13568-017-0462-6
20
BenkiarA.NadiaZ. J.BadisA.RebzaniF.SorayaB. T.RekikH.et al (2013). Biochemical and molecular characterisation of a thermo-and detergent-stable alkaline serine keratinolytic protease from Bacillus circulans strain DZ100 for detergent formulations and feather-biodegradation process.Int. Biodeterior. Biodegrad.83129–138. 10.1016/j.ibiod.2013.05.014
21
BernalC.CairoJ.CoelloN. (2006). Purification and characterisation of a novel exocellular keratinase from Kocuria rosea.Enzyme Microb. Technol.3849–54. 10.1016/j.enzmictec.2005.02.021
22
BhangeK.ChaturvediV.BhattR. (2016). Simultaneous production of detergent stable keratinolytic protease, amylase and biosurfactant by Bacillus subtilis PF1 using agro industrial waste.Biotechnol. Rep.1094–104. 10.1016/j.btre.2016.03.007
23
BockleB.GalunskyB.MuellerR. (1995). Characterisation of a keratinolytic serine proteinase from Streptomyces pactum DSM 40530.Appl. Environ. Microbiol.613705–3710. 10.1128/aem.61.10.3705-3710.1995
24
BohaczJ.Korniłłowicz-KowalskaT. (2019). Fungal diversity and keratinolytic activity of fungi from lignocellulosic composts with chicken feathers.Process Biochem.80119–128. 10.1016/j.procbio.2019.02.012
25
BohaczJ.Korniłłowicz-KowalskaT.KitowskiI.CiesielskaA. (2020). Degradation of chicken feathers by Aphanoascus keratinophilus and Chrysosporium tropicum strains from pellets of predatory birds and its practical aspect.Int. Biodeterior. Biodegrad.151:104968. 10.1016/j.ibiod.2020.104968
26
BoseA.PathanS.PathakK.KehariaH. (2014). Keratinolytic protease production by Bacillus amyloliquefaciens 6B using feather meal as substrate and application of feather hydrolysate as organic nitrogen input for agricultural soil.Waste Biomass Valor.5595–605. 10.1007/s12649-013-9272-5
27
BouacemK.Bouanane-DarenfedA.JaouadiN. Z.JosephM.HaceneH.OllivierB.et al (2016). Novel serine keratinase from Caldicoprobacter algeriensis exhibiting outstanding hide dehairing abilities.Int. J. Biol. Macromol.86321–328. 10.1016/j.ijbiomac.2016.01.074
28
BragullaH. H.HombergerD. G. (2009). Structure and functions of keratin proteins in simple, stratified, keratinized and cornified epithelia.J. Anat.214516–559. 10.1111/j.1469-7580.2009.01066.x
29
BrandelliA. (2008). Bacterial keratinases: useful enzymes for bioprocessing agroindustrial wastes and beyond.Food Bioprocess Technol.1105–116. 10.1007/s11947-007-0025-y
30
BrandelliA.DaroitD. J.RiffelA. (2010). Biochemical features of microbial keratinases and their production and applications.Appl. Microbiol. Biotechnol.851735–1750. 10.1007/s00253-009-2398-5
31
BranskaB.FoøtováL.DvoøákováM.LiuH.PatakovaP.ZhangJ.et al (2020). Chicken feather and wheat straw hydrolysate for direct utilization in biobutanol production.Renew. Energy1451941–1948. 10.1016/j.renene.2019.07.094
32
BressollierP.LetourneauF.UrdaciM.VerneuilB. (1999). Purification and characterisation of a keratinolytic serine proteinase from Streptomyces albidoflavus.Appl. Environ. Microbiol.652570–2576. 10.1128/aem.65.6.2570-2576.1999
33
BroutaF.DescampsF.FettT.LossonB.GerdayC.MignonB. (2001). Purification and characterization of a 43? 5 kDa keratinolytic metalloprotease from Microsporum canis.Med. Mycol.39269–275.
34
CaiC. G.LouB. G.ZhengX. D. (2008). Keratinase production and keratin degradation by a mutant strain of Bacillus subtilis.J. Zhejiang Univ. Sci. B960–67. 10.1631/jzus.b061620
35
CallegaroK.WelterN.DaroitD. J. (2018). Feathers as bioresource: microbial conversion into bioactive protein hydrolysates.Process Biochem.751–9. 10.1016/j.procbio.2018.09.002
36
ChaturvediV.BhangeK.BhattR.VermaP. (2014). Production of kertinases using chicken feathers as substrate by a novel multifunctional strain of Pseudomonas stutzeri and its dehairing application.Biocat. Agric. Biotechnol.3167–174. 10.1016/j.bcab.2013.08.005
37
CheongC. W.LeeY. S.AhmadS. A.OoiP. T.PhangL. Y. (2018). Chicken feather valorization by thermal alkaline pretreatment followed by enzymatic hydrolysis for protein-rich hydrolysate production.Waste Manage.79658–666. 10.1016/j.wasman.2018.08.029
38
Choińska-PulitA.ŁabaW.RodziewiczA. (2019). Enhancement of pig bristles waste bioconversion by inoculum of keratinolytic bacteria during composting.Waste Manage.84269–276. 10.1016/j.wasman.2018.11.052
39
DaroitD. J.BrandelliA. (2014). A current assessment on the production of bacterial keratinases.Crit. Rev. Biotechnol.34372–384. 10.3109/07388551.2013.794768
40
DayanandanA.KanagarajJ.SounderrajL.GovindarajuR.RajkumarG. S. (2003). Application of an alkaline protease in leather processing: an ecofriendly approach.J. Clean. Prod.11533–536. 10.1016/S0959-6526(02)00056-2
41
De Oliveira MartinezJ. P.CaiG.NachtschattM.NavoneL.ZhangZ.RobinsK.et al (2020). Challenges and opportunities in identifying and characterising keratinases for value-added peptide production.Catalysts10:184. 10.3390/catal10020184
42
DongY. Z.ChangW. S.ChenP. T. (2017). Characterisation and overexpression of a novel keratinase from Bacillus polyfermenticus B4 in recombinant Bacillus subtilis.Bioresour. Bioprocess.4:47. 10.1186/s40643-017-0177-1
43
EmranM. A.IsmailS. A.Abdel-FattahA. M. (2020). Valorization of feather via the microbial production of multi-applicable keratinolytic enzyme.Biocatal. Agric. Biotechnol.27:101674. 10.1016/j.bcab.2020.101674
44
EstellD. A.GraycarT. P.MillerJ. V.PowersD. B.BurnierJ. P.NgP. G.et al (1986). Probing steric and hydrophobic effects on enzyme-substrate interactions by protein engineering.Science233659–664. 10.1126/science.233.4764.659
45
FakhfakhN.KtariN.HaddarA.MnifI. H.DahmenI.NasriM. (2011). Total solubilisation of the chicken feathers by fermentation with a keratinolytic bacterium, Bacillus pumilus A1, and the production of protein hydrolysate with high antioxidative activity.Process Biochem.461731–1737. 10.1016/j.procbio.2011.05.023
46
FalcoF. C.EspersenR.SvenssonB.GernaeyK. V.LantzA. E. (2019). An integrated strategy for the effective production of bristle protein hydrolysate by the keratinolytic filamentous bacterium Amycolatopsis keratiniphila D2.Waste Manage.8994–102. 10.1016/j.wasman.2019.03.067
47
FangZ.ShaC.PengZ.ZhangJ.DuG. (2019). Protein engineering to enhance keratinolytic protease activity and excretion in Escherichia coli and its scale-up fermentation for high extracellular yield.Enzyme Microb. Technol.12137–44. 10.1016/j.enzmictec.2018.11.003
48
FangZ.ZhangJ.DuG.ChenJ. (2016). Improved catalytic efficiency, thermophilicity, anti-salt and detergent tolerance of keratinase KerSMD by partially truncation of PPC domain.Sci. Rep.6:27953. 10.1038/srep27953
49
FangZ.YongY. C.ZhangJ.DuG.ChenJ. (2017a). Keratinolytic protease: a green biocatalyst for leather industry.Appl. Microbiol. Biotechnol.1017771–7779. 10.1007/s00253-017-8484-1
50
FangZ.ZhangJ.DuG.ChenJ. (2017b). Rational protein engineering approaches to further improve the keratinolytic activity and thermostability of engineered keratinase KerSMD.Biochem. Eng. J.127147–153. 10.1016/j.bej.2017.08.010
51
FangZ.ZhangJ.LiuB.DuG.ChenJ. (2013). Biochemical characterisation of three keratinolytic enzymes from Stenotrophomonas maltophilia BBE11-1 for biodegrading keratin wastes.Int. Biodeterior. Biodegradation82166–172. 10.1016/j.ibiod.2013.03.008
52
FangZ.ZhangJ.LiuB.DuG.ChenJ. (2015). Insight into the substrate specificity of keratinase KerSMD from Stenotrophomonas maltophilia by site-directed mutagenesis studies in the S1 pocket.RSC Adv.574953–74960. 10.1039/c5ra12598g
53
FangZ.ZhangJ.LiuB.JiangL.DuG.ChenJ. (2014). Cloning, heterologous expression and characterisation of two keratinases from Stenotrophomonas maltophilia BBE11-1.Process Biochem.49647–654. 10.1016/j.procbio.2014.01.009
54
FerozS.MuhammadN.RanayakeJ.DiasG. (2020). Keratin-Based materials for biomedical applications.Bioact. Mater.5496–509. 10.1016/j.bioactmat.2020.04.007
55
FerrarezeP. A. G.CorreaA. P. F.BrandelliA. (2016). Purification and characterization of a keratinolytic protease produced by probiotic Bacillus subtilis.Biocatal. Agric. Biotechnol.7102–109. 10.1016/j.bcab.2016.05.009
56
ForgácsG.AlinezhadS.MirabdollahA.Feuk-LagerstedtE.HorváthI. S. (2011). Biological treatment of chicken feather waste for improved biogas production.J. Environ. Sci.231747–1753. 10.1016/s1001-0742(10)60648-1
57
FrancinoM. P. (2012). The ecology of bacterial genes and the survival of the new.Int. J. Evol. Biol.2012:394026. 10.1155/2012/394026
58
FriedrichA. B.AntranikianG. (1996). Keratin degradation by Fervidobacterium pennavorans, a novel thermophilic anaerobic species of the order thermotogales.Appl. Environ. Microbiol.622875–2882. 10.1128/aem.62.8.2875-2882.1996
59
GegeckasA.ŠimkutëA.GudiukaitëR.ÈitavièiusD. J. (2018). Characterisation and application of keratinolytic paptidases from Bacillus spp.Int. J. Biol. Macromol.1131206–1213. 10.1016/j.ijbiomac.2018.03.046
60
GongJ. S.WangY.ZhangD. D.ZhangR. X.SuC.LiH.et al (2015). Biochemical characterisation of an extreme alkaline and surfactant-stable keratinase derived from a newly isolated actinomycete Streptomyces aureofaciens K13.RSC Adv.524691–24699. 10.1039/c4ra16423g
61
GradišarH.FriedrichJ.KrižajI.JeralaR. (2005). Similarities and specificities of fungal keratinolytic proteases: comparison of keratinases of Paecilomyces marquandii and Doratomyces microsporus to some known proteases.Appl. Environ. Microbiol.713420–3426. 10.1128/aem.71.7.3420-3426.2005
62
GradišarH.KernS.FriedrichJ. (2000). Keratinase of Doratomyces microsporus.Appl. Microbiol. Biotechnol.53196–200. 10.1007/s002530050008
63
GrazianoG.MerlinoA. (2014). Molecular bases of protein halotolerance.Biochim. Biophys. Acta Proteins Proteomics1844850–858. 10.1016/j.bbapap.2014.02.018
64
GrazziotinA.PimentelF. A.De JongE. V.BrandelliA. (2008). Poultry feather hydrolysate as a protein source for growing rats.Braz. J. Vet. Res. An. Sci.4561–67.
65
GrazziotinA.PimentelF. A.SangaliS.de JongE. V.BrandelliA. (2007). Production of feather protein hydrolysate by keratinolytic bacterium Vibrio sp. kr2.Bioresour. Technol.983172–3175. 10.1016/j.biortech.2006.10.034
66
GuoL.LuL.YinM.YangR.ZhangZ.ZhaoW. (2020). Valorization of refractory keratinous waste using a new and sustainable bio-catalysis.Chem. Eng. J.397:125420. 10.1016/j.cej.2020.125420
67
GuptaR.RamnaniP. (2006). Microbial keratinases and their prospective applications: an overview.Appl. Microbiol. Biotechnol.70:21. 10.1007/s00253-005-0239-8
68
GuptaR.SharmaR.BegQ. K. (2013). Revisiting microbial keratinases: next generation proteases for sustainable biotechnology.Crit. Rev. Biotechnol.33216–228. 10.3109/07388551.2012.685051
69
HabbecheA.SaoudiB.JaouadiB.HaberraS.KerouazB.BoudelaaM.et al (2014). Purification and biochemical characterisation of a detergent-stable keratinase from a newly thermophilic actinomycete Actinomadura keratinilytica strain Cpt29 isolated from poultry compost.J. Biosci. Bioeng.117413–421.
70
HamicheS.MechriS.KhelouiaL.AnnaneR.El HattabM.BadisA.et al (2019). Purification and biochemical characterization of two keratinases from Bacillus amyloliquefaciens S13 isolated from marine brown alga Zonaria tournefortii with potential keratin-biodegradation and hide-unhairing activities.Int. J. Biol. Macromol.122758–769. 10.1016/j.ijbiomac.2018.10.174
71
HammamiA.FakhfakhN.AbdelhediO.NasriM.BayoudhA. (2018). Proteolytic and amylolytic enzymes from a newly isolated Bacillus mojavensis SA: characterization and applications as laundry detergent additive and in leather processing.Int. J. Biol. Macromol.10856–68. 10.1016/j.ijbiomac.2017.11.148
72
HassanM. A.Abol-FotouhD.OmerA. M.TamerT. M.AbbasE. (2020a). Comprehensive insights into microbial keratinases and their implication in various biotechnological and industrial sectors: a review.Int. J. Biol. Macromol.154567–583. 10.1016/j.ijbiomac.2020.03.116
73
HassanM. A.TahaT. H.HamadG. M.HashemM.AlamriS.MostafaY. S. (2020b). Biochemical characterisation and application of keratinase from Bacillus thuringiensis MT1 to enable valorisation of hair wastes through biosynthesis of vitamin B-complex.Int. J. Biol. Macromol.153561–572. 10.1016/j.ijbiomac.2020.03.032
74
HossainM. S.AzadA. K.SayemS. A.MostafaG.HoqM. M. (2007). Production and partial characterisation of feather-degrading keratinolytic serine protease from Bacillus licheniformis MZK-3.J. Biol. Sci.7599–606. 10.3923/jbs.2007.599.606
75
HuangY.BuskP. K.HerbstF. A.LangeL. (2015). Genome and secretome analyses provide insights into keratin decomposition by novel proteases from the non-pathogenic fungus Onygena corvina.Appl. Microbiol. Biotechnol.999635–9649. 10.1007/s00253-015-6805-9
76
JadhavP.PathadeG. (2019). Degradation of feathers by bacterial consortium and its application in seed germination.Int. Res. J. Biol. Sci.820–23.
77
JaouadiB.AbdelmalekB.FodilD.FerradjiF. Z.RekikH.ZaraîN.et al (2010). Purification and characterisation of a thermostable keratinolytic serine alkaline proteinase from Streptomyces sp. strain AB1 with high stability in organic solvents.Bioresour. Technol.101836–8369.
78
JaouadiB.Ellouz-ChaabouniS.AliM. B.MessaoudE. B.NailiB.DhouibA.et al (2009). Excellent laundry detergent compatibility and high dehairing ability of the Bacillus pumilus CBS alkaline proteinase (SAPB).Biotechnol. Bioprocess Eng.14503–512. 10.1007/s12257-008-0244-8
79
JaouadiB.Ellouz-ChaabouniS.RhimiM.BejarS. (2008). Biochemical and molecular characterisation of a detergent-stable serine alkaline protease from Bacillus pumilus CBS with high catalytic efficiency.Biochimie901291–1305. 10.1016/j.biochi.2008.03.004
80
JaouadiN. Z.RekikH.BadisA.TrabelsiS.BelhoulM.YahiaouiA. B.et al (2013). Biochemical and molecular characterisation of a serine keratinase from Brevibacillus brevis US575 with promising keratin-biodegradation and hide-dehairing activities.PLoS One8:e76722. 10.1371/journal.pone.0076722
81
JeongJ. H.LeeO. M.JeonY. D.KimJ. D.LeeN. R.LeeC. Y.et al (2010). Production of keratinolytic enzyme by a newly isolated feather-degrading Stenotrophomonas maltophilia that produces plant growth-promoting activity.Process Biochem.451738–1745. 10.1016/j.procbio.2010.07.020
82
JinM.ChenC.HeX.ZengR. (2019). Characterization of an extreme alkaline-stable keratinase from the draft genome of feather-degrading Bacillus sp. JM7 from deep-sea.Acta Oceanol. Sin.3887–95. 10.1007/s13131-019-1350-5
83
JonesL. N.SimonM.WattsN. R.BooyF. P.StevenA. C.ParryD. A. D. (1997). Intermediate filament structure: hard α-keratin.Biophys. Chem.6883–93. 10.1016/s0301-4622(97)00013-6
84
KalaikumariS. S.VennilaT.MonikaV.ChandrarajK.GunasekaranP.RajendhranJ. (2019). Bioutilization of poultry feather for keratinase production and its application in leather industry.J. Clean. Prod.20844–53. 10.1016/j.jclepro.2018.10.076
85
KangD.HerschendJ.Al-SoudW. A.MortensenM. S.GonzaloM.JacquiodS.et al (2018). Enrichment and characterization of an environmental microbial consortium displaying efficient keratinolytic activity.Bioresour. Technol.270303–310. 10.1016/j.biortech.2018.09.006
86
KimJ. D. (2007). Purification and characterisation of a keratinase from a feather-degrading fungus, Aspergillus flavus Strain K-03.Mycobiology32219–225. 10.4489/myco.2007.35.4.219
87
KimJ. S.KluskensL. D.de VosW. M.HuberR.van der OostJ. (2004). Crystal structure of fervidolysin from Fervidobacterium pennivorans, a keratinolytic enzyme related to subtilisin.J. Mol. Biol.335787–797. 10.1016/j.jmb.2003.11.006
88
KojimaM.KanaiM.TominagaM.KitazumeS.InoueA.HorikoshiK. (2006). Isolation and characterisation of a feather-degrading enzyme from Bacillus pseudofirmus FA30-01.Extremophiles10229–235. 10.1007/s00792-005-0491-y
89
Korniłłowicz-KowalskaT.BohaczJ. (2011). Biodegradation of keratin waste: theory and practical aspects.Waste Manage.311689–1701. 10.1016/j.wasman.2011.03.024
90
KowalczykP.Mahdi-OraibiS.MisiewiczA.GabzdylN.MiskiewiczA.SzpareckiG. (2018). Feather-degrading bacteria: their biochemical and genetic characteristics.Arab. J. Sci. Eng.4333–41. 10.1007/s13369-017-2700-2
91
KshetriP.RoyS. S.ChanuS. B.SinghT. S.TamreihaoK.SharmaS. K.et al (2020). Valorization of chicken feather waste into bioactive keratin hydrolysate by a newly purified keratinase from Bacillus sp. RCM-SSR-102.J. Environ. Manage.273:111195. 10.1016/j.jenvman.2020.111195
92
KumarC. G.TakagiH. (1999). Microbial alkaline proteases: from a bioindustrial viewpoint.Biotechnol. Adv.17561–594. 10.1016/s0734-9750(99)00027-0
93
KunertJ. (2000). Physiology of keratinophilic fungi.Rev. Iberoam. Micol.177–85.
94
KuoJ. M.YangJ. I.ChenW. M.PanM. H.TsaiM. L.LaiY. J.et al (2012). Purification and characterisation of a thermostable keratinase from Meiothermus sp. I40.Int. Biodeterior. Biodegradation70111–116. 10.1016/j.ibiod.2012.02.006
95
ŁabaW.SzczekałaK. B. (2013). Keratinolytic proteases in biodegradation of pretreated feathers.Pol. J. Environ. Stud.221101–1109.
96
LangeL.HuangY.BuskP. K. (2016). Microbial decomposition of keratin in nature—a new hypothesis of industrial relevance.Appl. Microbiol. Biotechnol.1002083–2096. 10.1007/s00253-015-7262-1
97
LangeveldJ. P.WangJ. J.Van de WielD. F.ShihG. C.GarssenG. J.BossersA.et al (2003). Enzymatic degradation of prion protein in brain stem from infected cattle and sheep.J. Infect. Dis.1881782–1789. 10.1086/379664
98
LeeY. J.DhanasinghI.AhnJ. S.JinH. S.ChoiJ. M.LeeS. H.et al (2015). Biochemical and structural characterisation of a keratin-degrading M32 carboxypeptidase from Fervidobacterium islandicum AW-1.Biochem. Biophys. Res. Commun.468927–933. 10.1016/j.bbrc.2015.11.058
99
LeitnerA.PaustT.MartiO.WaltherP.HerrmannH.BeilM. (2012). Properties of intermediate filament networks assembled from keratin 8 and 18 in the presence of Mg2+.Biophys. J.103195–201. 10.1016/j.bpj.2012.06.014
100
LetourneauF.SoussotteV.BressollierP.BranlandP.VerneuilB. (1998). Keratinolytic activity of Streptomyces sp. S. K1-02: a new isolated strain.Lett. Appl. Microbiol.2677–80. 10.1046/j.1472-765x.1998.00281.x
101
LiQ. (2019). Progress in microbial degradation of feather waste.Front. Microbiol.10:2717. 10.3389/fmicb.2019.02717
102
LiZ.RoccatanoD.LorenzM.MartinezR.SchwanebergU. (2014). Insights on activity and stability of subtilisin E towards guanidinium chloride and sodium dodecylsulfate.J. Biotechnol.16987–94. 10.1016/j.jbiotec.2013.11.001
103
LinH. H.YinL. J.JiangS. T. (2009). Expression and purification of Pseudomonas aeruginosa keratinase in Bacillus subtilis DB104 expression system.J. Agric. Food Chem.577779–7784. 10.1021/jf901903p
104
LvL. X.SimM. H.LiY. D.MinJ.FengW. H.GuanW. J.et al (2010). Production, characterization and application of a keratinase from Chryseobacterium L99 sp. nov.Process Biochem.451236–1244. 10.1016/j.procbio.2010.03.011
105
MacedoA. J.da SilvaW. O. B.GavaR.DriemeierD.HenriquesJ. A. P.TermignoniC. (2005). Novel keratinase from Bacillus subtilis S14 exhibiting remarkable dehairing capabilities.Appl. Environ. Microbiol.71594–596. 10.1128/aem.71.1.594-596.2005
106
MitsuikiS.HuiZ.MatsumotoD.SakaiM.MoriyamaY.FurukawaK.et al (2006). Degradation of PrPSc by keratinolytic protease from Nocardiopsis sp. TOA-1.Biosci. Biotechnol. Biochem.701246–1248. 10.1271/bbb.70.1246
107
MoktadirM. A.AhmadiH. B.SultanaR.LiouJ. J.RezaeiJ. (2020). Circular economy practices in the leather industry: A practical step towards sustainable development.J. Clean Prod.251:119737. 10.1016/j.jclepro.2019.119737
108
NafadyN. A.HassanE. A.Abd-AllaM. H.BagyM. M. K. (2018). Effectiveness of eco-friendly arbuscular mycorrhizal fungi biofertilizer and bacterial feather hydrolysate in promoting growth of Vicia faba in sandy soil.Biocatal. Agric. Biotechnol.16140–147. 10.1016/j.bcab.2018.07.024
109
NafeeyS.MartinI.FelderT.WaltherP.FelderE. (2016). Branching of keratin intermediate filaments.J. Struct. Biol.194415–422. 10.1016/j.jsb.2016.03.023
110
NamG. W.LeeD. W.LeeH. S.LeeN. J.KimB. C.ChoeE. A.et al (2002). Native-feather degradation by Fervidobacterium islandicum AW-1, a newly isolated keratinase-producing thermophilic anaerobe.Arch. Microbiol.178538–547. 10.1007/s00203-002-0489-0
111
NavoneL.SpeightR. (2018). Understanding the dynamics of keratin weakening and hydrolysis by proteases.PLoS One13:e0202608. 10.1371/journal.pone.0202608
112
NnolimN. E.OkohA. I.NwodoU. U. (2020a). Bacillus sp. fpf-1 produced keratinase with high potential for chicken feather degradation.Molecules25:150. 10.3390/molecules250715055
113
NnolimN. E.OkohA. I.NwodoU. U. (2020b). Proteolytic bacteria isolated from agro-waste dumpsites produced keratinolytic enzymes.Biotechnol. Rep.27:e00483. 10.1016/j.btre.2020.e00483
114
OkoromaE. A.PurchaseD.GarelickH.MorrisR.NealeM. H.WindlO.et al (2013). Enzymatic formulation capable of degrading scrapie prion under mild digestion conditions.PLoS One8:e68099. 10.1371/journal.pone.0068099
115
OnifadeA. A.Al-SaneN. A.Al-MusallamA. A.Al-ZarbanS. (1998). A review: potentials for biotechnological applications of keratin-degrading microorganisms and their enzymes for nutritional improvement of feathers and other keratins as livestock feed resources.Bioresour. Technol.661–11. 10.1016/s0960-8524(98)00033-9
116
OuttrupH.DambmannC.ChristiansenM.AaslyngD. A.Nove NordiskA. S. (1995). Alkaline Protease Bacillus sp. JP 395, Method of Making and Detergent Compositions.U.S. Patent 5466594. Brussels: EC.
117
ParraR.AldredD.MaganN. (2005). Medium optimization for the production of the secondary metabolite squalestatin S1 by a Phoma sp. combining orthogonal design and response surface methodology.Enzyme Microb. Technol.37704–711. 10.1016/j.enzmictec.2005.04.009
118
PatinvohR. J.Feuk-LagerstedtE.LundinM.HorváthI. S.TaherzadehM. J. (2016). Biological pretreatment of chicken feather and biogas production from total broth.Appl. Biochem. Biotechnol.1801401–1415. 10.1007/s12010-016-2175-8
119
PaulT.DasA.MandalA.HalderS. K.DasMohapatraP. K.PatiB. R.et al (2014a). Production and purification of keratinase using chicken feather bioconversion by a newly isolated Aspergillus fumigatus TKF1: detection of valuable metabolites.Biomass Convers. Biorefin.4137–148. 10.1007/s13399-013-0090-6
120
PaulT.DasA.MandalA.HalderS. K.DasMohapatraP. K.PatiB. R.et al (2014b). Valorisation of chicken feather waste for production of keratinase, oligopeptides and essential amino acids under submerged fermentation by Paenibacillus woosongensis TKB2.Waste Biomass Valor.5575–584. 10.1007/s12649-013-9267-2
121
PaulT.DasA.MandalA.HalderS. K.JanaA.MaityC.et al (2014c). An efficient cloth cleaning properties of a crude keratinase combined with detergent: towards industrial viewpoint.J. Clean. Prod.66672–684. 10.1016/j.jclepro.2013.10.054
122
PaulT.JanaA.MandalA. K.MandalA.MohpatraP. K. D.MondalK. C. (2016). Bacterial keratinolytic protease, imminent starter for NextGen leather and detergent industries.Sustain. Chem. Pharm.38–22. 10.1016/j.scp.2016.01.001
123
PereiraJ. Q.LopesF. C.PetryM. V.da Costa MedinaL. F.BrandelliA. (2014). Isolation of three novel Antarctic psychrotolerant feather-degrading bacteria and partial purification of keratinolytic enzyme from Lysobacter sp. A03.Int. Biodeterior. Biodegrad.881–7. 10.1016/j.ibiod.2013.11.012
124
RahayuS.SyahD.SuhartonoM. T. (2012). Degradation of keratin by keratinase and disulfide reductase from Bacillus sp. MTS of Indonesian origin.Biocat. Agric Biotechnol.1152–158. 10.1016/j.bcab.2012.02.001
125
RajputR.TiwaryE.SharmaR.GuptaR. (2012). Swapping of pro-sequences between keratinases of Bacillus licheniformis and Bacillus pumilus: altered substrate specificity and thermostability.Enzyme Microb. Technol.51131–138. 10.1016/j.enzmictec.2012.04.010
126
RamnaniP.SinghR.GuptaR. (2005). Keratinolytic potential of Bacillus licheniformis RG1: structural and biochemical mechanism of feather degradation.Can. J. Microbiol.51191–196. 10.1139/w04-123
127
RawlingsN. D. (2016). Peptidase specificity from the substrate cleavage collection in the MEROPS database and a tool to measure cleavage site conservation.Biochimie1225–30. 10.1016/j.biochi.2015.10.003
128
ReddyM. R.ReddyK. S.ChouhanY. R.BeeH.ReddyG. (2017). Effective feather degradation and keratinase production by Bacillus pumilus GRK for its application as bio-detergent additive.Bioresour. Technol.243254–263. 10.1016/j.biortech.2017.06.067
129
RibitschD.KarlW.Birner-GruenbergerR.GruberK.EiteljoergI.RemlerP.et al (2010). C-terminal truncation of a metagenome-derived detergent protease for effective expression in E. coli.J. Biotechnol.150408–416. 10.1016/j.jbiotec.2010.09.947
130
RiegerT. J.De OliveiraC. T.PereiraJ. Q.BrandelliA.DaroitD. J. (2017). Proteolytic system of Bacillus sp. CL18 is capable of extensive feather degradation and hydrolysis of diverse protein substrates.Br. Poult. Sci.58329–335. 10.1080/00071668.2017.1293229
131
RiessenS.AntranikianG. (2001). Isolation of Thermoanaerobacter keratinophilus sp. nov., a novel thermophilic, anaerobic bacterium with keratinolytic activity.Extremophiles5399–408. 10.1007/s007920100209
132
RiffelA.BrandelliA. (2006). Keratinolytic bacteria isolated from feather waste.Brazilian J. Microbiol.37395–399. 10.1590/s1517-83822006000300036
133
RiffelA.DaroitD. J.BrandelliA. (2011). Nutritional regulation of protease production by the feather-degrading bacterium Chryseobacterium sp. kr6.New Biotechnol.28153–157. 10.1016/j.nbt.2010.09.008
134
RiffelA.OrtolanS.BrandelliA. (2003). De-hairing activity of extracellular proteases produced by keratinolytic bacteria.J. Chem. Technol. Biotechnol.78855–859. 10.1002/jctb.828
135
RomeroL. M.FairhurstG. D. (2016). Measuring corticosterone in feathers: strengths, limitations, and suggestions for the future.Comp. Biochem. Physiol. Part A Mol. Integr. Physiol.202112–122. 10.1016/j.cbpa.2016.05.002
136
SangaliS.BrandelliA. (2000). Feather keratin hydrolysis by a Vibrio sp. strain kr2.J. Appl. Microbiol.89735–743. 10.1046/j.1365-2672.2000.01173.x
137
SanghviG.PatelH.VaishnavD.OzaT.DaveG.KunjadiaP.et al (2016). A novel alkaline keratinase from Bacillus subtilis DP1 with potential utility in cosmetic formulation.Int. J. Biol. Macromol.87256–262. 10.1016/j.ijbiomac.2016.02.067
138
SapkotaA. R.LeffertsL. Y.McKenzieS.WalkerP. (2007). What do we feed to food-production animals? A review of animal feed ingredients and their potential impacts on human health.Environ. Health Perspect.115663–670. 10.1289/ehp.9760
139
SchommerV. A.WenzelB. M.DaroitD. J. (2020). Anaerobic co-digestion of swine manure and chicken feathers: Effects of manure maturation and microbial pretreatment of feathers on methane production.Renew. Energy1521284–1291. 10.1016/j.renene.2020.01.154
140
SchrooyenP. M.DijkstraP. J.OberthürR. C.BantjesA.FeijenJ. (2001). Partially carboxymethylated feather keratins. 2. Thermal and mechanical properties of films.J. Agric. Food Chem.49221–230. 10.1021/jf0004154
141
SelvamK.VishnupriyaB. (2012). Biochemical and molecular characterisation of microbial keratinase and its remarkable applications.Int. J. Pharm. Biol. Arch.3267–275.
142
SharmaM.SharmaM.RaoV. M. (2011). In vitro biodegradation of keratin by dermatophytes and some soil keratinophiles.Afr. J. Biochem. Res.51–6. 10.15373/2249555x/august2014/189
143
SilotoR. M.WeselakeR. J. (2012). Site saturation mutagenesis: Methods and applications in protein engineering.Biocatal. Agric. Biotechnol.1181–189. 10.1016/j.bcab.2012.03.010
144
SousaM.SouzaO.MacielM.CruzR.RêgoM. G.MagalhãesO.et al (2015). Keratinolytic potential of fungi isolated from soil preserved at the Micoteca URM.Eur. J. Biotechnol. Biosci.310–15.
145
SrivastavaB.KhatriM.SinghG.AryaS. K. (2020). Microbial keratinases: An overview of biochemical characterization and its eco-friendly approach for industrial applications.J. Clean. Prod.252:119847. 10.1016/j.jclepro.2019.119847
146
StiborovaH.BranskaB.VeselaT.LoveckaP.StranskaM.HajslovaJ.et al (2016). Transformation of raw feather waste into digestible peptides and amino acids.J. Chem. Technol. Biotechnol.911629–1637. 10.1002/jctb.4912
147
SuC.GongJ. S.ZhangR. X.TaoL. Y.DouW. F.ZhangD. D.et al (2017). A novel alkaline surfactant-stable keratinase with superior feather-degrading potential based on library screening strategy.Int. J. Biol. Macromol.95404–411. 10.1016/j.ijbiomac.2016.11.045
148
SuntornsukW.TongjunJ.OnnimP.OyamaH.RatanakanokchaiK.KusamranT.et al (2005). Purification and characterisation of keratinase from a thermotolerant feather-degrading bacterium.World J. Microbiol. Biotechnol.21:1111. 10.1007/s11274-005-0078-x
149
TakagiH.MorinagaY.IkemuraH.InouyeM. (1988). Mutant subtilisin E with enhanced protease activity obtained by site-directed mutagenesis.J. Biol. Chem.26319592–19596.
150
TakenakaS.MiyatakeA.TanakaK.KuntiyaA.TechapunC.LeksawasdiN.et al (2015). Characterisation of the native form and the carboxy-terminally truncated halotolerant form of α-amylases from Bacillus subtilis strain FP-133.J. Basic Microbiol.55780–789. 10.1002/jobm.201400813
151
TamreihaoK.MukherjeeS.KhunjamayumR.DeviL. J.AsemR. S.NingthoujamD. S. (2019). Feather degradation by keratinolytic bacteria and biofertilizing potential for sustainable agricultural production.J. Basic Microbiol.594–13. 10.1002/jobm.201800434
152
TatineniR.DoddapaneniK. K.PotumarthiR. C.VellankiR. N.KandathilM. T.KolliN.et al (2008). Purification and characterisation of an alkaline keratinase from Streptomyces sp.Bioresour. Technol.991596–1602. 10.1016/j.biortech.2007.04.019
153
TesfayeT.SitholeB.RamjugernathD.ChunilallV. (2017). Valorisation of chicken feathers: Characterisation of physical properties and morphological structure.J. Clean Prod.149349–365. 10.1016/j.jclepro.2017.02.112
154
ThankaswamyS. R.SundaramoorthyS.PalanivelS.RamuduK. N. (2018). Improved microbial degradation of animal hair waste from leather industry using Brevibacterium luteolum (MTCC 5982).J. Clean. Prod.189701–708. 10.1016/j.jclepro.2018.04.095
155
ThysR. C. S.BrandelliA. (2006). Purification and properties of a keratinolytic metalloprotease from Microbacterium sp.J. Appl. Microbiol.1011259–1268. 10.1111/j.1365-2672.2006.03050.x
156
TianJ.XuZ.LongX.TianY.ShiB. (2019). High-expression keratinase by Bacillus subtilis SCK6 for enzymatic dehairing of goatskins.Int. J. Biol. Macromol.135119–126. 10.1016/j.ijbiomac.2019.05.131
157
TiwaryE.GuptaR. (2010). Medium optimisation for a novel 58 kDa dimeric keratinase from Bacillus licheniformis ER-15: biochemical characterisation and application in feather degradation and dehairing of hides.Bioresour. Technol.1016103–6110. 10.1016/j.biortech.2010.02.090
158
TiwaryE.GuptaR. (2012). Rapid conversion of chicken feather to feather meal using dimeric keratinase from Bacillus licheniformis ER-15.J. Bioprocess. Biotech.21–5.
159
ToivolaD. M.BoorP.AlamC.StrnadP. (2015). Keratins in health and disease.Curr. Opin. Cell Biol.3273–81. 10.1016/j.ceb.2014.12.008
160
TsiroulnikovK.RezaiH.Bonch-OsmolovskayaE.NedkovP.GousterovaA.CueffV.et al (2004). Hydrolysis of the amyloid prion protein and nonpathogenic meat and bone meal by anaerobic thermophilic prokaryotes and Streptomyces subspecies.J. Agric. Food Chem.526353–6360. 10.1021/jf0493324
161
ul HaqI.AkramF. (2018). Striking applications of keratinase enzyme isolated from various natural sources: a review.Proc. Pakistan Acad. Sci B Life Environ. Sci.551–17.
162
Vasileva-TonkovaE.GousterovaA.NeshevG. (2009). Ecologically safe method for improved feather wastes biodegradation.Int. Biodeterior. Biodegradation631008–1012. 10.1016/j.ibiod.2009.07.003
163
VermaA.SinghH.AnwarM. S.KumarS.AnsariM. W.AgrawalS. (2016). Production of thermostable organic solvent tolerant keratinolytic protease from Thermoactinomyces sp. RM4: IAA production and plant growth promotion.Front. Microbiol.7:1189. 10.3389/fmicb.2016.01189
164
VermaA.SinghH.AnwarS.ChattopadhyayA.TiwariK. K.KaurS.et al (2017). Microbial keratinases: industrial enzymes with waste management potential.Crit. Rev. Biotechnol.37476–491. 10.1080/07388551.2016.1185388
165
VidmarB.VodovnikM. (2018). Microbial keratinases: enzymes with promising biotechnological applications.Food Technol. Biotechnol.56312–328.
166
VillaA. L. V.AragãoM. R. S.dos SantosE. P.MazottoA. M.ZingaliR. B.de SouzaE. P.et al (2013). Feather keratin hydrolysates obtained from microbial keratinases: effect on hair fiber.BMC Biotechnol.13:15. 10.1186/1472-6750-13-15
167
VojcicL.PitzlerC.KoerferG.JakobF.MartinezR.MaurerK. H.et al (2015). Advances in protease engineering for laundry detergents.New Biotechnol.32629–634. 10.1016/j.nbt.2014.12.010
168
WangB.YangW.McKittrickJ.MeyersM. A. (2016). Keratin: Structure, mechanical properties, occurrence in biological organisms, and efforts at bioinspiration.Prog. Mater. Sci.76229–318. 10.1016/j.pmatsci.2015.06.001
169
WangF.ZiemanA.CoulombeP. A. (2016). Skin keratins.Methods Enzymol.568303–350.
170
WangJ. J.GarlichJ. D.ShihJ. C. H. (2006). Beneficial effects of versazyme, a keratinase feed additive, on body weight, feed conversion, and breast yield of broiler chickens.J. Appl. Poult. Res.15544–550. 10.1093/japr/15.4.544
171
WellsJ. A.CunninghamB. C.GraycarT. P.EstellD. A. (1987). Recruitment of substrate-specificity properties from one enzyme into a related one by protein engineering.Proc. Natl. Acad. Sci. U.S.A.845167–5171. 10.1073/pnas.84.15.5167
172
WilliamsC. M.LeeC. G.GarlichJ. D.ShihJ. C. (1991). Evaluation of a bacterial feather fermentation product, feather-lysate, as a feed protein.Poult. Sci.7085–94. 10.3382/ps.0700085
173
WilliamsC. M.RichterC. S.MackenzieJ. M.ShihJ. C. (1990). Isolation, identification, and characterisation of a feather-degrading bacterium.Appl. Environ. Microbiol.561509–1515. 10.1128/aem.56.6.1509-1515.1990
174
WuW. L.ChenM. Y.TuI. F.LinY. C.EswarKumarN.ChenM. Y.et al (2017). The discovery of novel heat-stable keratinases from Meiothermus taiwanensis WR-220 and other extremophiles.Sci. Rep.71–12. 10.1007/s00792-009-0281-z
175
XiaY.MasséD. I.McAllisterT. A.BeaulieuC.UngerfeldE. (2012). Anaerobic digestion of chicken feather with swine manure or slaughterhouse sludge for biogas production.Waste Manage.32404–409. 10.1016/j.wasman.2011.10.024
176
YamamuraS.MoritaY.HasanQ.YokoyamaK.TamiyaE. (2002). Keratin degradation: a cooperative action of two enzymes from Stenotrophomonas sp.Biochem. Biophys. Res. Commun.2941138–1143. 10.1016/s0006-291x(02)00580-6
177
YanB. Q.ChenX. L.HouX. Y.HeH.ZhouB. C.ZhangY. Z. (2009). Molecular analysis of the gene encoding a cold-adapted halophilic subtilase from deep-sea psychrotolerant bacterium Pseudoalteromonas sp. SM9913: cloning, expression, characterisation and function analysis of the C-terminal PPC domains.Extremophiles13725–733. 10.1007/s00792-009-0263-1
178
YangH.LiJ.DuG.LiuL. (2017). “Microbial production and molecular engineering of industrial enzymes: challenges and strategies,” in Biotechnology of Microbial Enzymes, ed.BrahmachariG. (Cambridge, MA: Academic Press), 151–165. 10.1016/b978-0-12-803725-6.00006-6
179
ZhangR. X.GongJ. S.SuC.ZhangD. D.TianH.DouW. F.et al (2016). Biochemical characterisation of a novel surfactant-stable serine keratinase with no collagenase activity from Brevibacillus parabrevis CGMCC 10798.Int. J. Biol. Macromol.93843–851. 10.1016/j.ijbiomac.2016.09.063
180
ZhangX. (2012). Applying the mutation of Bacillus subtilis and the optimisation of feather fermentation medium to improve Keratinase activity.Adv. Biol. Chem.2:6. 10.4236/abc.2012.21008
181
ZhangZ.LiD.ZhangX. (2019). Enzymatic decolorization of melanoidins from molasses wastewater by immobilized keratinase.Bioresour. Technol.280165–172. 10.1016/j.biortech.2019.02.049
182
ZhaoH. Y.FengH. (2018). Engineering Bacillus pumilus alkaline serine protease to increase its low-temperature proteolytic activity by directed evolution.BMC Biotechnol.18:34. 10.1186/s12896-018-0451-0
Summary
Keywords
microbial keratinase, valorization, keratin-rich wastes, biodegradation, amino acids, enzyme technology
Citation
Nnolim NE, Udenigwe CC, Okoh AI and Nwodo UU (2020) Microbial Keratinase: Next Generation Green Catalyst and Prospective Applications. Front. Microbiol. 11:580164. doi: 10.3389/fmicb.2020.580164
Received
04 July 2020
Accepted
30 November 2020
Published
18 December 2020
Volume
11 - 2020
Edited by
Pankaj Kumar Arora, Babasaheb Bhimrao Ambedkar University, India
Reviewed by
Santosh Kr. Karn, Sardar Bhagwan Singh Post Graduate Institute of Biomedical Science & Research, India; Gaurav Saxena, Jawaharlal Nehru University, India
Updates

Check for updates
Copyright
© 2020 Nnolim, Udenigwe, Okoh and Nwodo.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Uchechukwu U. Nwodo, UNwodo@ufh.ac.za
This article was submitted to Microbiotechnology, a section of the journal Frontiers in Microbiology
Disclaimer
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.