2. Protein-Based Biostimulants
2.1. Production
Protein-based biostimulants are basically mixtures of peptides and amino acids
[2][20]. Most PBB products are derived from protein-rich substances (plant or animal origins) that have been enzymatically or chemically treated or subjected to thermal hydrolysis. The products are, therefore, often referred to as protein hydrolysates (PHs)
[2][3][11][21]. They contain peptides and free essential and non-essential amino acids present in different quantities, depending on the protein source, processing methods utilized and degree of hydrolysis
[2][13] (
Figure 1). The active ingredients (peptides and amino acids) in the PHs, contribute to an increased uptake of beneficial elements into plant tissues via the leaves or roots
[3][11]. Currently, more than 90% of commercially available PHs are derived from chemical hydrolysis of animal proteins, e.g., collagen, fish by-products, blood meal, chicken feathers, etc.
[20][22]. Commercially available animal-derived PH products include Siapton
[3], Pepton
[23], and Hydrostim
[24]. However, there are restrictions on the use of PBBs derived from animal by-products in the European Union (EU), where animal-derived products can only be used as raw material for biostimulants at the endpoint of the manufacturing chain, and with a particular focus on the safety of humans, animals, and the environment
[25]. Under current EU regulations, biostimulants from animal-derived products may also not be applied directly to edible plant parts and the maximum concentration of heavy metals must be non-detectable
[25]. Sweden, as an EU country, is following EU regulations. Commercial plant-derived PHs, e.g., Coveron
[26] and Trainer
[21], are also available in different forms (liquid, water-soluble powder, granules) and can be applied as foliar spray, seed, root, or soil treatments
[11][22]. However, plant biostimulants are a recently emerging field of research with an increasing number of publications from 2015 and onwards
[5] and the research on PBBs and PHs is keeping track of that development
[2][3][4]. As an increasing number of commercial plant- and animal protein-based biostimulants will enter the market as a result of the increasing research activities, additional regulations on the use of the products are expected.
Figure 1. Possible active ingredients in protein-based biostimulants (PBBs). Compounds in white and black are large molecules, while active ingredients in colored hexagons are low molecular weight components of proteins
[27].
2.2. Effects of PBBs on Soil and on Agronomic, Physiological, and Molecular Plant Parameters
Research on PBBs and their commercial use in agricultural and horticultural applications are of a rather recent origin, with most development having taken place during the past two decades
[11]. Most of the PBBs evaluated to date have been shown to have a broad-spectrum effect on the biochemical properties and microbial community of the soil. They have also been found to have a significant effect on plant growth and health, as summarized in
Table 1. As a result, PBBs have been used in soil bioremediation activities, for soil restoration, and for preventing soil erosion
[28]. Studies have indicated that a high nitrogen content (>50%) and a high percentage (>60%) of peptides with low molecular weight (<3 kDa) are beneficial in PBBs used as an amendment to semi-arid soil
[28].
Furthermore, PBBs have a positive impact on the metabolic processes of plants, as they enhance root and shoot growth, photosynthesis rate, and crop quality
[3][12][22][29][30]. PBBs are reported to regulate biochemical processes that boost the tolerance of crops against abiotic stresses (drought, salinity, and heavy metals)
[12]. They have also been found to stimulate nutrient uptake and nutrient use efficiency in crops, largely due to their growth-enhancing effects on roots
[12]. In addition, PBBs can have indirect effects on plants by enhancing uptake and efficient use of macro- and micronutrients
[12][30]. Most biostimulating effects have been linked to the presence of soluble peptides and free amino acids in PHs, which in many cases, act as precursors for the biosynthesis of phytohormones (plant-growth regulators) and other metabolically important bioactive compounds which then contribute to the plant-growth enhancement
[3][8][22]. These soluble peptides and free amino acids are easily absorbed by soil microorganisms, which helps to improve soil structure, soil organic matter content, and nutrient availability
[28].
Enhanced shoot and root growth have been reported, e.g., in kiwi and snapdragon plants to which PBBs were applied at a low dosage
[26][31][32]. Increased coleoptile length in maize has been reported, although a relatively high concentration of PBBs was needed to obtain that effect
[11]. Soy PBB incorporated into broccoli seed pellets has been found to enhance plant height
[6]. Similarly, enhanced plant height and plant canopy area have been obtained in maize
[33] and tomato
[34] through the use of PBBs. Moreover, the use of PBBs has been found to enhance the biomass production of broccoli, maize, lettuce
[6][30][35], banana, and rocket
[36][37]. In one study, plant height and total biomass of hibiscus plants were increased by applying PBBs from two urban biowaste materials
[38].
In addition to the effect on plant growth, PBBs have been found to be involved in several molecular and physiological processes in plants
[12]. For example, the nitrogen content in maize and cucumber plants has been found to be increased by treatment with plant-derived PHs and hydrolyzed collagen, respectively
[39][40]. Furthermore, PBB treatment of maize has been shown to induce the secretion of enzymes involved in carbon and nitrogen metabolism
[33][41].
Several studies have demonstrated that PBBs can improve crop tolerance to abiotic stresses
[22], e.g., calcium protein hydrolysate has been found to reduce chloride uptake in Oriental persimmon (
Diospyros kaki L.)
[42]. Furthermore, gelatin-treated cucumber plants have been shown to exhibit higher salinity tolerance than untreated plants
[43], while the foliar application of PH to lettuce can enhance the tolerance to low temperatures
[44]. Paul et al.
[45] observed an increased growth in tomatoes treated with PHs under drought stress. Others have observed a reduction in anti-nutritional content (nitrate) in leaves of lettuce treated with PH (both foliar and root application) compared with untreated plants
[46]. The ability of plants to tolerate abiotic stresses following PH treatment has been attributed to genes being induced that contribute to enhanced growth, improved nutrient status, greater cell structure stability, osmolite and antioxidant accumulation, and enzyme activation by PHs
[22].
Generally, the effect of PBBs depends on the source and characteristics of the PBB, the crop (species and cultivars) on which the PBB is utilized, the age or growth stage of the crop, growing conditions, PBB concentration, timing and mode of application (soil, seed, or foliar treatment), PBB solubility, and leaf permeability
[22].
There have only been a few comparative studies on the efficiency of PBBs and other categories of biostimulants and chemical fertilizers
[47][48][49][50]. One major principle of biostimulants is that they help to reduce the quantity of fertilizer required, rather than replacing chemical fertilizers
[51]. Dudas
[47] achieved enhanced growth and biochemical concentrations in lettuce by using biostimulants and fertilizer, compared with an untreated control. The specific effects of PBBs and other categories of biostimulants are largely based on the different bioactive components present in their molecules
[49][50][52]. These specific effects include the enhancement of antioxidant content, antibiotic effect, abiotic tolerance, etc.
[20]. The comparative efficiency of different categories of biostimulants in relation to chemical fertilizers can be established using different omics approaches
[53].
Table 1. Reported effect on crop performance of different protein hydrolysates (PHs) used as protein-based biostimulants (PBBs).
2.3. Social, Economic, and Environmental Aspects of PBBs
Through their direct and indirect effects on crop yield and quality, nutrient-use efficiency, and tolerance to biotic and abiotic stresses, PBBs have the potential to contribute to socioeconomic development
[54][55][56]. First, the production and use of protein-rich side-streams from agro-industries create novel jobs and novel products, which in turn provide novel income opportunities
[54]. The sustainable use of more side-streams from agro-industries contributes to (i) social development in societies involved in the business, (ii) economic development and growth through product development, and (iii) environmental benefits from more complete use of natural resources
[56]. Farm income is increased due to increases in crop yield and quality resulting from use of PBBs
[56][57]. Economic benefits from the use of plant-based biostimulants, due to the increase in the yield have been reported for a range of crops, including perennial wall rocket and lamb’s lettuce
[58][59]. However, the economic return of using plant side-streams for additional products is always decreasing as soon as an extra harvesting or processing step is introduced into their production
[57]. Thus, a benefit of using PBBs from side streams of the food industry (e.g., wheat gluten or potato protein) is that these substances are readily available at a reasonable price from the industry
[14]. Furthermore, the use of PBBs may lead to the production of healthier crops and more nutritious food, which will enhance the health of consumers
[56]. PBBs might improve land-use efficiency by enhancing crop yield, quality, and profitability per acre
[60].
The economic efficiency of various types of biostimulants has been limitedly evaluated. Most studies report a certain increase in crop yield or plant development, often given in % of increase as related to a control treatment. For PBBs, the comparison of effects between different types or to other types of biostimulants, e.g., other biological, chemical or fertilizer compounds, is mainly lacking; although, a high effect has been reported in few studies
[61].
The use of PBBs may also lead to the production of healthier crops and more nutritious food, improving consumer health
[56]. Additionally, PBBs may improve land use efficiency by enhancing crop yield, quality, and profitability per acre
[58].
The use of biostimulants has been proven to have positive effects on the environment by improving the nutrient-use efficiency of crops, thereby reducing the quantities of agrochemicals needed in food production by up to 50%
[3][4]. PBBs also improve soil health, by boosting the communities of beneficial soil microorganisms present
[54] and by strengthening soil structure and increasing soil water-holding capacity, thus preventing soil erosion
[55]. The small quantity of biostimulants required for crop growth and development improvements means that there are no residues left in crops and soil
[2][37]. There is, thus, a limited risk of PBBs causing environmental problems in food, soil, or water bodies
[2][37][62][63][64][65][66]. The fact that most PBBs are highly biodegradable also results in the safety of life on land and in water
[3][9]. Thus, the use of PBBs could result in improved surface water quality and lower carbon emissions
[29].
The recycling and conversion of protein-rich wastes or side streams products from agriculture and agro-allied industries into PBBs, pave the way for a more resilient use of natural resources
[3][67][68][69][70][71]. The food industry is one of the major contributors to greenhouse gas emissions contributing to climate change, and the increased use of side streams from food production is seen as important to mitigate climate change
[68]. This leads to a strong focus in the plant biologicals industries to continue to develop novel natural active ingredients (biostimulants) from agro-industrial wastes
[70].
3. Hydrolyzed Wheat Gluten (HWG) and Potato Protein (PP) as Possible PBBs
3.1. Hydrolyzed Wheat Gluten (HWG)
Wheat gluten is defined as the rubbery mass of proteins, obtained when wheat flour is washed with water to remove starch and other water-soluble components
[72][73][74]. Wheat gluten is available in large quantities and at low cost as a result of large-scale industrial starch extraction from wheat flour
[71][72][73][74][75][76][77][78][79][80]. Some industrially produced gluten is used as a co-product for several purposes, e.g., within the baking industry
[78]. However, the quantities of wheat gluten produced leave much scope for additional uses
[72][81][82][83]. To increase the applicability of wheat gluten, structural modification to enhance its functional properties is often required
[71][72], as it is highly polymerized in its native state
[14][74][77][81]. The most common way to modify its structure is by enzymatic or thermal treatment or chemical hydrolysis, or a combination of these processes
[71][72][78].
Like many other plant PHs, HWG has a wide set of applications in the food industry, particularly as an ingredient since it resembles glutamate in terms of taste
[71][78]. As HWG is a hydrolyzed protein-rich co-stream from starch production, it most likely (based on the above discussion) has properties that make it suitable as a biostimulant within agriculture and horticulture
[72]. However, to the knowledge, HWG has, until now, not been evaluated as a source to be used in agricultural applications. Similar to other PHs (biostimulants), the hydrolysis of wheat gluten results in a breakdown of the protein into peptides and a large amount of free amino acids, which are beneficial for plant growth and health
[71][76][77][78][79][80].
3.2. Potato Protein (PP)
Potato fruit juice (PFJ) is a massive protein-rich side-stream generated in starch extraction from potatoes
[14]. In 2018, the amount of PFJ obtained after starch extraction represented around ~1% (3.5 million tons) of the total global potato production (>360 million tons)
[81][84][85]. In the past, PFJ was regarded as waste and was released into nearby streams and other water bodies, resulting in environmental pollution
[82][83]. However, potato protein (PP) is a potentially valuable product that can be produced from PFJ through acidification and harsh thermal processing
[14][86]. These processes result in intensive coagulation and protein recovery
[14][82]. In theory, a total of 200,000 tons of PP could be generated from the 3.5 million tons of PFJ made available annually worldwide
[73][79]. Some studies have indicated that PP is one of the largest under-utilized agro-industrial protein-rich side-streams in the world
[14]. PP has the potential to act as a ready source of organic nitrogen for crops, as the protein content of PP is >80%
[14]. A sustainable way of using PP would be through its application as a PBB. PP has been limitedly evaluated for its use in agriculture, although, trials to use it as a functional food component are ongoing
[87][88].