Abstract
Nanobiotechnology involves the use of nanotechnology integrated with biology. It is an emergent field of research that holds vivid applications in agriculture sector and food industry. In agriculture, nanofertilizers are helping to enhance plant growth by providing smart nourishment. Nanopesticides (control pests), nanoinsecticides (against insects), nanofungicides, and nanoherbicides (control weeds in the field) are the output of advanced nanobiotechnological research. Nanoparticles are also used in seed science to enhance seed germination. The technological breakthough in nanotechnology was achieved after the development of nanosensors. Nanobiosensors are available for detecting phytopathogens and pesticide residues. In food sectors, nanoparticles are utilized in food processing and packaging. Besides this, nanoadditives, nutraceutical delivery agents, and nanoencapsulation devices find multiple applications in several fields. Nanoparticles have been effectively used in the food packaging to enhance storage period and decrease pathogenic growth on stored food. Nanobiosensors are utilized to detect the contamination of foodborne pathogens, toxic substance, and pesticide detection in food. Despite a lot of advantages of nanobiotechnology, the environmental toxicity of nanoparticles is a matter of concern that requires risk assessment of nanoparticles on human health and environmental effects.
Access provided by Autonomous University of Puebla. Download chapter PDF
Similar content being viewed by others
Keywords
6.1 Introduction
Nanobiotechnology integrates nanotechnology with biology. Nanobiotechnology is a new, emergent, and interdisciplinary field of research that refers to the use of nanotechnology to modify living organisms to enable the combinations of biological and nonbiological materials. The word “nano” refers to scale between 1 and 100 nm, and the term nanobiotechnology was coined by Lynn W. Jelinski, a biophysicist from Cornell University, USA. Nanobiotechnology finds application in genetic engineering and breeding programs (Scrinis and Lyons 2007). Variety of materials are used to synthesize nanoparticles (NPs) such as metal oxides, silicates, magnetic materials, semiconductor quantum dots (QDs), lipids, polymers, and emulsions (Niemeyer and Doz 2001; Oskam 2006; Puoci et al. 2008; Prasad et al. 2017a).
The use of nanobiotechnology is relevant in the current perspective because the widespread use of chemical pesticides and fertilizers has contaminated the environment, is hazardous for human health, and affects the biodiversity. To combat the problem, several nanotechnology-based products such as nanofertilizers, nanoherbicides, nanopesticides, nanosensors, nanofungicides and nanoinsecticides enhanced seed germination, and genetically modified crops are being developed (Jampilek and Kralova 2015; Bhattacharyya et al. 2016; Prasad et al. 2014, 2017a).
Nanotechnology holds great potential to increase global food production and food quality. Important areas of nanotechnology application in the food sector are food processing, food packaging (active, antimicrobial and smart packaging), nano-additives, nanoencapsulation, nanosensors for contamination detection in food, and controlled release of nutraceuticals (Chellaram et al. 2014; Prasad et al. 2017b).
6.2 Application of Nanobiotechnology in Agriculture
Conventional agriculture uses agrochemicals, such as fertilizers, pesticides, fungicides, insecticides, and herbicides for crop growth and protection. However, their overuse is damaging the ecosystem by adding toxins in ground and surface water (Mukhopadhyay 2014). However, nanobiotechnology holds to promise to solve the agricultural problems and to restrict chemical overuse (Fig. 6.1). The applications of nanobiotechnology are described in this chapter (Table 6.1).
6.2.1 Nanofertilizers
Fertilizers are chemical compounds that provide nutrients to plant (Bottoms and Emerson 2013). Chemical fertilizers are in use since the early 1950s and have become the synonym of fertilzers. However, excessive use of chemical fertilizers has rattled the problem of water contamination, decreased soil fertility and initiated eutrophication. Nanofertilizers hold the promise to alleviate the environmental problems caused by the use of chemical fertilizers. Nanofertilizers can improve plant growth as they contain nutrients and growth-promoting substances encapsulated in nanopolymers, chelates or emulsions. Nanofertilizers enjoy environmental and other benefits like less contamination of water bodies, reduced soil toxicity, delayed and steady nutrient release, increased production yield, improved photosynthesis, enhanced fertilizer effect period, and increased soil nutrients (Naderi and Danesh-Shahkari 2013; Mehrazar et al. 2015).
Several examples of successful application of metal-based nanofertilizers for improved plant growth are available in the scientific literature. For example, iron-chelated nanofertilizer application on two varieties of spinach, Varamin 88 and Viroflayand, respectively at 4 kg ha−1 showed 58% and 47% improvement in wet weight along with enhanced leaf surface index and aerial organs (Moghadam et al. 2012). In addition, the EDTA-coated Fe3O4 NPs increased iron content in sunflower (Shahrekizad et al. 2015). Similarly, iron pyrite NP treatment on spinach seeds improved plant growth and enhanced breakdown of starch in seeds (Srivastava et al. 2014). Iron oxide NPs improve peanut growth by augmenting the availability of iron (Rui et al. 2016). The Fe2O3 NP application increases the plant iron and protein content and reduces the frequency of chlorosis (Siva and Benita 2016). Copper (Cu) NP application increased the growth and yield of wheat cultivar Millat-2011 by enhancing leaf area, chlorophyll content, fresh and dry weight, and root dry weight (Hafeez et al. 2015).
Synthetic apatite NP application increases the soybean plant growth rate (32.6%) and seed yield (20.4%), respectively (Liu and Lal 2014). The nanozeourea fertilizer enhanced crude protein of maize plant growing in black soil by 26.1% and in red soils by 36.1%, which was higher than conventional urea fertilizer application (Manikandan and Subramanian 2016). The SiO2 nanofertilizer application increased growth and yield in cucumber through improved nitrogen and phosphorus content in the plant (Yassen et al. 2017).
Recently, the demand for chitosan NP has increased based on their role as nanofertilizer. Chitosan is a biodegradable and biocompatible polymer of randomly distributed β-(1 → 4)-linked D-glucosamine and N-acetyl-D-glucosamine units. Several examples show an impressive plant growth result due to chitosan NP application. Nanochitosan-NPK fertilizer increases the growth and production of wheat growing in sandy soil (Abdel-Aziz et al. 2016). Application of zinc-boron nanofertilizer, prepared by loading ZnSO4 on chitosan NP emulsion, on coffee leaves increased the level of Zn, N, and P uptake and improved chlorophyll content (Wang and Nguyen 2018). Chitosan–polymethacrylic acid (PMAA) NP application on pea plant increased starch accumulation in root tips. In addition, synthesis of proteins such as convicilin, vicilin, and legumin β was upregulated (Khalifa and Hasaneen 2018).
6.2.2 Nanoherbicides
Weeds are unwanted plants that reduce crop yield thus need timely removal from agricultural lands. Conventional herbicides kill weeds from the aboveground plant parts and do not remove tubers or roots that sprout another plant under favorable conditions (Ali et al. 2014). In addition, the absence of moisture in herbicides render them less effective in rainfed agriculture systems (Subramanian and Tarafdar 2011).
Nanoherbicides application could be an effective method to remove weeds (Fig. 6.2). The NP-based herbicide has several advantages over conventional herbicides such as increased water solubility, lower weed resistance, and decreased toxicity. NPs of poly(epsilon-caprolactone) containing the herbicide atrazine were tested on target (Brassica sp.) and nontarget (Zea mays) plants. Encapsulated herbicide did not harm a nontarget plant (Zea mays). The NPs increase the mobility of atrazine in the soil, resulting in increased herbicide effectiveness against Brassica sp. (Pereira et al. 2014). Chitosan/tripolyphosphate NP-based nanoherbicides are also under development. Chitosan/tripolyphosphate NPs loaded with paraquat herbicide are less toxic to crops and are safe in controlling weeds (Grillo et al. 2014). The 2000 g ha−1 application of atrazine-loaded nanocapsule effectively decreased the root and shoot growth in B. pilosa and reduced photosystem II activity (Sousa et al. 2018).
6.2.3 Nanopesticides
Plant pests are a major threat to crop production and require stringent control measures. The conventional methods for pest control employ several types of chemical pesticides, most of which are xenobiotic in nature. In addition, the excessive use of pesticides is causing adverse effects on organisms, environment, and nitrogen-fixing ability of plants (Ghormade et al. 2011; Elrahman and Mostafa 2015; Bhattacharyya et al. 2016).
NP-based pesticides enjoy several advantages over conventional pesticides. Nanosilica derived from the plant is effective in controlling the infection of nuclear polyhedrosis virus (BmNPV) of silkworm (Barik et al. 2008). Silica NPs used against Sitophilus oryzae provide 90% pest mortality (Debnath et al. 2011). In another study, 70–80-nm sized silica NP provided 100% mortality against Corcyra cephalonica (Vani and Brindhaa 2013). The Ag NPs, synthesized from aqueous leaf extracts of Euphorbia prostrate, demonstrated 100% mortality rate against Sitophilus oryzae L., a rice pest (Abduz Zahir et al. 2012). The Ag NPs synthesized from leaf extract of Euphorbia hirta provide protection against larvae and pupae of the cotton bollworm (Helicoverpa armigera). In addition, the longevity of male and female pest decreases after Ag NP treatment on larvae and pupae of the cotton bollworm (Durga Devi et al. 2014). The use of CuO NPs controls cotton leafworm larvae (Spodoptera littorals) with mortality of 100% (Shaker et al. 2016). The treatment of Bacillus thuringiensis-coated ZnO NPs delay the larval and pupal development period of Callosobruchus maculatus. The results show that Bt ZnO NPs are effective nanopesticide against C. maculatus (Malaikozhundan et al. 2017).
6.2.4 Nanoinsecticides
Insects are vectors of various plant diseases that damage crops and therefore require active control. Several chemical-based insecticides have been used to inhibit their reproduction or kill them (Ragaei and Sabry 2014). However, chemical-based insecticides suffer from several drawbacks as they are degraded by light, temperature, microorganism, and hydrolysis. Therefore, only a small quantity of these insecticides reaches the target site. As a result, repeated application of insecticides is necessary to control the insects, which increase the cost of crop production. In addition, the use of insecticides is known to damage ecosystems and human health (Perlatti et al. 2013).
To combat the practical problems associated with field application of chemical insecticide, several NP-based insecticides are being formulated and tested. For example, the ZnO NPs provide mortality rate of 91.6% against Trialeurodes vaporariorum (Greenhouse whitefly) (Khooshe-Bast et al. 2016). The use of biosilver and gold NPs affects the growth and decreases the body weight of Pericallia ricini larvae. Therefore, Ag and Au NPs could be used to control insects (Sahayaraj et al. 2016). The Ag and Zn NP application against Aphis nerii at 700 mg mL−1 provides the highest insect mortality rate (Rouhani et al. 2012). The Ag NP application on cotton leafworm (Spodoptera littoralis) provides more than 50% mortality of leafworms at 250 ppm and higher concentrations (El-Bendary and El-Helaly 2013). The nanoalumina dust, synthesized using a modified glycine-nitrate combustion process, displayed fair mortality rate against Sitophilus oryzae and Rhyzopertha dominica (pests of stored grain) (Buteler et al. 2015). The two SiO2 NPs, namely Aerosil® and Nanosav, provided high-mortality rate of Rhyzopertha dominica and Tribolium confusum (Ziaee and Ganji 2016).
6.2.5 Nanofungicides
Phytopathogens attack plant tissues at different stages of growth. Some fungal pathogens like Fusarium spp., Botrytis cinerea, and Phythophora spp. infect aerial and few infect ground plant parts, causing a huge loss in crop yield. Conventional methods for phytopathogen control involve chemical fungicide application, which is highly toxic and nonbiodegradable in nature, contaminates the environment, and affects human health. To counter the problems associated with chemical fertilizer application in the field, the development of nanomaterial-based eco-friendly fungicide is underway for agriculture sustainability and greener environment (Abd-Elsalam and Alghuthaymi 2015). For achieving the goal, several nanofungicides have been tested against many plant pests.
Inhibition of several fungal pathogens by Ag NPs indicates their antifungal properties (Kim et al. 2012). For example, silver-based NPs were found to be effective against 18 fungal species (Alternaria alternata, A. brassicicola, A. solani, Botrytis cinerea, Cladosporium cucumerinum, Corynespora cassiicola, Cylindrocarpon destructans, Didymella bryoniae, Fusarium oxysporum f. sp. Cucumerinum, F. oxysporum f. sp. lycopersici, F. solani, Fusarium sp., Glomerella cingulata, Monosporascus cannonballus, Pythium aphanidermatum, P. spinosum, and Stemphylium lycopersici). The Ag NPs were also found effective against Bipolaris sorokiniana infection in wheat (Mishra et al. 2014). The antifungal activity of Ag NPs was also found against Candida spp. (Kim et al. 2009; Panacek et al. 2009), Bipolaris sorokiniana, Magnaporthe grisea (Jo et al. 2009), and powdery mildews (Lamsal et al. 2011). In addition, Ag and Cu NPs, used against A. alternata and Botrytis cinerea, showed maximum inhibition of the fungal hyphae growth at the concentration of 15 mg L−1 of Ag and Cu NPs (Ouda 2014).
High-molecular-weight chitosan NPs show antifungal activity against F. solani and Aspergillus niger (Ing et al. 2012). Cu–chitosan NP application at 0.12% concentration against A. solani and F. oxysporum in tomato caused 70.5% and 73.5% inhibition of fungal mycelia and spore germination by 61.5% and 83.0%, respectively (Saharan et al. 2015). Cu NPs inhibit the activity of plant pathogenic fungi like Phoma destructive (DBT-66), Curvularia lunata (MTCC 2030), A. alternata (MTCC 6572), and F. oxysporum (MTCC 1755). Since Cu NP can be quickly and conveniently synthesized using C-TAB-IPA method, it holds potential to be used as a commercial fungicide (Kanhed et al. 2014).
The ZnO NP application against Botrytis cinerea and Penicillium expansum causes deformation in fungal hyphae and inhibition of B. cinerea growth. In addition, ZnO NPs inhibit the growth of conidiophores and conidia of P. expansum, leading to the death of fungal hyphae (He et al. 2011). The ZnO and magnesium oxide (MgO)-based NP application has been reported to reduce spore germination of Alternaria alternata, Fusarium oxysporum, Rhizopus stolonifer, and Mucor plumbeus (Wani and Shah 2012).
More recently, the NP combinations are under use for effective nanofungicide preparation. For example, the combination of 25% nano trifloxystrobin with 50% tebuconazole (75 WG) fungicide made through ball milling produced better antifungal activity in comparison to conventional fungicide against Macrophomina phaseolina (Kumar et al. 2016). The combination of chitosan (CS) and silver (Ag) (also abbreviated as Ag@CS NPs) displayed significant antifungal activity against Pyricularia oryzae, responsible for rice blast (Pham et al. 2018). The ZnO NP combination with ciprofloxacin and ceftazidime demonstrated antifungal property against A. alternata, A. niger, B. cinerea, F. oxysporum, and P. expansum. The maximum antifungal activity was achieved when 0.25 mg mL−1 ZnO NPs was combined with 8 μg mL−1 ciprofloxacin and 32 μg mL−1 ceftazidime (Jamdagni et al. 2018).
6.2.6 Seed Science: Enhancing Seed Germination
Seed yield is the most important factor in determining crop productivity. Usually, the laboratory-tested germination seeds are distributed to farmers for cropping. However, most of the times the provided seeds show viability rate below the claim. The NP-based methods are being developed to improve the seed germination of stored seeds (Manimaran 2015).
The NPs of C, Zn, Au, Ag, and Si have been claimed to improve seed germination of several plants. For example, the carbon nanotube application at 10–40 μg mL−1 solvent increases tomato seed germination (Khodakovskaya et al. 2009). The ZnO NP application enhances the germination rate in many plants (Singh et al. 2013). The ZnO NP application at 15 mg L−1 enhances rice seed germination (Upadhyaya et al. 2017).
The Au and Ag are the nanoparticles of choice for many reasons. Au NP application at 1000 μM increased the Gloriosa superba germination rate (Gopinath et al. 2014). The Ag NP treatment increased seed germination percentage rate of Boswellia ovalifoliolata by 95% (Savithramma et al. 2012). The Ag NP treatment at 50 mg L−1 on Pennisetum glaucum seeds shows the highest germination percentage (93.33%) (Parveen and Rao 2014).
The TiO2 NPs are preferred in plant sciences due to photocatalytic activity, stability, and lower costs. The 10 ppm nanosize TiO2 treatment decreases the mean germination time (34%) in spinach seeds by facilitating water absorption (Feizi et al. 2012). Anatase NP (TiO2) application at 40 mg mL−1 enhances the germination of parsley seeds (92.46%) (Dehkourdi and Mosavi 2013). TiO2 NPs applied at 2000 mg L−1 in canola plants have been reported to enhance seed germination (Mahmoodzadeh et al. 2013).
Nanosilicon dioxide (nSiO2) application at 8 g L−1 enhanced tomato seed germination percent (22.16%), germination meantime (3.98%), and seed germination index (22.15%) (Siddiqui and Al-Whaibi 2014). The SiO2 (10–20 nm) and Mo NP (>100 nm) application in rice seeds also shows better germination (Adhikari et al. 2013). The 200 ppm silica NPs were reported to enhance cucumber seed germination (Alsaeedi et al. 2018).
In a recent study, several metallic NPs were reported to enhance the germination percentage of a medicinal plant Artemisia absinthium. In the study, the germination percentage of 98.6% was achieved with Ag NPs followed by Cu NPs (69.6%) and Au NPs (56.5%), respectively (Hussain et al. 2017). In another study, binary mixtures of six metal oxide NPs (TiO2, Fe2O3, CuO, NiO, Co3O4, and ZnO) were used for evaluating seed germination in brassica. The 2–6% seed germination enhancement was achieved at 1000 and 2000 mg L−1 concentration of Ti, Co, and Fe metal oxide NPs. The CuO NP was found to be most toxic for brassica seed germination (Ko et al. 2017).
6.2.7 Nanobiosensors for Plant Pathogen Detection
Traditional microscopy-based and culture-dependent methods are available for detecting plant pathogens, which are time-consuming and often inaccurate (Fletcher et al. 2006). In addition, the immunological and molecular methods available for pathogen detection suffer from longer test time, weak signal strength, and bulky instrumentation (Kashyap et al. 2016). However, nanobiosensor application in plant pathology could provide a novel approach for detecting plant pathogens. The methods of pathogen detection are simple, rapid, and accurate (Sharon et al. 2010; Ismail et al. 2017). For example, fluorescent silica NPs, combined with antibody molecules were used to detect Xanthomonas axonopodis pv. vesicatoria that causes bacterial spot disease in Solanaceae family plants (Yao et al. 2009). Copper NP-modified gold electrode was used to detect oilseed rape infected with fungal pathogen Sclerotinia sclerotiorum (Wang et al. 2010). The TiO2 or SnO NPs were used for detecting p-ethylguaiacol present in fruits and plants infected with fungi Phytophthora cactorum (Fang et al. 2014). Quantum dots fret-based biosensor was used to detect Candidatus phytoplasma aurantifolia that causes witche’s broom disease of lime (Rad et al. 2012).
Nanobiosensors are also effective in detecting plant viral disease. The immunosensor shows high specificity and sensitivity for virus detection. For example, a chemiresistive sensor based on polypyrrole (PPy) nanoribbon was used to detect plant viruses (Chartuprayoon et al. 2013). Nanorod-based fiber-optic particle plasmon resonance immunosensor was utilized to detect orchid viruses (Cymbidium mosaic virus and Odontoglossum ringspot virus), which has several advantages such as faster analysis, good reproducibility, and lower detection limit than ELISA (Lin et al. 2014). A nanowire-based biosensor was developed for detecting plant diseases (Ariffin et al. 2014). Carbon nanotube-based Cu NPs are used to develop biosensor for detecting Begomovirus (CLCuKoV-Bur). The developed sensor detects viruses up to 0.01 ng μ L−1 DNA concentration (Tahira et al. 2018).
6.2.8 Nanobiosensors for Pesticide Residue Detection
Nowadays pesticides are in heavy use for crop improvement. When pesticides degrade in environment, some toxic residues are released in the soil which may enter into the food chain through contaminated water and soil. Henceforth, accurate pesticide detection methods are required to measure the soil and plant contamination status. Conventional methods of pesticide residue detection include mass spectrometry, GC, HPLC, and UV-Vis spectrometry. However, these methods require skilled technicians and are time-consuming, therefore, not suitable for field analysis. As a result, newer methods are required for accurate pesticide residue detection in crop fields. Several nanobiosensor-based methods are under development that are cheaper, fast and do not require sample pretreatment (Vimala et al. 2016). For example, an electrochemical magnetoimmunosensing method was developed for detecting atrazine residue in samples (Zacco et al. 2006). Nanocomposite ZrO2/Au film electrode is used for detecting parathion (Wang and Li 2008). Amperometric biosensor based on assembling acetylcholinesterase on poly(dimethylsiloxane)-poly(diallydimethylammonium)/gold NP composite film is used for detecting organophosphates (Zhao et al. 2009). The MnO2 nanosheet-carbon dots are used for detecting organophosphorus pesticides (Yan et al. 2018). An optical biosensor was developed for detecting organophosphate pesticide using CdTe as fluorescent probe (Sun et al. 2011). Core-shell nanosensors based on localized surface plasmon resonance (LSPR) were developed for detecting atrazine (Yang et al. 2014). Recently, a fluorescence sensor was synthesized by combining copper (II) oxide and multiwall carbon nanotubes for detecting glyphosate. The detection was based on catalytic inhibition activity of the copper (II) oxide and multiwall carbon nanotubes (Chang et al. 2016). Sahoo et al. (2018) used zinc oxide quantum dots for detecting aldrin, tetradifon, glyphosate, and atrazine in water.
6.2.9 Production of Genetically Modified Crops
Nanobiotechnology also finds application in gene modification. For example, mesoporous silica nanoparticle (MSN) was used to transport DNA and chemicals into plant cells and leaves (Torney et al. 2007). The MSNs were used as carriers to deliver Cre recombinase protein into Zea mays cells for genome editing (Martin-Ortigosa et al. 2014). A fluorescent-conjugated polymer NP (CPN) was used for delivering siRNAs to knockdown a target gene in the cellulose biosynthesis pathway (NtCesA-1a and NtCesA1b) in plant protoplasts (Silva et al. 2010). Calcium phosphate NPs were used to deliver pBI121 harboring GFP driven by 35S promoter-encoding plasmid DNA into tobacco (Ardekani et al. 2014).
6.3 Application of Nanobiotechnology in Food Industry
The application of nanobiotechnology in the food sector is a newer concept with immense potential. Nanobiotechnology use in food has improved its taste, color, and flavor. Its application has also enhanced absorption and bioavailability of nutrients as well as health supplements. New food packaging materials are being developed using nanobiotechnology with improved mechanical strength, oxygen barrier, and antimicrobial properties. Nanosensors are used for detecting microbial contamination and toxic substances in food. The major areas of nanobiotechnology application in food sectors include food processing, food packaging, nanoemulsions, nanoencapsulations, nanoadditives, and nutraceutical delivery (Singh et al. 2017) (Fig. 6.3).
6.3.1 Food Processing
Food processing is done to maintain the nutritional quality of the food and enhance its shelf life. As a result, processed foods are less likely to get spoiled than fresh foods. In addition, such foods can be easily transported to long distances. Nowadays, commercially marketed food is processed using enzyme immobilization nanofiltration and other methods (Dasgupta et al. 2015) to improve the shelf life. Some of the common nanobiotechnology methods used in food processing are described further.
6.3.1.1 Enzyme Immobilization
Some food processing methods employ enzymes to modify food components for improving flavor, texture, and nutritional quality. The latest methods employ enzymes that are immobilized using NPs for thorough dispersal around food matrices to increase enzyme activity (Thangavel 2014). For example, SiO2 NPs are used for triacylglycerol lipase immobilization in olive oil. The SiO2 NPs, with reactive aldehyde groups, covalently bind to a porcine triacylglycerol lipase and help in hydrolyzing olive oil. The enzyme immobilization also helps in improving stability, adaptability, and reusability of food products (Bai et al. 2006). Similarly, magnetite NPs are used to immobilize lipase (Lee et al. 2009). In addition, polyacrylonitrile (PAN) nanofibrous membranes were used for immobilizing Candida rugosa lipase for the hydrolysis of soybean oil (Li and Wu 2009).
6.3.1.2 Nanofrying
The US-based Oilfresh Corporation is marketing a new nanoceramic product with several proclaimed benefits. The benefit includes reduced use of oil in restaurants and in fast food due to the larger surface area of the product (Momin et al. 2013).
6.3.1.3 Nanofiltration
Nanofiltration is a cost-effective separation method for product separation that stands somewhere between reverse osmosis and ultrafiltration. It separates substances less than 10 Å and removes divalent and multivalent ions. Nanofiltration is commercially used for desalination of seawater, concentration of juices (Warczok et al. 2004), demineralization, and removal of color from water. The technology is also applicable in wastewater treatment, water purification, and cheese making (Hussain and Al-Rawajfeh 2009). For example, the commercial cottage cheese whey making suffers from acidity, dilution, and saltiness. Nanofiltration of cottage cheese whey effectively concentrates solids by removing sodium, potassium salts, and some acids (Nguyen et al. 2003). Another commercial example of nanofiltration is of lactic acid separation, which is an important product of the food industry that requires costly purification system. Lactic acid enrichment with inorganic nanofiltration and molecular sieving membranes by pervaporation was achieved at much lower costs than vacuum evaporation and electrodialysis (Duke et al. 2008).
6.3.1.4 Nanolamination
Food is spoiled by the accumulation of moisture, gases, and lipids, which can be protected through nanolamination. Nanolaminates are thin, harmless protective films synthesized from polysaccharides, proteins, and lipids. These are barrier against carbon dioxide and oxygen that preserves food, improves food texture, flavor, and color. In addition nanolaminations enhance the level of nutrients and antioxidants in the food (Ali et al. 2014). For example, lipid-based nanolaminates are good barriers against moisture, while polysaccharide- and protein-based films protect from oxygen- and carbon dioxide-based damage (Ravichandran 2010).
6.3.2 Food Packaging
The packaging increases the shelf life of food by reducing microbial spoilage, decreasing gas and moisture exchange. Many commercial NP-based food packaging products are available and discussed further.
6.3.2.1 Active Packaging
The NP-based active packaging provides antimicrobial, antioxidation, and moisture scavenging properties to the food items (Yildirim et al. 2017). The main action of active packaging NPs lies in the inhibition of the microbial growth that leads to the spoiling of food (Chellaram et al. 2014).
The chitosan films are used in food preservation due to antimicrobial and nontoxic properties (Tripathi et al. 2008). Nanoclay is used in the packaging of food, beer bottles, carbonated drinks, and thermoformed containers. The packaged nanoclay acts as a gas barrier that keeps oxygen-sensitive foods fresh for longer time spans. The polyethylene terephthalate (PET) beer bottles use nanoclays produced by Nanocor® which enhance beer storage time from 11 weeks to about 30 weeks (Silvestre et al. 2011). The Ag NPs combined with hydroxypropyl methylcellulose (HPMC) matrix provide antimicrobial property, which is internally coated on food packaging material (Moura et al. 2012). In addition, the ZnO NPs are also used in food packaging as they are safe and hold antimicrobial activity (Espitia et al. 2012). Also, allyl isothiocyanate (AIT) and carbon nanotubes (CNT) are utilized as antimicrobial film for the packaging of shredded and cooked chicken meat. The diffusion of the AIT from the film in the packaged chicken decreases the microbial contamination, which allows controlled oxidation and reduces color change (Dias et al. 2013). In another study, the antimicrobial activity of ZnO NP/CS film provided about 1.5- to two-fold increase in the antimicrobial activity against B. subtilis and E. coli (Priyadarshi and Negi 2016). Durethan is a transparent plastic film, which contains clay NPs that block oxygen, carbon dioxide, and moisture to keep the food fresh. The use of nanoclay in durethan preparation makes the plastic lighter, stronger, and heat resistant (Davari et al. 2017). The Ag NPs synthesized by crosslinking with trisodium citrate enhanced shelf life of the grapefruit. The Ag NPs filled with hydroxypropyl methylcellulose (HPMC) and xanthan films show good antibacterial activity with decreased decay index (Kothari and Setia 2017). A variety of NP-reinforced polymers termed as nanocomposites are used in the food packaging industry (Momin et al. 2013). For example, the composite of Ag and ZnO NPs enhances the shelf life of fresh juice (Emamifar et al. 2010).
Fruits and vegetables degrade faster after harvest due to ethylene production. Therefore, ethylene adsorbent powders are added in packaging to maintain the freshness of food and food products. Alkali-treated halloysite nanotubes have the highest ethylene adsorption capacity because the treatment increases the nanotube pore size (Gaikwad et al. 2018). Polyethylene nanocomposite films containing combinations of organoclay (OC) NP are also used in antimicrobial packaging of food that are effective against Escherichia coli (Fasihnia et al. 2017). Sarwar et al. (2017) found the antimicrobial activity of PVA/nanocellulose/Ag nanocomposite films against Staphylococcus aureus (MRSA) and E. coli (DH5-α). The developed film was nontoxic and possessed high thermal stability and high mechanical strength .
6.3.2.2 Biodegradable Packaging
The use of nondegradable plastics change the soil nature and causes the accumulation of toxic gases in the atmosphere, which is responsible for environmental pollution and global warming. To counter the problem associated with nondegradable plastics, the production of biodegradable plastics has been initiated. However, the biodegradable plastic production at a commercial level is a costly affair, and also they are permeable to water and gas permeable and lack mechanical strength.
The newer methods employ natural or synthetic NPs to rectify the defects of biodegradable plastics because NP-based bioplastics have advantages like biodegradability and higher mechanical strength (Chellaram et al. 2014). For example, biodegradable starch/clay nanocomposite films hold higher mechanical strength and are used in food packaging (Avella et al. 2005). In addition, the incorporation of NPs in bioplastics impart antimicrobial nature to them. For example, laser-generated Cu NPs embedded in a biodegradable polymer matrix (polylactic acid) equip them with antibacterial nature, for better food storage capability (Longano et al. 2012). A biodegradable material, poly(lactic acid) used in food packaging, provides higher mechanical strength and antimicrobial activity (Gonzalez and Igarzabal 2013). Also, specialized bioplastics are available for thermal-sensitive foods. For example, pectin-TiO2 nanocomposite aerogels are available for packaging thermosensitive food that lowers the thermal conductivity to food . The presence of TiO2 enhances thermal stability and provides antimicrobial activity under UV light and dark conditions (Nesi et al. 2018).
6.3.2.3 Smart Packaging
In smart packaging , the nanosensors are used for detecting microbial and biochemical changes and release of antimicrobials, antioxidants, and enzymes in food. The smart food spoilage detection is based on the concept that unpleasant odors are generated from food and drinks when contaminated with bacteria. A chemical sensor system called electronic nose senses the odor released from spoiled food (Casalinuovo et al. 2006). In a more specified example, Concina et al. (2009) used an electronic nose to detect the volatile compounds released from spoiled tomato. Electronic tongues, based on amperometric sensors, are also in use for food analysis (Scampicchio et al. 2008). In addition, surface-enhanced Raman scattering (SERS) sensors made up of a graphene and Ag nanocomposite was developed to detect the prohibited color additives in food (Xie et al. 2012).
6.3.3 Nanocoating
Wax coating is widely used for improving the shelf life of apples and cheeses. Coating delays senescence and protects the fruit from decay (Ghosh et al. 2017). The recent development of nanoscale edible coatings was made possible through nanotechnology. Edible coatings and films are used on various foods including fruits, vegetables, meats, cheese, and bakery products (Momin et al. 2013). Nanocomposite edible coating is used for increasing the shelf life of olive (Ghosh et al. 2017).
6.3.4 Nanoadditives
Nanoadditives such as vitamins, antimicrobials, antioxidants, and preservatives are used to enhance taste, absorption, and bioavailability of nutrients (Momin et al. 2013). For example, food additive nanoscale silica powder increases the shelf life and bioavailability of specific nutrients (Canham 2007). The NPs containing calcium show effective absorption properties (Jeon and Lee 2009). The TiO2 or E-171, a colored additive, produces a nontransparent white film that shows shielding against UV light (Latva-Nirva et al. 2009). The nanocrystalline powder of lycopene and resveratrol increases the absorption and bioavailability of nutrients in the body (Hsieh 2010). Nanoadditive, acyl ascorbates, synthesized through lipase condensation of ascorbic acid with fatty acids is used as antioxidant as it inhibits the oxidation of polyunsaturated fatty acid (Sharma and Pathak 2010). Aquasol preservative manufactured by AquaNova contains nanoscale micelle that increases absorption of nutritional additives and enhanced the preservation of food. Bioral™ omega-3 fatty acid nanocochleates, manufactured by BioDelivery Sciences International, is added to cakes, muffins, pasta, soups, cookies, cereals, chips, and confectionery. Synthetic lycopene, manufactured by BASF AG and DSM Nutritional Products Ltd., is an antioxidant and used in soft drinks, juices, breakfast cereals, instant soups, salad dressings, and yogurt (Kirdar 2015). Nisin-loaded chitosan-monomethyl fumaric acid (CM-N) NPs used as food additive show antibacterial activity against foodborne pathogens in orange juice (Khan et al. 2017).
6.3.5 Nanoencapsulation
Nanoencapsulation is the process to encapsulate substances at the nanoscale range (Lopez et al. 2006). The benefit of nanoencapsulation includes increased bioavailability of nutrients, preservation of the ingredients and additives during processing, removal of unpleasant tastes and flavors, and controlled release of additives (Chaudhry et al. 2010). Lipid-based nanoencapsulation systems such as nanoliposomes, archaeosomes, and nanocochleates can protect antioxidants from degradation and increase their solubility and bioavailability (Mozafari et al. 2006). Functional bread has been enriched with nanoencapsulated omega-3 fatty acids. Encapsulation decreased lipid oxidation during baking and reduces the formation of acrylamide and hydroxymethylfurfural (HMF) in bread (Gokmen et al. 2011). Donsi et al. (2011) used the high-pressure homogenization (HPH) method to prepare sunflower oil or oil-in-water nanoemulsions. A terpene and D-limonene mixture was encapsulated into sunflower oil or essential oil-in-water nanoemulsions. Encapsulation of terpenes and D-limonene inhibits the growth of microbes. Isolated lactoferrin from camel milk is encapsulated using calcium alginate. Calcium alginate nanocapsules help to control lactoferrin digestion (Raei et al. 2015).
Curcumin is a medically important compound produced by Curcuma longa plants. However, they are lipophilic in nature and unstable in gastrointestinal fluids. It has been shown that encapsulation of curcumin in nanoform enhances their antioxidant properties with increased absorption rate during digestion (Rao and Khanum 2016). In addition, nanoencapsulation could be used to encapsulate fish oils that deteriorate rapidly otherwise. As a result, nanoliposome system was developed to encapsulate fish oil (Ghorbanzade et al. 2017).
6.3.6 Nanoemulsions
The emulsion is a mixture of two immiscible liquid phases in which one phase disperses as droplets. Nanoemulsions consist of nanosize oil droplets of 10–100 nm. Nanoemulsions can be produced using high- and low-energy methods. A high-energy method uses mechanical devices (high-pressure valve homogenizers, microfluidizers, and sonication) to generate intense disruptive forces that breakdown the oil and water phases to form oil droplets. A low-energy method is based on the spontaneous formation of oil droplets within mixed oil-in-water emulsifier systems (Silva et al. 2012).
6.3.7 Nutraceutical Delivery
The major problem of the nutraceutical industry lies with the active components that poorly dissolve in oil or water, thus finding it difficult to reach target sites, thereby resulting in low bioavailability of nutrients (Putheti 2015). Nanobiotechnology employs a new strategy for the efficient delivery of nutraceuticals through nanoencapsulation. For example, nanoencapsulation of nutraceuticals is most commonly done using hydrophobins (Hyd), a small cysteine-rich amphipathic protein. The Hyd proteins bind to hydrophobic materials like vitamin D3 (VD3) with high affinity and protect the vitamin against degradation. The Hyd protein also acts as nanovehicle of hydrophobic nutraceuticals (Israeli-Lev et al. 2014). Dual nutraceutical nanohybrids consisting of folic acid and calcium were synthesized based on layered double hydroxide structure through exfoliation reassembly hybridization method. The report shows that the use of nutraceutical nanohybrids increases contents of essential nutrients in the human body (Kim and Oh 2016).
6.3.8 Nanobiosensor for Detection of Food Pathogen and Other Contaminants
Traditionally, the food pathogens are detected through microbial culture observation, PCR amplification, and immunology-based method (ELISA). Recently, many NP-based biosensor systems have been developed that are fast, inexpensive and require a little experience. Magnetic NPs coated with antibody (anti-AFM1) are used to separate the bound and unbound fractions of the component. Nanosensors successfully detect a minute change in the food color and gases released due to spoilage (Pradhan et al. 2015).
Biosensor-based methods involve detection of foodborne pathogen antibodies bound to NPs (Popov et al. 2010). An electronic tongue or nose consisting of an array of nanosensors was developed to detect the food spoilage through signals of gases released by food items (Garcia et al. 2006). Several cited examples have used nanosensors for pathogen detection. For example, nanobiosensors were used to detect food pathogens such as Staphylococcus spp., Bacillus spp., Clostridium spp., Shigella, and E. coli (Otles and Yalcin 2010). A gold NP-based biosensor with graphite-epoxy composite electrodes was used for the identification of Salmonella IS200 (Oliveira Marques et al. 2009). Streptavidin-coated magnetic NPs were used for detecting foodborne pathogens like Escherichia coli O157: H7, Salmonella enterica, Vibrio cholera, and Campylobacter jejuni (Song et al. 2013). Shelby et al. (2017) used magnetofluorescent nanosensor for detecting foodborne pathogen E. coli O157: H7. Piezoelectric biosensor based on an Au NP was used for detecting Escherichia coli O157: H7 in apple juice, milk, and ground beef. An Au/Si hetero-nanorod biosensor was used to detect Salmonella sp. based on the fluorescence (Fu et al. 2008). Electrically active polyaniline-coated magnetic (EAPM) NP-based biosensor was used to detect endospores of Bacillus anthracis in food samples (Pal and Alocilja 2009).
Nanosensors find huge application in toxin detection from various products. For example, an electrochemical immunosensor was used for detecting aflatoxin M1 (AFM1) in milk. The sensor was based on a competitive immunoassay in which the enzyme horseradish peroxidase (HRP) was used as a tag (Paniel et al. 2010). Optical biosensor based on competitive dispersion of gold nanorods (GNRs) detect aflatoxin B1 (AFB1) in food products (Xu et al. 2013). The Au NP-based aptasensor was used for detecting AFB1 in food samples (Hosseini et al. 2015). The use of Au NP in biosensor amplifies the signal frequency change due to the relatively large mass of the NPs (Chen et al. 2008). An optical carbon nanotube (CNT) immunosensor detects Staphylococcal enterotoxin B (SEB) in food. The deployment of CNT has lowered the detection limit of SEB and increased the immunosensor sensitivity at least sixfold (Yang et al. 2008).
Recently, the aptamer-based biosensors are under the course of development. Aptamers are single-stranded nucleic acids (DNA and RNA) or peptides that bind to the targeted molecules with high affinity and specificity (Song et al. 2012). In a classical example, luminescent assay, based on aptamer sensors, was used for detecting toxins in food (McKeague et al. 2011). In addition, aptamer-based nanosensors successfully detect acetamiprid pesticides in food (Verdian 2017). Besides aptamer biosensors, NP-based fluorescence resonance energy transfer methods are also used for detecting organophosphorus pesticides in food samples (Long et al. 2015).
6.4 Nanoparticles: Risks and Regulations
Besides various advantages of nanobiotechnology in the food industry, some safety issues are associated with the use of NPs. Several vivid nanotechnological application can impart accidental effects on plants and animals, thus need a thorough evaluation. NPs may accumulate within body organs and tissues due to smaller dimensions (Savolainen et al. 2010). Animals may inhale NPs into the lungs, resulting in severe disorders. The NPs may deposit on leaves and floral plant parts to create a toxic layer that prevents pollen tube penetration on stigma. They may also affect the translocation of water and minerals (Tarafdar 2015). Exposure of human endothelial cells with NPs could lead to cytotoxicity, genotoxicity, and dysfunction of nitric oxide signaling (Cao 2018). The NPs can enter the human body through the lungs, intestinal tract, and skin. Skin contact with toxic NPs and their inhalation are major risks in agriculture practices (Hoet et al. 2004). Inhaled NPs may reach the brain to cause neurodegeneration (Win-Shwe and Fujimaki 2011). Some studies reported the neurotoxic nature of NPs (Wu et al. 2013; Chin-Chan et al. 2015; Coccini et al. 2015; Migliore et al. 2015).
As a result, special regulations are required for NP preparation and application in agriculture and food industries (Amenta et al. 2015). In 2011, the guidance draft on risk assessment for nanotechnology use in food, feed applications, and pesticides was issued by the European Food Safety Authority (EFSA Scientific Committee). Environmental Protection Agency (EPA), USA, issued a proposal to use Sect. 6(a)(2) of the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) to obtain information on the use of nanomaterials in pesticide products and its potential effect on humans or the environment (EFSA Scientific Committee 2011). As a result, National Institute for Occupational Safety and Health (NIOSH), USA, issued warning against occupational exposure to carbon nanotubes and nanofibers during research and development (Howard 2013).
6.5 Conclusion
Nanobiotechnology involves the use of nanotechnology to modify living organisms and to enable the combination of biological and nonbiological materials. Nanobiotechnology has multiple applications in agriculture, food, and other sectors. The NP-based herbicides, pesticides, fertilizers, fungicides, and insecticides are needed for improving the crop productivity in an eco-friendly way. In seed science, nanotechnology is used to enhance seed germination. The role of nanobiosensors has also been proved useful in pathogen diagnosis, pesticide residue detection, and food contaminant determination. The nanobiotechnology application in food includes food processing (improving texture, color and shelf life), packaging (antimicrobial, oxygen and aroma scavenger), application of nanoadditives, nanoencapsulation, and controlled nutraceuticals delivery at the time of digestion. The NPs have been effectively used in developing food storage packaging materials that can decrease pathogenic growth of stored food. Nanobiosensors are also used to detect the contamination of foodborne pathogens, toxic substance, and pesticide in food. However, extensive studies are required to understand the NP-associated toxicity and involved mechanism to avoid application-based harmful effects on the environment and human health.
References
Abd-Elsalam KA, Alghuthaymi MA (2015) Nanobiofungicides: are they the next-generation of fungicides? J Nanotech Mater Sci 2:38–40
Abdel-Aziz HMM, Hasaneen MNA, Omer AM (2016) Nano chitosan-NPK fertilizer enhances the growth and productivity of wheat plants grown in sandy soil. Span J Agric Res 14:e0902. https://doi.org/10.5424/sjar/2016141-8205
Abduz Zahir A, Bagavan A, Kamaraj C, Elango G, Abdul Rahuman A (2012) Efficacy of plant-mediated synthesized silver nanoparticles against Sitophilus oryzae. J Biopest 5:95–102
Adhikari T, Kundu S, Rao AS (2013) Impact of SiO2 and Mo nanoparticles on seed germination of rice (Oryza sativa L.). Int J Agric Food Sci Technol 4:809–816
Ali MA, Rehman I, Iqbal A, Din S, Rao AQ, Latif A, Samiullah TR, Azam S, Husnain T (2014) Nanotechnology, a new frontier in agriculture. Adv Life Sci 1:129–138
Alsaeedi A, El-Ramady H, Alshaal T, El-Garawani M, Elhawat N, Al-Otaibi A (2018) Exogenous nanosilica improves germination and growth of cucumber by maintaining K+/na+ ratio under elevated na+ stress. Plant Physiol Biochem 125:164–171
Amenta V, Aschberger K, Arena M, Bouwmeester H, Moniz FB, Brandhoff P, Gottardo S, Marvin HJP, Mech A, Pesudo LQ, Rauscher H, Schoonjans R, Vettori MV, Weigel S, Peters RJ (2015) Regulatory aspects of nanotechnology in the Agri/feed/food sector in EU and non-EU countries. Regul Toxicol Pharmacol 73:463–476
Ariffin SAB, Adam T, Hashim U, Faridah S, Zamri I, Uda MNA (2014) Plant diseases detection using nanowire as biosensor transducer. Adv Mater Res 832:113–117
Ardekani MRS, Abdin MZ, Nasrullah N, Samim M (2014) Calcium phosphate nanoparticles a novel non-viral gene delivery system for genetic transformation of tobacco. International journal of pharmacy and pharmaceutical. Science 6:605–609
Avella M, De Vlieger JJ, Errico ME, Fischer S, Vacca P, Volpe MG (2005) Biodegradable starch/clay nanocomposite films for food packaging applications. Food Chem 93:467–474
Bai YX, Li YF, Yang Y, Yi LX (2006) Covalent immobilization of triacylglycerol lipase onto functionalized nanoscale SiO2 spheres. Process Biochem 41:770–777
Barik TK, Sahu B, Swain V (2008) Nanosilica – from medicine to pest control. Parasitol Res 103(2):253–258
Bhattacharyya A, Duraisamy P, Govindarajan M, Buhroo AA, Prasad R (2016) Nano-biofungicides: Emerging trend in insect pest control. In: Advances and Applications through Fungal Nanobiotechnology (ed. Prasad R), Springer International Publishing Switzerland 307–319
Bottoms M, Emerson SH (2013) Chemistry, fertilizer, and the environment. California Foundation for Agriculture in the Classroom pp 1–98
Buteler M, Sofie SW, Weaver DK, Driscoll D, Muretta J, Stadler T (2015) Development of nanoalumina dust as insecticide against Sitophilus oryzae and Rhyzopertha dominica. Int J Pest Manag 61:80–89
Canham LT (2007) Nanoscale semiconducting silicon as nutritional food additive. Nanotech 18:1–6
Cao Y (2018) The toxicity of nanoparticles to human endothelial cells. Adv Exp Med Biol 1048:59–69
Casalinuovo IA, Pierro DD, Coletta M, Francesco PD (2006) Application of electronic noses for disease diagnosis and food spoilage detection. Sensors 6:1428–1439
Chang Y, Lin Y, Xiao G, Chiu T, Hu C (2016) A highly selective and sensitive nanosensor for the detection of glyphosate. Talanta 161:94–98
Chartuprayoon N, Rheem Y, Ng JCK, Nam J, Chen W, Myung NV (2013) Polypyrrole nanoribbon based chemiresistive immunosensors for viral plant pathogen detection. Anal Methods 5:3497–3502
Chaudhry Q, Watkins R, Castle L (2010) Nanotechnologies in the food. In: Chaudhry Q, Castle L, Watkins R (eds) New opportunities, new questions, new concerns. Royal Society of Chemistry, UK, pp 1–17
Chin-Chan M, Navarro-Yepes J, Quintanilla-Vega B (2015) Environmental pollutants as risk factors for neurodegenerative disorders: Alzheimer and Parkinson diseases. Front Cell Neurosci 9:1–22
Chen SH, Wu VC, Chuang YC (2008) Using oligonucleotide-functionalized au nanoparticles to rapidly detect foodborne pathogens on a piezoelectric biosensor. J Microbiol Methods 73:7–17
Chellaram C, Murugaboopathi G, John AA, Sivakumar R, Ganesan S, Krithika S, Priya G (2014) Significance of nanotechnology in food industry. APCBEE Procedia 8:109–113
Coccini T, Grandi S, Lonati D, Locatelli C, Simone UD (2015) Comparative cellular toxicity of titanium dioxide nanoparticles 3 on human astrocyte and neuronal cells after acute and 4 prolonged exposure. Neurotoxicology 48:77–89
Concina I, Falasconi M, Gobbi E, Bianchi F, Musci M, Mattarozzi M, Pardo M, Mangia A, Careri M, Sberveglieri G (2009) Early detection of microbial contamination in processed tomatoes by electronic nose. Food Cont 20:873–880
Dasgupta N, Ranjan S, Mundekkad D, Ramalingam C, Shanker R, Kumar A (2015) Nanotechnology in agro-food: from field to plate. Food Res Int 69:381–400
Davari MR, Kazazi SB, Pivehzhani OA (2017) Nanomaterials: implications on agroecosystem. In: Prasad R, Kumar M, Kumar V (eds) Nanotechnology: an agricultural paradigm. Springer Nature, Singapore, pp 59–71
Debnath N, Das S, Seth D, Chandra R, Bhattacharya SC, Goswami A (2011) Entomotoxic effect of silica nanoparticles against Sitophilus oryzae (L.). J Pest Sci 84:99–105
Dehkourdi EH, Mosavi M (2013) Effect of anatase nanoparticles (TiO2) on parsley seed germination (Petroselinum crispum) in vitro. Biol Trace Elem Res 155:283–286
Dias MV, Soares NDFF, Borges SV, Sousa MMD, Nunes CA, Oliveira IRND, Medeiros EAA (2013) Use of allyl isothiocyanate and carbon nanotubes in an antimicrobial film to package shredded, cooked chicken meat. Food Chem 141:3160–3166
Donsì F, Annunziata M, Sessa M, Ferrari G (2011) Nanoencapsulation of essential oils to enhance their antimicrobial activity in foods. LWT – Food Sci Tech 44:1908–1914
Duke MC, Lim A, Luz SC, Nielsen L (2008) Lactic acid enrichment with inorganic nanofiltration and molecular sieving membranes by pervaporation. Food Bioprod Proc 86:290–295
Durga Devi G, Murugan K, Panneer Selvam C (2014) Green synthesis of silver nanoparticles using Euphorbia hirta (Euphorbiaceae) leaf extract against crop pest of cotton bollworm, Helicoverpa armigera (Lepidoptera: Noctuidae). J Biopest 7:54–66
El-bendary HM, El-Helaly AA (2013) First record nanotechnology in agricultural: silica nano- particles a potential new insecticide for pest control. App Sci Report 4:241–246
Elrahman SHA, Mostafa MAM (2015) Applications of nanotechnology in agriculture: an overview. Egyptian J Soil Sci 55:197–214
Emamifar A, Kadivar M, Shahedi M, Soleimanian-Zad S (2010) Evaluation of nanocomposite packaging containing ag and ZnO on shelf life of fresh orange juice. Innovative Food Sci Emerg Technol 11:742–748
Espitia PJP, Soares NDFF, Coimbra JSDR, Andrade NJD, Cruz RS, Medeiros EAA (2012) Zinc oxide nanoparticles: synthesis, antimicrobial activity and food packaging applications. Food Bioprocess Technol 5:1447–1464
EFSA Scientific Committee (2011) Guidance on the risk assessment of the application of nanoscience and nanotechnologies in the food and feed chain. EFSA J 9:1–36
Fang Y, Umasankar Y, Ramasamy RP (2014) Electrochemical detection of p-ethylguaiacol, a fungi infected fruit volatile using metal oxide nanoparticles. Analyst 139:3804–3810
Fasihnia SH, Peighambardoust SH, Peighambardoust SJ (2017) Nanocomposite films containing organoclay nanoparticles as an antimicrobial (active) packaging for potential food application. J Food Process Preserv e13488:1–10
Feizi H, Moghaddam PR, Shahtahmassebi N, Fotovat A (2012) Impact of bulk and nanosized titanium dioxide (TiO2) on wheat seed germination and seedling growth. Biol Trace Elem Res 146:101–106
Fletcher J, Bender C, Budowle B, Cobb WT, Gold SE, Ishimaru CA, Luster D, Melcher U, Murch R, Scherm H, Seem RC, Sherwood JL, Sobral BW, Tolin SA (2006) Plant pathogen forensics: capabilities, needs, and recommendations. Microbiol Mol Biol Rev 70:450–471
Fu J, Park B, Siragusa G, Jones L, Tripp R, Zhao Y, Cho Y (2008) An au/Si hetero-nanorod-based biosensor for Salmonella detection. Nanotech 19:1–7
Gaikwad KK, Singh S, Lee YS (2018) High adsorption of ethylene by alkali-treated halloysite nanotubes for food-packaging applications. Environ Chem Letters 16:1055–1062
Garcia M, Aleixandre M, Gutiérrez J, Horrillo MC (2006) Electronic nose for wine discrimination. Sensors Actuat 113:911–916
Gopinath K, Gowri S, Karthika V, Arumugam A (2014) Green synthesis of gold nanoparticles from fruit extract of Terminalia arjuna, for the enhanced seed germination activity of Gloriosa superba. J Nanostr Chem 4:115–126
Ghorbanzade T, Jafari SM, Akhavan S, Hadavi R (2017) Nano-encapsulation of fish oil in nano-liposomes and its application in fortification of yogurt. Food Chem 216:146–152
Ghormade V, Deshpande MV, Paknikar KM (2011) Perspective for nano-biotechnology enabled protection and nutrition of plants. Biotech Adv 29:792–803
Ghosh A, Dey K, Mani A, Dey AN, Bauri FK (2017) Implication of nanocomposite edible coating for shelf life extension of Indian olive (Elaeocarpus floribundus Blume). Curr J App Sci Tech 22:1–8
Gokmen V, Mogol BA, Lumaga RB, Fogliano V, Kaplun Z, Shimoni E (2011) Development of functional bread containing nanoencapsulated omega-3 fatty acids. J Food Eng 105:585–591
Gonzalez A, Igarzabal CIA (2013) Soy protein-poly(lactic acid) bilayer films as biodegradable material for active food packaging. Food Hydrocoll 33:289–296
Grillo R, Pereira AE, Nishisaka CS, de Lima R, Oehlke K, Greiner R, Fraceto LF (2014) Chitosan/tripolyphosphate nanoparticles loaded with paraquat herbicide: an environmentally safer alternative for weed control. J Hazard Materials 278:163–171
Hafeez A, Razzaq A, Mahmood T, Jhanzab HM (2015) Potential of copper nanoparticles to increase growth and yield of wheat. J Nanosc Advanced Tech 1:6–11
He L, Liu Y, Mustapha A, Lin M (2011) Antifungal activity of zinc oxide nanoparticles against Botrytis cinerea and Penicillium expansum. Microbiol Res 166:207–215
Hoet PHM, Brüske-Hohlfeld I, Salata OV (2004) Nanoparticles–known and unknown health risks. J Nanobiotechnol 2:1–15
Hosseini M, Khabbaz H, Dadmehr M, Ganjali MR, Mohamadneja J (2015) Aptamer-based colorimetric and chemiluminescence detection of aflatoxin B1 in foods samples. Acta Chim Slov 62:721–728
Howard J (2013) Occupational exposure to carbon nanotubes and nanofibers. https://www.cdc.gov/niosh/docs/2013-145/pdfs/. Accessed 20 June 2018
Hsieh KL (2010) Lycopene and resveratrol dietary supplement. US Patent WO/2010/132021, 18 Nov 2010
Hussain AA, Al-Rawajfeh AE (2009) Recent patents of nanofiltration applications in oil processing, desalination, wastewater and food industries. Recent Patents Chemical Eng 2:51–66
Hussain M, Raja NI, Mashwani ZUR, Iqbal M, Sabir S, Yasmeen F (2017) In vitro seed germination and biochemical profiling of Artemisia absinthium exposed to various metallic nanoparticles. 3Biotech 7:101–108
Ing LY, Zin NM, Sarwar A, Katas H (2012) Antifungal activity of chitosan nanoparticles and correlation with their physical properties. Int J Biomat 632698. https://doi.org/10.1155/2012/632698
Ismail M, Prasad R, Ibrahim AIM, Ahmed ISA (2017) Modern prospects of nanotechnology in plant pathology. In: Nanotechnology (eds. Prasad R, Kumar M, Kumar V), Springer Nature Singapore Pte Ltd. 305–317
Jamdagni P, Rana JS, Khatri P, Nehra K (2018) Comparative account of antifungal activity of green and chemically synthesized zinc oxide nanoparticles in combination with agricultural fungicides. Int J Nano Dimen 9:198–208
Jampílek J, králová K (2015) Application of nanotechnology in agriculture and food industry, its prospects and risks. Ecol Chem Eng S22:321–361
Jeon JS, Lee HS (2009) Nano-particles containing calcium and method for preparing the same. US Patent WO/2009/011520, 22 Jan 2009
Jo Y, Kim BH, Jung G (2009) Antifungal activity of silver ions and nanoparticles on phytopathogenic fungi. Plant Dis 93:1037–1043
Kanhed P, Birla S, Gaikwad S, Gade A, Seabra AB, Rubilar O, Duran N, Rai M (2014) In vitro antifungal efficacy of copper nanoparticles against selected crop pathogenic. Fungi Mater Lett 115:13–17
Kashyap PL, Rai P, Sharma S, Chakdar H, Kumar S, Pandiyan K, Srivastava AK (2016) Nanotechnology for the detection and diagnosis of plant pathogens. In: Ranjan S et al (eds) Nanoscience in food and agriculture 2, sustainable agriculture reviews 21. Springer, Basel pp 253–276
Khan I, Tango CN, Sumaira M, Deog-Hwan O (2017) Evaluation of nisin-loaded chitosan-monomethyl fumaric acid nanoparticles as a direct food additive. Carbohydrate Poly 184:100–107
Khalifa NS, Hasaneen MN (2018) The effect of chitosan–PMAA–NPK nanofertilizer on Pisum sativum plants. 3Biotech 8:193–205
Khodakovskaya M, Dervishi E, Mahmood M, Xu Y, Li Z, Watanabe F, Biris AS (2009) Carbon nanotubes are able to penetrate plant seed coat and dramatically affect seed germination and plant growth. ACS Nano 3:3221–3227
Khooshe-Bast SN, Ghaffari-moghaddam M, Mirshekar A (2016) Insecticidal effects of zinc oxide nanoparticles and Beauveria bassiana TS11 on Trialeurodes vaporariorum (Westwood, 1856) (Hemiptera: Aleyrodidae). Acta Agri Slovenica 107:299–309
Kim T, Oh J (2016) Dual nutraceutical nanohybrids of folic acid and calcium containing layered double hydroxides. J Solid State Chem 233:125–132
Kim KJ, Sung WS, Suh BK, Moon SK, Choi JS, Kim JG, Lee DG (2009) Antifungal activity and mode of action of silver nano-particles on Candida albicans. Biometals 22:235–242
Kim SW, Jung JH, Lamsal K, Kim YS, Min JS, Lee YS (2012) Antifungal effects of silver nanoparticles (AgNPs) against various plant pathogenic fungi. Mycobiology 40:53–58
Kirdar SS (2015) ISITES conference. Valencia, pp 1517–1527
Ko KS, Koh DC, Kong IC (2017) Evaluation of the effects of nanoparticle mixtures on Brassica seed germination and bacterial bioluminescence activity based on the theory of probability. Nano 7:344–354
Kothari P, Setia H (2017) Silver nanoparticle filled HPMC and xanthan films for food packaging and safety. Indian J Sci Tech 10:1–6
Kumar GD, Natarajan N, Nakkeeran S (2016) Antifungal activity of nanofungicide Trifloxystrobin 25% + Tebuconazole 50% against Macrophomina phaseolina. African J Microbiol Res 10:100–105
Lin HY, Huang CH, Lu SH, Kuo IT, Chau LK (2014) Direct detection of orchid viruses using nanorod-based fiber optic particle plasmon resonance immunosensor. Biosens Bioelectron 51:371–378
Lamsal K, Kim SW, Jung JH, Kim YS, Kim KS, Lee YS (2011) Inhibition effects of silver nanoparticles against powdery mildews on cucumber and pumpkin. Mycobiol 39:26–32
Latva-Nirva, E, Dahms G, Jung A, Fiebrig B (2009) Ultrafine titanium dioxide nanoparticles and dispersions thereof. US Patent WO 2009/141499 Al, 26 Nov 2009
Le Israeli-Lev G, Livney YD (2014) Self-assembly of hydrophobin and its coassembly with hydrophobic nutraceuticals in aqueous solutions: towards application as delivery systems. Food Hydrocoll 35:28–35
Lee DG, Ponvel KM, Kim M, Hwang S, Ahn IK, Lee CH (2009) Immobilization of lipase on hydrophobic nano-sized magnetite particles. J Mol Catal B Enzym 57:62–66
Lopez A, Gavara R, Lagaron J (2006) Bioactive packaging: turning foods into healthier foods through biomaterials. Trends Food Sci Technol 17:567–575
Li FS, Wu WT (2009) Lipase-immobilized electrospun PAN nanofibrous membranes for soybean oil hydrolysis. Biochem Eng J 45:48–53
Liu R, Lal R (2014) Synthetic apatite nanoparticles as a phosphorus fertilizer for soybean (Glycine max). Sci Reports 4:5686–5691
Long Q, Li H, Zhang Y, Yao S (2015) Upconversion nanoparticle-based fluorescence resonance energy transfer assay for organophosphorus pesticides. Biosens Bioelectron 68:168–174
Longano D, Ditaranto N, Cioffi N, Niso FD, Sibillano T, Ancona A, Conte A, Del Nobile MA, Sabbatini L, Torsi L (2012) Analytical characterization of laser-generated copper nanoparticles for antibacterial composite food packaging. Anal Bioanal Chem 403:1179–1186
Mahmoodzadeh H, Nabavi M, Kashefi H (2013) Effect of nanoscale titanium dioxide particles on the germination and growth of canola (Brassica napus). J Ornam Hort Plants 3:25–32
Malaikozhundan B, Vaseeharan B, Vijayakumar S, Thangaraj MP (2017) Bacillus thuringiensis coated zinc oxide nanoparticle and its biopesticidal effects on the pulse beetle, Callosobruchus maculatus. J Photochem Photobiol B Biol 174:306–314
Manikandan A, Subramanian KS (2016) Evaluation of zeolite based nitrogen nano-fertilizers on maize growth, yield and quality on inceptisols and alfisols. Int J Plant Soil Sci 9:1–9
Manimaran M (2015) A review on nanotechnology and its implications in agriculture and food industry. Asian J Plant Sci Res 5:13–15
Martin-Ortigosa S, Peterson DJ, Valenstein JS, Lin VSY, Trewyn BG, Lyznik LA, Wang K (2014) Mesoporous silica nanoparticle-mediated intracellular Cre protein delivery for maize genome editing via loxP site excision. Plant Physiol 164:537–547
McKeague MK, Giamberardino A, DeRosa MC (2011) Advances in aptamer based biosensors for food safety. In: Somerset V (ed) Environmental biosensors. InTech, Croatia, pp 17–42
Mehrazar E, Rahaie M, Rahaie S (2015) Application of nanoparticles for pesticides, herbicides, fertilisers and animals feed management. Int J Nanoparticles 8:1–19
Migliore L, Uboldi C, Di Bucchianico S, Coppede F (2015) Nanomaterials and neurodegeneration. Environ Mol Mutagen 56:149–170
Mishra S, Singh BR, Singh A, Keswani C, Naqvi AH, Singh HB (2014) Biofabricated silver nanoparticles act as a strong fungicide against Bipolaris sorokiniana causing spot blotch disease in wheat. PLoS One 9:e97881. https://doi.org/10.1371/journal.pone.0097881
Moghadam A, Vattani H, Baghaei N, Keshavarz N (2012) Effect of different levels of fertilizer nano-iron chelates on growth and yield characteristics of two varieties of spinach (Spinacia oleracea L.): Varamin 88 and Viroflay. Res J App Sci Eng Tech 4:4813–4818
Momin JK, Jayakumar C, Prajapati JB (2013) Potential of nanotechnology in functional foods. Emirates J Food Agricult 25:10–19
Moura MRD, Mattoso LHC, Zucolotto V (2012) Development of cellulose-based bactericidal nanocomposites containing silver nanoparticles and their use as active food packaging. J Food Eng 109:520–524
Mozafari MR, Flanagan J, Matia-Merino L, Awati A, Omri A, Suntres ZE, Singh H (2006) Recent trends in the lipid-based nanoencapsulation of antioxidants and their role in foods. J Sci Food Agri 86:2038–2045
Mukhopadhyay SS (2014) Nanotechnology in agriculture: prospects and constraints. Nanotech Sci App 7:63–71
Naderi MR, Danesh-Shahraki A (2013) Nanofertilizers and their roles in sustainable agriculture. Intl J Agri Crop Sci 5:2229–2232
Nesi A, Gordi M, Davidovi S, Radovanovic Z, Nedeljkovi J, Smirnova I, Gurikov P (2018) Pectin-based nanocomposite aerogels for potential insulated food packaging application. Carbohydrate Poly 195:128–135
Nguyen M, Reynolds N, Vigneswaran S (2003) By-product recovery from cottage cheese production by nanofiltration. J Clean Prod 11:803–807
Niemeyer CM, Doz P (2001) Nanoparticles, proteins, and nucleic acids: biotechnology meets materials science. Angewandte Chemie Int Ed 40:4128–4158
Oliveira Marques PRB, Lermo A, Campoy S, Yamanaka H, Barbe J, Alegret S, Pividori MI (2009) Double-tagging polymerase chain reaction with a thiolated primer and electrochemical genosensing based on gold nanocomposite sensor for food safety. Anal Chem 81:1332–1339
Oskam G (2006) Metal oxide nanoparticles: synthesis, characterization and application. J SolGel Sci Technol 37:161–164
Otles S, Yalcin B (2010) Nano-biosensors as new tool for detection of food quality and safety. LogForum 6:67–70
Ouda SM (2014) Antifungal activity of silver and copper nanoparticles on two plant pathogens, Alternaria alternata and Botrytis cinerea. Res J Microbiol 9:34–42
Pal S, Alocilja EC (2009) Electrically active polyaniline coated magnetic (EAPM) nanoparticle as novel transducer in biosensor for detection of Bacillus anthracis spores in food samples. Biosens Bioelectron 24:1437–1444
Panacek A, Kolar M, Vecerova R, Prucek R, Soukupova J, Krystof V, Hamal P, Zboril R, Kvıtek L (2009) Antifungal activity of silver nanoparticles against Candida spp. Biomaterials 30:6333–6340
Paniel N, Radoi A, Marty J (2010) Development of an electrochemical biosensor for the detection of aflatoxin M1 in milk. Sensors 10:9439–9448
Parveen A, Rao S (2014) Effect of nanosilver on seed germination and seedling growth in Pennisetum glaucum. J Clust Sci 26:693–701
Pereira AES, Grillo R, Mello NFS, Rosa AH, Fraceto LF (2014) Application of poly(epsilon-caprolactone) nanoparticles containing atrazine herbicide as an alternative technique to control weeds and reduce damage to the environment. J Hazard Mat 268:207–215
Perlatti B, Bergo PLD, da Silva MFDGF, Fernandes JB, Forim MR (2013) Polymeric nanoparticle-based insecticides: a controlled release purpose for agrochemicals. In: Trdan S (ed) Insecticides - development of safer and more effective technologies, InTech, Croatia, pp 523–550
Pham DC, Nguyen TH, Ngoc UTH, Le NTT, Tran TV, Nguyen DH (2018) Preparation, characterization and antifungal properties of chitosan-silver nanoparticles synergize fungicide against Pyricularia oryzae. J Nanosc Nanotech 18:1–7
Popov KI, Filippov AN, Khurshudyan SA (2010) Food nanotechnologies. Russian J Gen Chem 80:630–642
Pradhan N, Singh S, Ojha N, Shrivastava A, Barla A, Rai V, Bose S (2015) Facets of nanotechnology as seen in food processing, packaging, and preservation industry. Biomed Res Int 365672. https://doi.org/10.1155/2015/365672
Prasad R, Kumar V, Prasad KS (2014) Nanotechnology in sustainable agriculture: present concerns and future aspects. Afr J Biotechnol 13(6):705–713
Prasad R, Bhattacharyya A, Nguyen QD (2017a) Nanotechnology in sustainable agriculture: Recent developments, challenges, and perspectives. Front Microbiol 8:1014. doi: https://doi.org/10.3389/fmicb.2017.01014
Prasad R, Kumar V, Kumar M (2017b) Nanotechnology: Food and Environmental Paradigm. Springer Nature Singapore Pte Ltd. (ISBN 978-981-10-4678-0)
Priyadarshi R, Negi YS (2016) Effect of varying filler concentration on zinc oxide nanoparticle embedded chitosan films as potential food packaging material. J Polym Environ 25:1087–1098
Puoci F, Lemma F, Spizzirri UG, Cirillo G, Curcio M, Picci N (2008) Polymer in agriculture: a review. Am J Agri Biol Sci 3:299–314
Putheti S (2015) Application of nanotechnology in food, nutraceuticals and pharmaceuticals. e-J Sci Tech 2:17–23
Rad F, Mohsenifar A, Tabatabaei M, Safarnejad MR, Shahryari F, Safarpour H, Foroutan A, Mardi M, Davoudi D, Fotokian M (2012) Detection of Candidatus Phytoplasma aurantifolia with a quantum dots FRET-based biosensor. J Plant Pathol 94:525–534
Raei M, Rajabzadeh G, Zibaei S, Jafari SM, Sani AA (2015) Nano-encapsulation of isolated lactoferrin from camel milk by calcium alginate and evaluation of its release. Int J Biol Macromol 79:669–673
Ragaei M, Sabry AH (2014) Nanotechnology for insect pest control. Int J Sci Environ Tech 3:528–545
Rao PJ, Khanum H (2016) A green chemistry approach for nanoencapsulation of bioactive compound curcumin. LWT - Food Sci Tech 65:695–702
Ravichandran R (2010) Nanotechnology applications in food and food processing: innovative green approaches, opportunities and uncertainties for global market. Int J Green Nanotech 1:P72–P96
Rouhani M, Samih MA, Kalantari S (2012) Insecticide effect of silver and zinc nanoparticles against Aphis nerii Boyer de Fonscolombe (Hemiptera: Aphididae). Chilean J Agri Res 72:590–594
Rui M, Ma C, Hao Y, Guo J, Rui Y, Tang X, Zhao X, Fan X, Zhang Z, Hou T, Zhu S (2016) Iron oxide nanoparticles as a potential iron fertilizer for peanut (Arachis hypogaea). Front Plant Sci 7:815–824
Saharan V, Sharma G, Yadav M, Choudhary MK, Sharma SS, Pal A, Raliya R, Biswas P (2015) Synthesis and in vitro antifungal efficacy of cu–chitosan nanoparticles against pathogenic fungi of tomato. Int J Biol Macromol 75:346–353
Sahayaraj K, Madasamy M, Radhika SA (2016) Insecticidal activity of bio-silver and gold nanoparticles against Pericallia ricini fab. (Lepidaptera: Archidae). J Biopest 9:63–72
Sahoo D, Mandal A, Mitra T, Chakraborty K, Bardhan M, Dasgupta AK (2018) Nanosensing of pesticides by zinc oxide quantum dot: an optical and electrochemical approach for the detection of pesticides in water. J Agric Food Chem 66:414–423
Sarwar MS, Niazi MBK, Jahan Z, Ahmad T, Hussain A (2017) Preparation and characterization of PVA/nanocellulose/ag nanocomposite films for antimicrobial food packaging. Carbohydrate Poly 184:453–464
Savithramma N, Ankanna S, Bhumi G (2012) Effect of nanoparticles on seed germination and seedling growth of Boswellia ovalifoliolata – an endemic and endangered medicinal tree. Taxon Nano Vision 2:61–68
Savolainen K, Pylkkänen L, Norppa H, Falck G, Lindberg H, Tuomi T, Vippola M, Alenius H, Hämeri K, Koivisto J, Brouwer D, Mark D, Bard D, Berges M, Jankowska E, Posniak M, Farmer P, Singh R, Krombach F, Bihari P, Kasper G, Seipenbusch M (2010) Nanotechnologies, engineered nanomaterials and occupational health and safety – a review. Saf Sci 48:957–963
Scampicchio M, Ballabio D, Arecchi A, Cosio SM, Mannino S (2008) Amperometric electronic tongue for food analysis. Microchim Acta 163:11–21
Scrinis G, Lyons K (2007) THE emerging nano-corporate paradigm: nanotechnology and the transformation of nature, food and Agri-food systems. Int J Socio Food Agri 15:22–44
Singh NB, Amist N, Yadav K, Singh D, Pandey JK, Singh SC (2013) Zinc oxide nanoparticles as fertilizer for the germination, growth and metabolism of vegetable crops. J Nanoeng Nanomanufacturing 3:353–364
Singh T, Shukla S, Kumar P, Wahla V, Bajpai VK, Rather IA (2017) Application of nanotechnology in food science: perception and overview. Front Microbiol 8:1–7
Shahrekizad M, Ahangara AG, Mirb N (2015) EDTA-coated Fe3O4 nanoparticles: a novel biocompatible fertilizer for improving agronomic traits of sunflower (Helianthus annuus). J Nanostruct 5:117–127
Shaker AM, Zaki AH, Abdel-Rahim EF, Khedr MH (2016) Novel CuO nanoparticles for pest management and pesticides photodegradation. Adv Environ Biol 10:274–283
Sharma R, Pathak Y (2010) Acyl ascorbate in enzymatic synthesis: industrial uses as a food nanoadditive. Nanotech 1:79–82
Sharon M, Choudhary AK, Kumar R (2010) Nanotechnology in agricultural diseases and food safety. J Phytology 2:83–92
Shelby T, Sulthana S, McAfee J, Banerjee T, Santra S (2017) Foodborne pathogen screening using magneto-fluorescent nanosensor: rapid detection of E. coli O157: H7. J Vis Exp 127:e55821. https://doi.org/10.3791/55821
Siddiqui MH, Al-Whaibi MH (2014) Role of nano-SiO2 in germination of tomato (Lycopersicum esculentum seeds mill.). Saudi J Bio Sci 21:13–17
Silva AT, Nguyen A, Ye C, Verchot J, Moon JH (2010) Conjugated polymer nanoparticles for effective siRNA delivery to tobacco BY-2 protoplasts. BMC Plant Biol 10:291–304
Silva HD, Cerqueira MA, Vicente AA (2012) Nanoemulsions for food applications: development and characterization. Food Bioprocess Technol 5:854–867
Silvestre C, Duraccio D, Cimmino S (2011) Food packaging based on polymer nanomaterials. Prog Poly Sci 36:1766–1782
Siva GV, Benita LFJ (2016) Iron oxide nanoparticles promotes agronomic traits of ginger (Zingiber officinale Rosc.). Int J Adv Res Biol Sci 3:230–237
Song K, Lee S, Ban C (2012) Aptamers and their biological applications. Sens 12:612–631
Song L, Hongna L, Yan D, Lin L, Nongyue H (2013) Development of a magnetic nanoparticles microarray for simultaneous and simple detection of foodborne pathogens. J Biomed Nanotech 9:1254–1260
Sousa GFM, Gomes DG, Campos EVR, Oliveira JL, Fraceto LF, Stolf-Moreira R, Oliveira HC (2018) Post-emergence herbicidal activity of nanoatrazine against susceptible weeds. Front Environ Sci 6:1–6
Srivastava G, Das CK, Das A, Singh SK, Roy M, Kim H, Sethy N, Kumar A, Sharma RK, Singh SK, Philip D, Das M (2014) Seed treatment with iron pyrite (FeS2) nanoparticles increases the production of spinach. RSC Adv 4:58495–58504
Subramanian KS, Tarafdar JC (2011) Prospects of nanotechnology in Indian farming. Indian J Agri Sci 81:887–893
Sun X, Liu B, Xia K (2011) A sensitive and regenerable biosensor for organophosphate pesticide based on self-assembled multilayer film with CdTe as fluorescence probe. Luminescence 26:616–621
Tahira MA, Bajwa SZ, Mansoor S, Briddon RW, Khan WS, Scheffler BE, Amin I (2018) Evaluation of carbon nanotube based copper nanoparticle composite for the efficient detection of agroviruses. J Hazard Mater 346:27–35
Tarafdar JC (2015) Nanoparticle production, characterization and its application to horticultural crops. In: Aishwath OP, Singh B, Dubey PN, Mishra BK (eds) Winter School on “utilization of degraded land and soil through horticultural crops for agricultural productivity and environmental quality”. NRCSS, Ajmer, Rajasthan, pp 222–229
Thangavel G (2014) Nanotechnology in food industry – a review. Int J Chem Tech 6:4096–4101
Torney FO, Trewyn BG, Lin VSY, Wang K (2007) Mesoporous silica nanoparticles deliver DNA and chemicals into plants. Nature Nanotech 2:295–300
Tripathi S, Mehrotra GK, Dutta PK (2008) Chitosan based antimicrobial films for food packaging applications. E-Polymers 93:1–7
Upadhyaya H, Roy H, Shome S, Tewari S, Bhattacharya MK, Panda SK (2017) Physiological impact of zinc nanoparticle on germination of rice (Oryza sativa L) seed. J Plant Sci Phytopathol 1:62–70
Vani C, Brindhaa U (2013) Silica nanoparticles as nanocides against Corcyra cephalonica (S.), the stored grain pest. Int J Pharm Biol Sci 4:1108–1118
Verdian A (2017) Apta-nanosensors for detection and quantitative determination of acetamiprid – a pesticide residue in food and environment. Talanta 176:456–464
Vimala V, Clarke SK, Urvinder Kaur S (2016) Pesticides detection using acetylcholinesterase nanobiosensor. Biosens J 5:1–4
Wang M, Li Z (2008) Nano-composite ZrO2/au film electrode for voltammetric detection of parathion. Sensors Actuators B Chem 133:607–612
Wang SL, Nguyen AD (2018) Effects of Zn/B nanofertilizer on biophysical characteristics and growth of coffee seedlings in a greenhouse. Res Chem Intermed 44:4889–4901
Wang Z, Wei F, Liu SY, Xu Q, Huang J-Y, Dong XY, Hua JH, Yang Q, Zhao YD, Chen H (2010) Electrocatalytic oxidation of phytohormone salicylic acid at copper nanoparticles-modified gold electrode and its detection in oilseed rape infected with fungal pathogen Sclerotinia sclerotiorum. Talanta 80:1277–1280
Wani AH, Shah MA (2012) A unique and profound effect of MgO and ZnO nanoparticles on some plant pathogenic fungi. J App Pharm Sci 02:40–44
Warczok J, Ferrando M, Lopez F, Guell C (2004) Concentration of apple and pear juices by nanofiltration at low pressures. J Food Eng 63:63–70
Win-Shwe T, Fujimaki H (2011) Nanoparticles and neurotoxicity. Int J Mol Sci 12:6267–6280
Wu J, Ding T, Sun J (2013) Neurotoxic potential of iron oxide nanoparticles in the rat brain striatum and hippocampus. Neurotoxicology 34:243–253
Xie Y, Li Y, Niu L, Wang H, Qian H, Yao W (2012) A novel surface-enhanced Raman scattering sensor to detect prohibited colorants in food by graphene/silver nanocomposite. Talanta 100:32–37
Xu X, Liu X, Li Y, Ying Y (2013) A simple and rapid optical biosensor for detection of aflatoxin B1 based on competitive dispersion of gold nanorods. Biosens Bioelectron 47:361–367
Yan X, Song Y, Zhu C, Li H, Du D, Su X, Lin Y (2018) MnO2 nanosheet-carbon dots sensing platform for sensitive detection of organophosphorus pesticides. Anal Chem 90:2618–2624
Yang M, Kostov Y, Rasooly A (2008) Carbon nanotubes based optical immunodetection of staphylococcal enterotoxin B (SEB) in food. Int J Food Microbiol 127:78–83
Yang S, Wu T, Zhao X, Li X, Tan W (2014) The optical property of core-shell nanosensors and detection of atrazine based on localized surface plasmon resonance (LSPR) sensing. Sensors 14:13273–13284
Yao KS, Li SJ, Tzeng KC, Cheng TC, Chang CY, Chiu CY, Liao CY, Hsu JJ, Lin ZP (2009) Fluorescence silica nanoprobe as a biomarker for rapid detection of plant pathogens. Adv Materials Res 79-82:513–516
Yassen A, Abdallah E, Gaballah M, Zaghloul S (2017) Role of silicon dioxide nano fertilizer in mitigating salt stress on growth, yield and chemical composition of cucumber (Cucumis sativus L.). Int J Agri Res 12:130–135
Yildirim S, Röcker B, Pettersen MK, Nilsen-Nygaard J, Ayhan Z, Rutkaite R, Radusin T, Suminska P, Marcos B, Coma V (2017) Active packaging applications for food. Comp Rev Food Sci Food Safety 17:165–199
Zacco E, Pividori MI, Alegret S (2006) Electrochemical magnetoimmunosensing strategy for the detection of pesticides residues. Anal Chem 78:1780–1788
Zhao W, Ge P, Xu J, Chen H (2009) Selective detection of hypertoxic organophosphates pesticides via PDMS composite based acetylcholinesterase-inhibition biosensor. Environ Sci Technol 43:6724–6729
Ziaee M, Ganji Z (2016) Insecticidal efficacy of silica nanoparticles against Rhyzopertha dominica F. And Tribolium confusum Jacquelin du Val. J Plant Prot Res 56:250–255
Author information
Authors and Affiliations
Editor information
Editors and Affiliations
Rights and permissions
Copyright information
© 2020 Springer Nature Switzerland AG
About this chapter
Cite this chapter
Priyanka, P., Kumar, D., Yadav, A., Yadav, K. (2020). Nanobiotechnology and its Application in Agriculture and Food Production. In: Thangadurai, D., Sangeetha, J., Prasad, R. (eds) Nanotechnology for Food, Agriculture, and Environment. Nanotechnology in the Life Sciences. Springer, Cham. https://doi.org/10.1007/978-3-030-31938-0_6
Download citation
DOI: https://doi.org/10.1007/978-3-030-31938-0_6
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-030-31937-3
Online ISBN: 978-3-030-31938-0
eBook Packages: Biomedical and Life SciencesBiomedical and Life Sciences (R0)