research articles on nanoparticles

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• Published: 03 June 2023

Human and environmental impacts of nanoparticles: a scoping review of the current literature

• Elizabeth Adjoa Kumah 1 ,
• Raoul Djou Fopa 2 ,
• Saeed Harati 2 ,
• Paul Boadu 3 ,
• Fatemeh Vida Zohoori 4 &
• Tannaz Pak 2  

BMC Public Health volume  23 , Article number:  1059 ( 2023 ) Cite this article

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Use of nanoparticles have established benefits in a wide range of applications, however, the effects of exposure to nanoparticles on health and the environmental risks associated with the production and use of nanoparticles are less well-established. The present study addresses this gap in knowledge by examining, through a scoping review of the current literature, the effects of nanoparticles on human health and the environment. We searched relevant databases including Medline, Web of Science, ScienceDirect, Scopus, CINAHL, Embase, and SAGE journals, as well as Google, Google Scholar, and grey literature from June 2021 to July 2021. After removing duplicate articles, the title and abstracts of 1495 articles were first screened followed by the full-texts of 249 studies, and this resulted in the inclusion of 117 studies in the presented review.

In this contribution we conclude that while nanoparticles offer distinct benefits in a range of applications, they pose significant threats to humans and the environment. Using several biological models and biomarkers, the included studies revealed the toxic effects of nanoparticles (mainly zinc oxide, silicon dioxide, titanium dioxide, silver, and carbon nanotubes) to include cell death, production of oxidative stress, DNA damage, apoptosis, and induction of inflammatory responses. Most of the included studies (65.81%) investigated inorganic-based nanoparticles. In terms of biomarkers, most studies (76.9%) used immortalised cell lines, whiles 18.8% used primary cells as the biomarker for assessing human health effect of nanoparticles. Biomarkers that were used for assessing environmental impact of nanoparticles included soil samples and soybean seeds, zebrafish larvae, fish, and Daphnia magna neonates.

From the studies included in this work the United States recorded the highest number of publications ( n  = 30, 25.64%), followed by China, India, and Saudi Arabia recording the same number of publications ( n  = 8 each), with 95.75% of the studies published from the year 2009. The majority of the included studies (93.16%) assessed impact of nanoparticles on human health, and 95.7% used experimental study design. This shows a clear gap exists in examining the impact of nanoparticles on the environment.

• While nanoparticles are beneficial in a range of applications, they pose significant threats to humans and the environment.

• Immortalised cell lines are mostly used as biomarkers to assess human health effect of nanoparticles.

• Biomarkers such as soil samples and zebrafish larvae are used to investigate the environmental effect of nanoparticles.

• This work has revealed the toxic effects of nanoparticles to include production of oxidative stress, DNA damage, apoptosis, cell death, and induction of inflammatory responses.

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Introduction

Importance and meaning.

Nanoparticles are small particles ranging from 1 to 100 nm (nm) in size [ 1 ]. They are used in a wide range of applications and can be grouped into four types: 1) inorganic-based nanoparticles, 2) carbon-based nanoparticles, 3) organic/polymer nanoparticles, and 4) composite-based nanoparticles [ 2 ]. Inorganic-based nanoparticles are made up of different metal and metal oxides. Examples of metal-based inorganic nanoparticles include aluminium, silver, gold, zinc, lead, iron, cadmium, and copper, whereas examples of metal oxide-based inorganic nanoparticles include aluminium oxide, copper oxide, iron oxide, silica, zinc oxide, titanium oxide, and magnesium aluminium oxide. Carbon-based nanoparticles include fullerene, graphene, multi- and single-walled carbon nanotubes, carbon black, and carbon fibres. Organic-based nanoparticles are derived from organic materials without carbon, for example, liposome, dendrimers, cyclodextrin, and micelle, whereas composite nanoparticles are made from combinations of metal oxide-based, metal-based, organic-based, and/or carbon-based nanoparticles.

In recent years, nanoparticles have gained increasing attention due to their use in consumer products, medicine, soil, and aquatic environments. For example, nanoparticles have been used for textiles [ 3 ], water treatment [ 4 ], environmental remediation [ 5 , 6 , 7 ], cancer therapy [ 8 ], radiology [ 9 ], and cosmetics [ 10 ]. This growing attention and extensive usage of nanoparticles is due to specific novel characteristics exhibited by such particles, which results from their small size and large surface area [ 11 ]. These unique qualities, while advantageous, pose certain risks to living organisms.

The harmful effects of nanoparticles

The small sizes of nanoparticles give them the ability to permeate physiological barriers of living organisms, causing harmful biological reactions. Nanoparticles are known to enter the human body through the lung, intestinal tract, or skin, and can be toxic to the brain, cause lung inflammation and cardiac problems [ 12 ]. In fact, certain nanoparticles have been found to cause permanent cell damage through organ injury and oxidative stress, due to their size and composition. In a study by Magrez et al. [ 13 ] to assess the toxic effect of carbon-based nanoparticles on lung cancer cells, the authors reported findings suggesting that carbon-based nanoparticles cause size-dependent cytotoxicity. The level of toxicity of nanoparticles is suggested to be dependent on factors such as composition of the nanoparticle, size, surface functionality, crystallinity, and aggregation [ 14 ]. Moreover, the toxicity of a nanoparticle in an individual is dependent on the genetic make-up of that individual, which is determined by the individual's ability to adapt and respond to toxic substances.

The gaps of previous studies

There are growing concerns regarding the toxicologic effects of nanoparticles, and frequent exposure to nanoparticles is regarded as a public health threat [ 15 ]. While there is extensive evidence about the benefits of nanoparticles, as well as the potential health and environmental risks associated with its production and use, current understanding of the impact of nanoparticles exposure to human health and the environment is limited. The current review seeks to explore, through a scoping review of the current literature, the effects of nanoparticles on human health and the environment. This review is unique as it adopts a systematic scoping approach to explore the current literature on the health risks posed by the manufacture, distribution, and use of nanoparticles. Published studies in this area have mainly used a narrative literature review approach [ 2 , 16 , 17 ].

Objective and research questions

The objective of this review is to map the distribution of the current literature on the human and environmental impacts of nanotoxicity. Specifically, this scoping review will be guided by the following research questions:

What is the relative distribution of the current literature on the human and environmental impact of nanotoxicity?

Which exposure pathways and nanoparticles have been researched and which have not?

What biomarkers have been used in assessing the human and environmental impact of exposure to nanoparticles?

This scoping review was conducted and reported in accordance with the Joanna Briggs Institute Reviewers Manual [ 18 ]. The following steps were followed:

Defining and aligning the objectives and research questions

Developing and aligning the inclusion criteria with the objectives and research questions

Describing the planned approach to evidence searching and selection

Searching for the evidence

Extracting the evidence

Charting the evidence

Summarising the evidence in relation to the objectives and research questions

The Preferred Reporting of Items for Systematic Reviews and Meta-Analysis (PRISMA) statement was used to summarise the screening process. The protocol of this review has been registered with the Open Science Framework [ 19 ].

Search strategy

The aim of the search strategy was to find both published and unpublished studies that have examined the effect of nanotoxicity on human health and the environment. Search terms consisted of a combination of key terms and concepts in the objective and research questions, using the Boolean operators, 'AND', and 'OR' as follows:

(nanomaterials OR nanoparticles OR nanostructures) AND (toxicity OR health) AND (“biomarker* of exposure” OR biomarker OR exposure) AND (human OR environment).

The search was limited to peer-reviewed articles published from the year 2000. This was to enable us to study the current literature (research conducted over the last 2 decades). The search was limited to primary studies published in the English language due to difficulties with language translation.

Table 1 below presents a list of the databases, grey literature, and search engines that were searched for eligible papers. The reference list of all included papers was also searched for additional papers on the subject matter.

For the database searches, a master search strategy was first developed using the Medline database, this was then modified for the other databases. The supplementary material file presents the Medline search history. The literature search was conducted between 1 st June 2021 and 31 st July 2021.

Reference management

All search results were imported into an Endnote library to help manage references and to remove duplicate articles. Once duplicates were removed, the search results were exported from Endnote into Covidence (a web-based software platform that streamlines the production of scoping/systematic reviews) for screening. The Covidence software was also useful in identifying and deduplicating articles that could not be identified by Endnote.

Selection criteria

The following criteria were used to identify eligible articles for inclusion in the review.

Inclusion criteria

Types of participants.

Studies that have assessed the human and environmental impacts of nanotoxicity were considered for inclusion in this review. Human participants included children and/or adults of any age, gender, or ethnicity. Studies involving the use of animals as biomarkers for assessing the environmental impact of nanotoxicity were also considered for inclusion.

Studies that have examined the impacts of nanotoxicity as well as the biomarkers for assessing exposure to nanoparticles were eligible for inclusion in this review. While all types of nanoparticles were considered for inclusion, attention was given to studies involving metallic (oxides, pure metal) and carbonaceous (fullerenes, carbon nanotubes, and graphene) nanoparticles. This is mainly due to these particles being widely produced and used [ 20 ], therefore, they are considered the most relevant for public health.

Studies from any geographical location aimed at assessing the human and/or environmental impact of nanotoxicity were considered eligible for inclusion. Studies whose full texts were in a language other than English were excluded because there were no available translators.

Study types

We included all original primary research (both quantitative and qualitative), including, but not limited to randomised controlled studies, quasi-experimental studies, surveys, retrospective and prospective cohort studies, case studies, and phenomenological studies.

Exclusion criteria

The following exclusion criteria were applied to the title and abstract, as well as the full-text review stage:

Irrelevant problem/focus: studies that have not examined the human and/or environmental impact of nanotoxicity, or the biomarkers for assessing exposure to nanoparticles

Irrelevant type of study: review reports or studies that did not contain any original research

Selection of studies

We employed a two-step screening process to assess search results for eligible studies. The first level involved screening of the titles and abstracts and was done independently by two reviewers (EK and RF). The next step was carried out independently by three reviewers (EK, RF, and SH) and involved screening of the full-texts of potentially eligible papers. Disagreements between reviewers were resolved through discussions and consensus. Where disagreements persisted, a third reviewer (TP or FVZ) was consulted.

Data charting

We developed a standardised data extraction form in the Covidence software for data extraction. The form was designed to collect the following information from included studies: year of publication, aim/objective of study, study design, country, type of nanoparticle, application of the nanoparticle, major exposure route(s), biomarker/model used, how biomarker was obtained, and study outcome(s).

The developed data extraction form was pilot-tested using 10% of the included articles before beginning the actual data extraction. Data extraction was done by one reviewer (PB, RF, or SH) and verified by another (EK, TP, or FVZ), using the Covidence software.

Data synthesis

The extracted data was first exported into Excel for editing and to check for accuracy. The edited data was then exported from Excel into SPSS (version 26) to aid with data synthesis. Descriptive statistics was used to report included studies by their characteristics and outcome measures, described below.

Characteristics of included studies

Year of publication: studies were grouped based on their year of publication . As stated earlier, this included studies published from the year 2000 to July 2021 (the date of completion of literature searches).

Country in which study was conducted : to assess the distribution of the current literature on human and environmental impact of nanotoxicity, the countries in which eligible studies were conducted were classified into six regions based on the World Bank’s classification of countries. This included: East Asia and Pacific, Europe and Central Asia, Latin America and Caribbean, Middle East and North Africa, North America, South Asia, and Sub-Saharan Africa (World Bank Group, 2018).

Study design : randomised controlled trial, non-randomised controlled trial, cohort study, experimental study, case control study, longitudinal study, uncontrolled before and after studies.

Impact/effect assessed : human health and/or environment

Outcome measures

Type of nanoparticle : This was divided into four groups: 1) inorganic-based nanoparticles, 2) carbon-based nanoparticles, 3) organic nanoparticles, and 4) composite-based nanoparticles two groups, metallic (oxides, pure metal) and carbonaceous (fullerenes and carbon nanotubes) particles.

Biomarker or model used in assessing human and/or environmental exposure : primary cell or immortalised cell line

Effect/impact on human health and/or the environment

A narrative synthesis was then used to further explore findings.

Search results

The database searches resulted in 1553 papers (presented in Fig.  1 ): Medline ( n  = 1,381); ScienceDirect ( n  = 0); Sage Journals Online ( n  = 50); Campbell Collaboration ( n  = 0); Cochrane Collaboration ( n  = 0); Embase ( n  = 5); Scopus ( n  = 6); Web of Science ( n  = 50); CINAHL ( n  = 61). Google and Google Scholar searches yielded 100 results, and no article was obtained from grey literature searches. Following removal of duplicate articles, the titles and abstracts of 1495 articles were screened to assess their eligibility for inclusion, which resulted in the exclusion of a total of 1246 articles as they did not meet the inclusion criteria. As such, the full texts of 249 articles were assessed for eligibility. Following this stage, a total of 132 articles were excluded for several reasons (see Fig.  1 ), whereas 117 studies qualified for inclusion in the review.

Study flow diagram (adapted from Moher et al., 2009)

The studies included in this review originated from 23 countries across several continents, with the majority of the studies originating from Europe and Central Asia ( n  = 50). Nevertheless, the United Sates recorded the highest number of publications ( n  = 30), followed by China, India, and Saudi Arabia recording the same number of publications ( n  = 8). The lowest number of studies ( n  = 1 each) originated from Argentina, Czech Republic, Egypt, Mexico, Pakistan, Poland, and Russia. There were no studies recorded from Sub-Saharan Africa. Figure  2 presents a classification of the included studies by region.

Classification of Studies by Region

Included studies were published between the year 2006 and 2021, with a high proportion of the articles (95.75%) published from the year 2009. However, the year 2020 recorded the highest number of publications ( n  = 15; 12.82%), followed by 2016 ( n  = 14; 11.97%). Table 2 below presents the number of publications per year.

The majority of the studies used an experimental study design ( n  = 112, 95.7%), with only 5 (4.3%) studies employing a cross-sectional design. Regarding the type of impact/effect of nanoparticle assessed, a vast majority of the studies assessed impact on human health ( n  = 109), 5 of the studies assessed effects on the environment, with only 3 studies assessing both human and environmental health impact (Fig.  3 ).

Effect/impact of nanoparticles on human/environmental health

Just over 65% ( n  = 77) of the included studies investigated the human and/or environmental effect of inorganic-based nanoparticles. The inorganic-based nanoparticles that were investigated include, but not limited to, bismuth oxide (Bi 2 O 3 ), silicon dioxide (SiO 2 ), copper oxide (CuO), zinc oxide (ZnO), titanium dioxide (TiO 2 ), silver (Ag), gold (Au), platinum (Pt), iron oxide (Fe 2 O 3 ), cerium oxide (CeO 2 ), cobalt oxide (Co 3 O 4 ), aluminium oxide (Al 2 O 3 ), molybdenum trioxide (MoO3), magnesium oxide (MgO), nickel oxide (NiO), chromium oxide (Cr 2 O 3 ), tungsten oxide (WO 3 ), yttrium oxide (Y 2 O 3 ), and manganese oxide (Mn 2 O 3 ).

Thirty-five (29.9%) studies reported on carbon-based nanoparticles (including single and multi-walled carbon nanotubes (SWCNTs/MWCNTs), graphene oxide (GO), and graphene nanoplatelets, GNP). Three studies [ 21 , 22 , 23 ] reported on both inorganic- and carbon-based nanoparticles; one study [ 24 ] reported on both inorganic-based and polymer nanoparticles (i.e., Titanium dioxide, terbium-doped gadolinium, and polylactic-co-glycolic acid, PLGA), whereas another study [ 25 ] investigated the effect of Poly lactic-co-glycolic acid (a polymer) nanoparticle on the environment.

The most investigated nanoparticles were ZnO ( n  = 25), followed by MWCNTs ( n  = 20), TiO 2 ( n  = 16), CeO ( n  = 15), SWCNTs and Fe 2 O 3 ( n  = 14), and SiO 2 ( n  = 12). The least studied nanoparticles include Pt, Au, MgO, MoO 3 , WO 3 , Carbon Black (CB), and GNP with only one report available.

A significant number ( n  = 90, 76.9%) of the included studies used immortalised cell lines as the biomarker for assessing the human health effect of nanoparticles. Examples of the immortalised cell lines that were used include the human hepatocarcinoma cell line (HepG2), human (alveolar) epithelial A549 cell line with human monocyte-derived dendritic cells (MDDCs) and macrophages (MDMs), Melanoma cells and human foreskin fibroblasts, human airway epithelial (BEAS-2B) cells, human bronchial epithelium (BEAS-2B) cells, human neuroblastoma SHSY5Y cell line, human keratinocyte (HaCaT) cell line, and MCF-7 cell line, which is a human breast cancer cell line with oestrogen, progesterone and glucocorticoid receptors. Immortalised cell lines were mostly purchased/obtained from organisations such as the American Type Culture Collection (ATCC, Manassas, VA, USA).

Twenty-two studies used primary cells obtained from study participants/volunteers. Examples of the primary cells that were used as biomarkers by included studies are human bone marrow mesenchymal stem cells (hBMMSCs) taken from the iliac crest of human donors, human lymphocytes (blood), and human dermal fibroblasts which were isolated by the outgrowth method using infant foreskins obtained after circumcision. Workplace air samples have also been used to investigate workplace exposures to graphene nanoplatelets [ 26 ]. Five studies [ 25 , 27 , 28 , 29 , 30 ] that reported on the environmental effect of nanoparticles used a variety of biomarkers, including soil samples and soybean seeds, Allium cepa bulbs, zebrafish larvae, seedlings of buckwheat, Nitrosomonas europaea KCTC 12270 bacterium (an ammonia-oxidizing bacterium) and Nitrospira moscoviensis (a nitrite-oxidizing bacterium), as well as aquatic species including Daphnia magna neonates, fish, and Carp (Cyprius carpio). The studies included in this review reported several toxicities associated with the production and application of nanoparticles. The most reported health impact of nanoparticles was found to be decreased cell viability and/or cell death (observed by twenty-nine studies). Twenty-eight studies also noted reactive oxygen species generation as a result of exposure to nanoparticles, especially to CNT ( n  = 7), ZnO ( n  = 7), SiO 2 ( n  = 5), and TiO 2 ( n  = 4). The third commonly observed health impact was dose-dependent oxidative stress in the biomarkers ( n  = 25), particularly, in cases of exposure to SiO 2 ( n  = 5), ZnO ( n  = 5), Fe 3 O 4 ( n  = 4), CeO 2 ( n  = 3), and CuO ( n  = 3). In addition, there were sixteen reports regarding DNA damage after exposure to nanoparticles, mainly for ZnO ( n  = 4) and MWCNTs ( n  = 3). Table 3 presents a comprehensive outline of the effects (human health and the environment) reported by each of the included studies. These are further explored in the ensuing section.

The objective of this scoping review was to ascertain the distribution of the current literature on the human and environmental impacts of nanoparticles. Specifically, in this review, we synthesised evidence regarding the exposure pathways and types of nanoparticles that have been researched and the ones that have not, as well as the biomarkers that have been used in assessing human and environmental impact of exposure to nanoparticles.

While the majority of studies originated from Europe and Central Asia, the United States of America (USA) alone recorded the highest number of publications. This finding is not surprising, as the USA has continuously fostered the development of nanotechnology through significant investments in research and development in this area. In 2016, the USA was projected to account for almost one-third of total global nanotechnology research funding [ 136 ]. Moreover, the USA and the European Union have over the years taken a committed approach towards enhancing the health and safety of nanoparticles [ 137 ]. As part of this commitment, annual meetings are held, where researchers discuss topics relating to nano-safety, as well as funding priorities and research needs.

While there have been some investments in nanotechnology research in African countries (including Egypt and South Africa), a recent publication by the United Nations Economic Commission for Africa (UNECA) indicates that the African continent, relative to other continents, is lagging behind with regards to nanotechnology research [ 138 ]. This assertion is consistent with the findings of this review, which found only one study originating from North Africa (Egypt), with no study conducted in Sub-Saharan Africa.

Over the past two decades, there have been increasing public awareness of nanotechnology and a growing concern about its commercial applications [ 139 ]. This has led to rapidly increasing scientific publications in this field, especially from early 2000s [ 140 ]. It is, therefore, not surprising that the studies included in this scoping review were published from the year 2006. Indeed, a literature search of nanotechnology publications by Huang et al. [ 140 ] revealed over 50,000 publications for the year 2006.

Although the included studies investigated a wide range of nanoparticles, most of them focused on inorganic-based nanoparticles (e.g., zinc oxide, titanium dioxide, copper oxide, and silica), followed by carbon-based nanoparticles (e.g., carbon-nanotubes, fullerenes, and graphene) (Table 3 ). This finding is consistent with previous reviews that have reported extensive investigation into the impact of inorganic-based and/or carbon-based nanoparticles [ 141 , 142 ]. These nanoparticles may have gained attention due to their extensive production and usage. In addition to their use for cancer treatment, inorganic and carbon-based nanoparticles provide significant benefits in photothermal therapy, diagnosis, tissue engineering, imaging contrast agents, and sensing applications [ 143 ]. This is due to their unique physical and chemical properties (such as electrical, thermal, structural, mechanical, and optical diversity), which make them stronger, flexible, and more electrically conductible towards several biological entities [ 141 , 144 ]. The advantages of, for example inorganic-based nanoparticles, including their high reactivity, small size and good capacity have been found to induce adverse harmful effects in both humans and the environment.

In this review, a number of approaches were used by included studies to assess the toxicity of nanoparticles. However, the majority of the studies applied the in vitro method, perhaps because in vitro studies are time saving and cost-effective. Nonetheless, the in vitro approach has been criticised by researchers (e.g., Bahadar et al. [ 145 ]) for producing varying results in different laboratories.

The included studies used differing methods in assessing cytotoxicity and genotoxicity: cell membrane integrity was assessed with Lactate dehydrogenase (LDH) assays [ 44 , 57 , 116 ]; cell viability was assessed using tetrazolium reduction assays [ 82 , 83 , 90 , 116 ]; apoptosis was assessed using immunohistochemistry biomarkers [ 60 , 65 , 86 ]; electron microscopy was used to assess intracellular localisation of nanoparticles [ 34 , 106 ]; and cell inflammation was estimated using chemokines biomarkers (i.e., IL-8, TNF- α, and IL-6) [ 146 ]. Compounds such as MTT, XTT, MTS, and WST-1 are used to detect viable cells [ 147 ]. However, in the current review, most of the studies employed MTT tetrazolium assays for investigating cell toxicity [ 47 , 49 , 50 , 58 , 116 ]. Similar findings have been reported by Bahadar et al. [ 145 ] who conducted a review on the toxicity of nanoparticles.

The human impact of nanoparticles

Most of the studies in this review focused on assessing the characteristics of nanoparticles, as well as the impact of nanoparticles on, particularly, human health. In recent years, there have been promising results from the application of nanoparticles to human health, especially in cancer treatment. This is due to the potential of nanoparticles to provide innovative solutions to curb the limitations of traditional treatment methods, including radiotherapy and chemotherapy [ 148 ]. Relative to conventional cancer treatment methods, nanoparticle-based drug delivery systems have been shown to have significant advantages in a) drug resistance, b) correctly targeting tumour cells, c) having good pharmacokinetics, and d) reduction of treatment side effects [ 149 ]. Notwithstanding these benefits, however, nanoparticles have potential harmful effects, and there are controversies about their safe use in humans [ 139 ]. This has undoubtedly led to the rapidly growing number of studies investigating the human health impact of nanoparticles, as was revealed in this review.

The majority of the studies (n = 90) in this review used immortalised cell lines as the biomarker for assessing human health impact of nanoparticles, and only 22 studies used primary cells as biomarkers. Immortalised cell lines have mostly been used for nano-safety studies because, relative to primary cells, they are generally less expensive, readily accessible, and easier to cultivate [ 150 ]. However, the type of cell that is used as biomarker for nano-safety studies is of great importance since this may have an impact on the general outcome of studies [ 151 ]. Cancer cell lines, for example, have a disturbed anti-apoptotic balance, and have undergone transformation in metabolism, which impacts their ability to sustain their high rate of proliferation [ 152 ]. As such, using these cells may have an impact on study findings. Nonetheless, the use of primary cells in nano-safety studies, are not without limitations. Primary cells have limited lifespan in vitro and can suffer from clonal changes.

In using immortalised cell lines, several studies [ 153 , 154 ]) have reported variations in findings regarding nanoparticle-induced effects in cell lines obtained from different species or tissues. For example, Zhang et al. [ 153 ] and Mukherjee et al. [ 154 ] investigated the effect of exposure to silver nanoparticle on mammalian cells. Zhang et al. [ 153 ] used epithelial cells and microphages, and Mukherjee et al. [ 154 ] used the human dermal and cervical cell lines as biomarkers. Mukherjee et al. [ 154 ] reported nanoparticle-induced cytotoxicity such as elevated levels of oxidative stress, cell membrane damage, and glutathione depletion, whereas Zhang et al. [ 153 ] reported effects including changes in antioxidant defence and metallothionein. Moreover, while Ekstrand-Hammarstrom et al. [ 155 ] and Kermanizadeh et al. [ 156 ] have compared the effect of nanoparticles on immortalised cell lines versus primary cells of the same species and tissues, available data regarding the relative effectiveness of these two types of cells are unclear. Therefore, it is difficult to make explicit conclusions as to which of these two types of cells can be used as a reliable biomarker for nano-safety studies.

This review has revealed that humans are exposed to nanoparticles through inhalation, ingestion, or dermal route. After their exposure, nanoparticles induce toxic effects such as production of oxidative stress at the exposure site, inflammation, DNA damage, and cell death [ 87 , 88 ]. For instance, exposure of human neuroblastoma (Sh-sy5y) cells to inorganic nanoparticles, such as titanium dioxide, silica dioxide, and silver are associated with induction of neurotoxicity, membrane damage, reaction oxygen specie formation, decrease in cell viability, and autophagy dysfunction [ 40 ]. Similarly, exposure to carbon-based nanoparticles such as single and multi-walled carbon nanotubes reduce cell viability, as well as induce changes in cell structure, cell cycle, and cell-to-cell interactions in human lung epithelial cells (BEAS-2B) [ 107 ].

The environmental impact of nanoparticles

The findings of this scoping review indicate a gap in the literature regarding environmental impact of nanoparticles. Out of the 117 included studies, only 5 had assessed the environmental impact of exposure to nanoparticles. This significant gap in the scientific literature has been highlighted by authors such as Bundschuh et al. [ 157 ]. The growing production and usage of nanoparticles has undoubtedly led to a diversification of emission sources into both the aquatic and soil environment. Nanoparticles enter the environment mainly through three emission scenarios: a) released during production of nano-enabled products and raw materials, b) during application, and c) following disposal of products containing nanoparticles [ 158 ]. These emissions occur either indirectly through systems such as landfills or wastewater treatment plants, or directly to the environment. Nonetheless, nanoparticles are mostly released during the application phase and following disposal [ 159 ]. Indeed, during production, only about 2% of the production volume is emitted [ 160 ]. The studies in this review used biomarkers such as soil samples and soybean seeds, zebrafish larvae, fish, and Daphnia magna neonates. This finding is in line with a previous review by Bundschuh et al. [ 157 ], which explored the effects of nanoparticles on the environment.

Limitations of the review

In this review, every effort was made to reduce bias. The search strategy was developed by experts of the review team with many years of experience in conducting systematic/scoping reviews. A comprehensive search of multiple relevant databases and other resources was conducted by one review author (EAK) and a rerun of the searches was done after 4 weeks of the initial search. Two authors (EAK and RF or PB and SH) independently screened the search results, and disagreements between reviewers were resolved by FVZ or TP.

The main limitation of this review is that the searches were limited to studies published in the English language. This may have led to the exclusion of potentially relevant papers published in other languages. Also, searches were restricted to studies published from the year 2000, which may have led to the omission of potentially relevant papers.

Conclusions

This review has provided an extensive synthesis of the current literature on the effects of nanoparticles on human health and the environment. The review has shown that while nanoparticles are beneficial in a range of applications, they pose significant threats to humans and the environment. Through the use of several biological models and biomarkers (e.g., human bronchial epithelial cells (Beas-2), soil samples, and soybean seeds), the included studies revealed the toxic effects of nanoparticles, with the most investigated nanoparticles being Zinc Oxide, MWCNTs, Titanium Dioxide, Cerium Oxide, SWCNTs, Ferric Oxide, and Silicon Dioxide. The main health impacts of nanoparticles identified in this review are decreased cell viability, cell death, reactive oxygen species generation, production of oxidative stress (dose-dependent), DNA damage, apoptosis, and induction of inflammatory responses.

This review has revealed a significant gap in the scientific literature regarding environmental impact of nanoparticles of all types. Future studies should be directed at investigating the impact of the various types of nanoparticles on the aquatic, terrestrial, and soil environment. The findings from this review have also shown limited data regarding the relative effectiveness of immortalised cell lines and primary cells as biomarkers in nano-safety studies. Future research should focus on evaluating the effectiveness of these two types of cells, in order to determine the cell that can be used as a reliable biomarker for nano-safety studies. There is also the need for future studies in this area to focus on exploring the toxic effects of Platinum, Gold, Magnesium Oxide, Molybdenum Trioxide, Tungsten trioxide, and Carbon Black nanoparticles, as findings from this review has shown that these nanoparticles are least researched. The findings of this review will be useful to policy makers and stakeholders in assessing the potential effects of nanoparticles.

Availability of data and materials

All data generated or analysed during this study are included in this published article and in the presented supplementary material file.

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Acknowledgements

We would like to thank Daphne Silva Pino and Romana Petry for their contribution at the initial stages of this research.

This research was funded through the GRUN project (Towards the first implementation of groundwater remediation using nanotechnology in Brazil) as part of UKRI’s Global Challenges Research Fund (GCRF) and a grant from the São Paulo Research Foundation (FAPESP) (Grant 17/20308–0).

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Raoul Djou Fopa, Saeed Harati & Tannaz Pak

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Elizabeth Adjoa Kumah: Conceptualization, Methodology, Investigation, Formal analysis, Validation, Supervision, Writing—Original Draft, Writing—Review & Editing, Raoul Djou Fopa: Investigation, Data Curation, Saeed Harati: Investigation, Data Curation, Paul Boadu: Investigation, Data Curation, Formal analysis, Fatemeh Vida Zohoori: Conceptualization, Methodology, Validation, Supervision, Writing—Review & Editing, Funding acquisition, Tannaz Pak: Conceptualization, Methodology, Validation, Supervision, Writing—Review & Editing, Funding acquisition. The author(s) read and approved the final manuscript.

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Kumah, E.A., Fopa, R.D., Harati, S. et al. Human and environmental impacts of nanoparticles: a scoping review of the current literature. BMC Public Health 23 , 1059 (2023). https://doi.org/10.1186/s12889-023-15958-4

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Materials Horizons

Two decades of ceria nanoparticles research: structure, properties and emerging applications.

Cerium oxide nanoparticles (CeNPs) are versatile materials with unique and unusual properties that vary depending on their surface chemistry, size, shape, coating, oxidation states, crystallinity, dopant, structural and surface defects. This review details advances made over the past twenty years in the development of CeNPs and ceria-based nanostructures, the structural determinants affecting their activity, and translation of these distinct features into applications. The two-oxidation states of nanosized CeNPs (Ce3+/Ce4+) coexisting at the nanoscale level, facilitate formation of oxygen vacancies and defect states which confer extremely high reactivity and oxygen buffering capacity, and the ability to act as catalysts for oxidation and reduction reactions. However, the method of synthesis, surface functionalization, surface coating and defects are important factors in determining their properties. This review highlights the key properties of CeNPs, their synthesis, interactions and reaction pathways, and provides examples of emerging applications. Due to their unique properties, CeNPs have become quintessential candidates for catalysis, chemical mechanical planarization (CMP), sensing, biomedical applications and environmental remediation, with tremendous potential to create novel products and translational innovations in a wide range of industries. This review highlights the timely relevance and the transformative potential of these materials in addressing societal challenges and driving technological advancements across these fields.

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Nanoparticle classification, physicochemical properties, characterization, and applications: a comprehensive review for biologists

• Nadeem Joudeh 1 &
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Interest in nanomaterials and especially nanoparticles has exploded in the past decades primarily due to their novel or enhanced physical and chemical properties compared to bulk material. These extraordinary properties have created a multitude of innovative applications in the fields of medicine and pharma, electronics, agriculture, chemical catalysis, food industry, and many others. More recently, nanoparticles are also being synthesized ‘biologically’ through the use of plant- or microorganism-mediated processes, as an environmentally friendly alternative to the expensive, energy-intensive, and potentially toxic physical and chemical synthesis methods. This transdisciplinary approach to nanoparticle synthesis requires that biologists and biotechnologists understand and learn to use the complex methodology needed to properly characterize these processes. This review targets a bio-oriented audience and summarizes the physico–chemical properties of nanoparticles, and methods used for their characterization. It highlights why nanomaterials are different compared to micro- or bulk materials. We try to provide a comprehensive overview of the different classes of nanoparticles and their novel or enhanced physicochemical properties including mechanical, thermal, magnetic, electronic, optical, and catalytic properties. A comprehensive list of the common methods and techniques used for the characterization and analysis of these properties is presented together with a large list of examples for biogenic nanoparticles that have been previously synthesized and characterized, including their application in the fields of medicine, electronics, agriculture, and food production. We hope that this makes the many different methods more accessible to the readers, and to help with identifying the proper methodology for any given nanoscience problem.

Nano etymology

The prefix nano is derived from the Greek word nanos, “a dwarf”. In 1947, at the 14th conference of the International Union of Pure and Applied Chemistry (IUPAC), the prefix nano was officially adopted to describe the one-billionth part (10 –9 ) of a unit Footnote 1 . In scientific literature, the prefix nano has been adopted as a popular label in many fields of modern science to describe small entities and processes. These terms include, but are not limited to nanoscience, nanotechnology, nanorobots, nanomagnets, nanoelectronics, nanoencapsulation, etc. [ 1 ]. In all of these cases, the prefix nano is used to describe “very small” entities or processes, most often at actual nanometer scale.

Definitions

Nanoscience is a branch of science that comprises the study of properties of matter at the nanoscale, and particularly focuses on the unique, size-dependent properties of solid-state materials [ 2 ]. Nanotechnology is the branch that comprises the synthesis, engineering, and utilization of materials whose size ranges from 1 to 100 nm, known as nanomaterials [ 3 ]. The birth of nanoscience and nanotechnology concepts is usually linked to the famous lecture of Nobel laureate Richard Feynman at the 1959 meeting of the American Physical Society, ‘‘There’s Plenty of Room at the Bottom’’ [ 4 ]. However, the use of nanotechnology and nanomaterials goes back in history long before that.

History of nanotechnology

Long before the era of nanotechnology, people were unknowingly coming across various nanosized objects and using nano-level processes. In ancient Egypt, dyeing hair in black was common and was for a long time believed to be based on plant products such as henna [ 5 ]. However, recent research on hair samples from ancient Egyptian burial sites showed that hair was dyed with paste from lime, lead oxide, and water [ 6 ]. In this dyeing process, galenite (lead sulfide, PbS) nanoparticles are formed. The ancient Egyptians were able to make the dyeing paste react with sulfur (part of hair keratin) and produce small PbS nanoparticles which provided even and steady dyeing.

Probably the most famous example for the ancient use of nanotechnology is the Lycurgus Cup (fourth century CE). This ancient roman cup possesses unusual optical properties; it changes its color based on the location of the light source. In natural light, the cup is green, but when it is illuminated from within (with a candle), it becomes red. The recent analysis of this cup showed that it contains 50–100 nm Au and Ag nanoparticles [ 7 ], which are responsible for the unusual coloring of the cup through the effects of plasmon excitation of electrons [ 8 ]. The ancient use of nanotechnology does not stop here, in fact, there is evidence for the early use of nanotechnology processes in Mesopotamia, Ancient India, and the Maya [ 9 , 10 ].

Why nanomaterials are different

Today, due to their unique properties, nanomaterials are used in a wide range of applications, such as catalysis, water treatment, energy storage, medicine, agriculture, etc . [ 11 , 12 , 13 ]. Two main factors cause nanomaterials to behave significantly differently than the same materials at larger dimensions: surface effects and quantum effects [ 14 ]. These factors make nanomaterials exhibit enhanced or novel mechanical, thermal, magnetic, electronic, optical, and catalytic properties [ 1 , 15 , 16 ].

Nanomaterials have different surface effects compared to micromaterials or bulk materials, mainly due to three reasons; (a) dispersed nanomaterials have a very large surface area and high particle number per mass unit, (b) the fraction of atoms at the surface in nanomaterials is increased, and (c) the atoms situated at the surface in nanomaterials have fewer direct neighbors [ 1 , 14 ]. As a consequence of each of these differences, the chemical and physical properties of nanomaterials change compared to their larger-dimension counterparts. For instance, having fewer direct neighbor atoms for the atoms situated at the surface results in lowering the binding energy per atom for nanomaterials. This change directly affects the melting temperature of nanomaterials following the Gibbs–Thomson equation, e.g., the melting point of 2.5 nm gold nanoparticles is 407 degrees lower than the melting point of bulk gold [ 14 ]. Larger surface areas and larger surface-to-volume ratios generally increases the reactivity of nanomaterials due to the larger reaction surface [ 1 ], as well as resulting in significant effects of surface properties on their structure [ 17 ]. The dispersity of nanomaterials is a key factor for the surface effects. The strong attractive interactions between particles can result in the agglomeration and aggregation of nanomaterials, which negatively affects their surface area and their nanoscale properties [ 18 ]. Agglomeration can be prevented by increasing the zeta potential of nanomaterials (increasing the repulsive force) [ 19 ], optimizing the degree of hydrophilicity/hydrophobicity of the nanomaterial, or by optimizing the pH and the ionic strength of the suspension medium [ 20 ].

Nanomaterials display distinct size-dependent properties in the 1–100 nm range where quantum phenomena are involved. When the material radius approaches the asymptotic exciton Bohr radius (the separation distance between the electron and hole), the influence of quantum confinement becomes apparent [ 17 ]. In other words, by shrinking the size of the material, quantum effects become more pronounced, and nanomaterials become quantal. Those quantum structures are physical structures where all the charge carriers (electrons and holes) are confined within the physical dimensions [ 21 ]. As a result of quantum confinement effects, for instance, some non-magnetic materials in bulk such as palladium, platinum, and gold become magnetic in the nanoscale [ 14 ]. Quantum confinement can also result in significant changes in electron affinity or the ability to accept or donate electrical charges, which is directly reflected on the catalytic properties of the material. For example, the catalytic activity of cationic platinum clusters in N 2 O decomposition is dictated by the number of atoms in the cluster. 6–9, 11, 12, 15, and 20 atom-containing clusters are very reactive, while clusters with 10, 13, 14, and 19 atoms have low reactivity [ 14 ].

Classification of nanomaterials

The key elements of nanotechnology are the nanomaterials. Nanomaterials are defined as materials where at least one of their dimensions is in the nanoscale, i.e. smaller than 100 nm [ 22 ]. Based on their dimensionalities, nanomaterials are placed into four different classes, summarized in Fig.  1 .

Zero-dimensional nanomaterials (0-D): the nanomaterials in this class have all their three dimensions in the nanoscale range. Examples are quantum dots, fullerenes, and nanoparticles.

One-dimensional nanomaterials (1-D): the nanomaterials in this class have one dimension outside the nanoscale. Examples are nanotubes, nanofibers, nanorods, nanowires, and nanohorns.

Two-dimensional nanomaterials (2-D): the nanomaterials in this class have two dimensions outside the nanoscale. Examples are nanosheets, nanofilms, and nanolayers.

Three-dimensional nanomaterials (3-D) or bulk nanomaterials: in this class the materials are not confined to the nanoscale in any dimension. This class contains bulk powders, dispersions of nanoparticles, arrays of nanowires and nanotubes, etc .

Nanomaterials classification based on dimensionality

Nanoparticles (NPs)

The International Organization for Standardization (ISO) defines nanoparticles as nano-objects with all external dimensions in the nanoscale, where the lengths of the longest and the shortest axes of the nano-object do not differ significantly. If the dimensions differ significantly (typically by more than three times), terms such as nanofibers or nanoplates maybe preferred to the term NPs Footnote 2 .

NPs can be of different shapes, sizes, and structures. They can be spherical, cylindrical, conical, tubular, hollow core, spiral, etc., or irregular [ 23 ]. The size of NPs can be anywhere from 1 to 100 nm. If the size of NPs gets lower than 1 nm, the term atom clusters is usually preferred. NPs can be crystalline with single or multi-crystal solids, or amorphous. NPs can be either loose or agglomerated [ 24 ].

NPs can be uniform, or can be composed of several layers. In the latter case, the layers often are: (a) The surface layer, which usually consists of a variety of small molecules, metal ions, surfactants, or polymers. (b) The shell layer, which is made of a chemically different material from the core layer. (c) The core layer, which is the central portion of the NP [ 25 ].

Classification of NPs

Based on their composition, NPs are generally placed into three classes: organic, carbon-based, and inorganic [ 23 ].

Organic NPs

This class comprises NPs that are made of proteins, carbohydrates, lipids, polymers, or any other organic compounds [ 26 ]. The most prominent examples of this class are dendrimers, liposomes, micelles, and protein complexes such as ferritin (shown in Fig.  2 ). These NPs are typically non-toxic, bio-degradable, and can in some cases, e.g., for liposomes, have a hollow core. Organic NPs are sensitive to thermal and electromagnetic radiation such as heat and light [ 23 ]. In addition, they are often formed by non-covalent intermolecular interactions, which makes them more labile in nature and offers a route for clearance from the body [ 27 ]. There are different parameters that determine the potential field of application of organic NPs, e.g., composition, surface morphology, stability, carrying capacity, etc . Today, organic NPs are mostly used in the biomedical field in targeted drug delivery [ 23 ] and cancer therapy [ 28 ].

Types of organic NPs. A Dendrimers; B liposomes; C micelles; and D ferritin

Carbon-based NPs

This class comprises NPs that are made solely from carbon atoms [ 23 ]. Famous examples of this class are fullerenes, carbon black NPs, and carbon quantum dots (shown in Fig.  3 ). Fullerenes are carbon molecules that are characterized by a symmetrical closed-cage structure. C 60 fullerenes consist of 60 carbon atoms arranged in the shape of a soccer ball [ 29 ], but also other types of fullerenes such as C 70 and C 540 fullerenes have been described [ 30 ]. Carbon black NPs are grape-like aggregates of highly fused spherical particles [ 31 ]. Carbon quantum dots consist of discrete, quasi-spherical carbon NPs with sizes below 10 nm [ 32 ]. Carbon-based NPs unite the distinctive properties of sp 2 -hybridized carbon bonds with the unusual physicochemical properties at the nanoscale. Due to their unique electrical conductivity, high strength, electron affinity, optical, thermal, and sorption properties [ 25 , 33 ], carbon-based NPs are used in a wide range of application such as drug delivery [ 34 ], energy storage [ 35 ], bioimaging [ 36 ], photovoltaic devices, and environmental sensing applications to monitor microbial ecology or to detect microbial pathogens [ 33 ]. Nanodiamonds and carbon nano onions are more complex, carbon-based NPs. Due to their characteristic low toxicity and biocompatibility, they are used in drug delivery and tissue engineering applications [ 37 , 38 ].

Different types of carbon-based NPs. A C 60 fullerene; B carbon black NPs; and C carbon quantum dots

Inorganic NPs

This class comprises NPs that not made of carbon or organic materials. The typical examples of this class are metal, ceramic, and semiconductor NPs. Metal NPs are purely made of metal precursors, they can be monometallic, bimetallic [ 39 ], or polymetallic [ 40 ]. Bimetallic NPs can be made from alloys or formed in different layers (core–shell) [ 39 ]. Due to the localized surface plasmon resonance characteristics, these NPs possess unique optical and electricals properties [ 25 ]. In addition, some metal NPs also possess unique thermal, magnetic, and biological properties [ 23 ]. This makes them increasingly important materials for the development of nanodevices that can be used in numerous physical, chemical, biological, biomedical, and pharmaceutical applications [ 41 , 42 ] (these applications are discussed in detail later in the applications section of the review). In present days, the size-, shape-, and facet-controlled synthesis of metal NPs is important for creating cutting-edge materials [ 43 ].

Semiconductor NPs are made of semiconductor materials, which possess properties between metals and non-metals. These NPs possess unique wide bandgaps and show significant alteration in their properties with bandgap tuning compared to bulk semiconductor materials [ 25 ]. As a result, these NPs are important materials in photocatalysis, optic, and electronic devices [ 44 , 45 ]. Ceramic NPs are inorganic solids made of carbonates, carbides, phosphates, and oxides of metals and metalloids, such as titanium and calcium [ 46 ]. They are usually synthesized via heat and successive cooling and they can be found in amorphous, polycrystalline, dense, porous or hollow forms [ 25 ]. They are mainly used in biomedical applications due to their high stability and high load capacity [ 47 ]. Nevertheless, they are also used in other applications such as catalysis, degradation of dyes, photonics and optoelectronics [ 46 , 48 ].

Physicochemical properties of NPs

As mentioned earlier, NPs can be used in a long list of applications due to their unique physical and chemical properties that do not exist in their larger-dimension counterparts of the same materials. The following sections summarize the most import physicochemical properties that are changing on the nanoscale.

Mechanical properties

Mechanical properties refer to the mechanical characteristics of a material under different conditions, environments, and various external forces. As for traditional materials, the mechanical properties of nanomaterials generally consist of ten parts: strength, brittleness, hardness, toughness, fatigue strength, plasticity, elasticity, ductility, rigidity, and yield stress [ 49 ]. Most inorganic, non-metallic materials are brittle materials and do not have significant toughness, plasticity, elasticity, or ductility properties. Organic materials on the other hand, are flexible materials and do not necessarily have brittleness and rigidity properties.

Due to surface and quantum effects, NPs display different mechanical properties compared to bulk materials [ 49 ]. For example, conventional FeAl powder which is composed of microparticles (larger than 4 µm), is brittle, while ultrafine FeAl alloy powder displays a good combination of strength and ductility as well as enhanced plasticity [ 50 ]. These new properties are believed to arise due to the diverse interaction forces between NPs or between them and a surface. The most important interaction forces involved are van der Waals forces, which consist of three parts, Keesom force, Debye force, and London force [ 51 , 52 , 53 ]. Other relevant interaction forces are electrostatic and electrical double layer forces, normal and lateral capillary forces, solvation, structural, and hydration forces [ 54 ].

There are different theories on how the interaction forces between NPs give them new mechanical properties, such as the DLVO (Derjaguin–Landau–Verwey–Overbeek) theory, JKR (Johnson–Kendall–Roberts) theory, and DMT (Derjaguin–Muller–Toporov) theory. The DLVO theory combines the effects of van der Waals attraction and electrostatic repulsion to describe the stability of colloidal dispersions [ 54 ]. This theory can explain many phenomena in colloidal science, such as the adsorption and the aggregation of NPs in aqueous solutions and the force between charged surfaces interacting through a liquid medium [ 55 , 56 ]. Nevertheless, the DLVO theory is inadequate for the colloidal properties in the aggregated state [ 54 ].

When the size of objects decreases to the nanoscale, the surface forces become a major player in their adhesion, contact, and deformation behaviors. The JRK theory is applicable to easily deformable, large bodies with high surface energies, where it describes the domination of surface interactions by strong, short-range adhesion forces. In contrast to this, the DMT theory is applicable to very small and hard bodies with low surface energies, where it describes the adhesion being caused by the presence of weak, long-range attractive forces. Although the DLVO, JKR and DMT theories have been widely used to describe and study the mechanical properties of NPs [ 57 , 58 ], it is still a matter of debate whether or not continuum mechanics can be used to describe a particle or collection of particles at the nanometer scale [ 54 ].

Thermal properties

Heat transfer in NPs primarily depends on energy conduction due to electrons as well as photons (lattice vibration) and the scattering effects that accompany both [ 59 ]. The major components of thermal properties of a material are thermal conductivity, thermoelectric power, heat capacity, and thermal stability [ 59 , 60 ].

NP size has a direct impact on electrical and thermal conductivity of NPs [ 60 ]. As the NP size decreases, the ratio of particle surface area respective to its volume increases hyperbolically [ 60 ]. Since the conduction of electrons is one of the two main ways in which heat is transferred, the higher surface-to-volume ratio in NPs provides higher number of electrons for heat transfer compared to bulk materials [ 61 ]. Moreover, thermal conductivity in NPs is also promoted by microconvection, which results from the Brownian motion of NPs [ 62 ]. Nevertheless, this phenomenon only happens when solid NPs are dispersed in a liquid (generating a Nanofluid) [ 63 ]. As an example, the addition of Cu NPs to ethylene glycol enhances the thermal conductivity of the fluid up to 40% [ 64 ].

The thermoelectric power of a material depends on its Seebeck coefficient and electrical conductivity ( \(P={S}^{2}\sigma \) , where P is thermoelectric power, S is the Seebeck coefficient, and \(\sigma \) is the electrical conductivity). The scattering of NPs in bulk materials (doping) is known to enhance the thermoelectric power factor [ 65 ]. This enhancement could come from the enhancement of the Seebeck coefficient or the enhancement of electrical conductivity. The embedding of size-controlled NPs in bulk thermoelectric materials helps to reduce the lattice thermal conductivity and enhances the Seebeck coefficient due to electron energy filtering [ 66 , 67 ]. Generally, the enhancement of electrical conductivity is accompanied by the reduction of the Seebeck coefficient and vice versa [ 65 ] However, the doping of InGaAlAs material with 2–3 nm Er NPs resulted in the significant increase of thermoelectric power of the material through the enhancement of the conductivity while keeping the Seebeck coefficient unchanged [ 65 ]. Depending on NP size, volume fraction, and band offset, a NP-doped sample can either enhance or suppress the electrical conductivity in comparison with undoped bulk sample.

Experimental studies have shown that the heat capacity of NPs exceeds the values of analogous bulk materials by up to 10% [ 68 ], e.g. in the case of Al 2 O 3 and SiO 2 NPs [ 69 , 70 ]. The major contribution to heat capacity at ambient temperatures is determined by the vibration degrees of freedom, i.e., the peculiarities of phonon spectra (vibrational energy that arises from oscillating atoms within a crystal) are responsible for the anomalous behavior of heat capacity of NPs [ 68 ]. NPs usually exhibit a significant decrease in melting temperature compared to their analogous bulk materials [ 71 ]. The main reason for this phenomenon is that the liquid/vapor interface energy is generally lower than the average solid/vapor interface energy [ 72 ]. When the particle size decreases, its surface-to-volume ratio increases, and the melting temperature decreases as a result of the improved free energy at the particle surface [ 73 ]. For instance, the melting temperature of 3 nm Au NPs is 300 degrees lower than the melting temperature of bulk gold [ 14 ]. In addition, NP composition plays an important role in thermal stability. For example, the thermal stability of Au in Au 0.8 Fe 0.2 is significantly higher than of pure Au or Au 0.2 Fe 0.8 [ 74 ]. Generally, bimetallic alloy NPs show higher thermal stabilities and melting temperatures than monometallic NPs due to the alloying effect [ 75 , 76 ].

Magnetic properties

All magnetic compounds include a ‘magnetic element’ in their formula, i.e., Fe, Co, or Ni (at ambient temperatures). There are only three known exceptions that are made from mixed diamagnetic elements, Sc 3 In, ZrZn 2 , and TiBe 2-x Cu x [ 77 , 78 , 79 , 80 ]. Otherwise, elements such as Pd, Au, or Ag are diamagnetic. This all changes in the nanoscale. Several materials become magnetic in the form of NPs as a result of uneven electronic distribution [ 25 ]. For instance, FeAl is not magnetic in bulk but in the form of NPs, it is becomes magnetic [ 50 ], other examples include Pd and Au [ 81 ]. In bulk materials, the key parameters for determining magnetic properties are composition, crystallographic structure, magnetic anisotropy, and vacancy defects [ 82 , 83 ]. However, on the nanoscale, two more important parameters are strongly involved, i.e., size and shape [ 84 ].

One of the interesting size-dependent phenomena of NPs is superparamagnetism [ 84 ]. As the size of the NPs decreases, the magnetic anisotropy energy per NP decreases. The magnetic anisotropy energy is the energy keeping the magnetic moment in a particular orientation. At a characteristic size for each type of NPs, the anisotropy energy becomes equal to the thermal energy, which allows the random flipping of the magnetic moment [ 85 ], in this case, the NP is defined as being superparamagnetic [ 86 ]. Superparamagnetic NPs display high magnetization only in the presence of a magnetic field, and once it is removed they do not retain any magnetization [ 87 ]. Superparamagnetism was long believed to form only in small ferromagnetic or ferrimagnetic NPs [ 88 ], but interestingly, other paramagnetic materials show magnetism in the nanoscale too [ 81 ].

NP size effects can also be observed in changes in magnetic coercivity, i.e., the resistance of a magnetic material to changes in magnetization (Fig.  4 ). In contrast to large particles or bulk materials, which possess multiple magnetic domain structures, small NPs possess single magnetic domain structures below a certain critical radius (r c ), where all magnetic spins in the NP align unidirectionally (blue arrows in Fig.  4 ). However, the NP radius has to be lower than the threshold radius for superparamagnetism (r sp ) in order to be superparamagnetic [ 89 ]. In the single-domain regime, between r sp and r c , the magnetic coercivity increases as the size of the NP increases until it reaches the maximum at r c [ 84 ]. In this size regime, due to the high magnetic coercivity, the NPs behave similarly as their larger dimension counterparts despite having a single domain structure, i.e., they become ferromagnetic for ferromagnetic materials or paramagnetic for paramagnetic materials etc . Above r c , the magnetic coercivity starts to decrease when multiple magnetic domains are formed in a single NP. The critical radius represents the size where it is energetically favored for the NP to exist without a domain wall [ 86 ]. The calculated critical radii for some common magnetic materials are 35 nm of Ni, 8 nm for Co, and 1 nm for Fe [ 90 ]. Above that point, multi-domain magnetism begins in which a smaller reversal magnetic field is required to make the net magnetization zero [ 84 ].

The change in magnetic coercivity of NPs as a function of particle radius. Figure adapted from Kalubowilage et al., 2019 [ 89 ]. rc critical radius, rsp threshold radius for superparamagnetism

The second key parameter for determining the magnetic properties of NPs is the shape of NPs. In comparison to the size parameter, there is significant less research on the effect of shape on the magnetic properties of NPs having the same volume [ 86 ]. However, large differences in coercivity were found between a set of cubic and spherical CoFe 2 O 4 NPs [ 91 ]. Unlike the curved topography in spherical CoFe 2 O 4 NPs, cubic CoFe 2 O 4 NPs have fewer missing oxygen atoms, and it was hypothesized that this led to less surface pinning and to lower coercivity for the cubic structures [ 86 ]. Other studies also found differences in magnetism between spherical and cubic Fe 3 O 4 NPs [ 92 , 93 ].

Similar to bulk materials, the composition also affects the magnetism of NPs. The magnetocrystalline phase of the NP is significant in determining its magnetic coercivity [ 94 ]. This effect can be observed in magnetic bimetallic core–shell or alloy NPs with anisotropic crystalline structures. For example, Co@Pt core–shell NPs composed of an isotropically structured face-centered cubic Co core and a non-magnetic Pt shell exhibit superparamagnetic behavior with zero coercivity at room temperature [ 95 ]. In general, the compositional modification of NPs by the adoption of magnetic dopants is known to significantly change the magnetism of NPs [ 96 ].

Electronic and optical properties

Metallic and semiconductor NPs possess interesting linear absorption, photoluminescence emission, and nonlinear optical properties due to the quantum confinement and localized surface plasmon resonance (LSPR) effect [ 97 , 98 ]. LSPR phenomena arise when the incident photon frequency is constant with the collective excitation of the conductive electrons [ 25 ].Due to this phenomenon, noble metal NPs exhibit a strong size-dependent UV–visible extinction band that is not present in the spectra of bulk metals. Generally, the optical properties of NPs depend on the size, shape, and the dielectric environment of the NPs [ 99 ].

The collective excitations of conductive electrons in metals are called plasmons [ 100 ]. Depending on the boundary conditions, bulk plasmons, surface-propagating plasmons, and surface-localized plasmons are distinguished (Fig.  5 A–C). Because of their longitudinal nature, the bulk plasmons cannot be excited by visible light. The surface-propagating plasmons propagate along metal surfaces in a waveguide-like fashion [ 98 ]. In the case of NPs, when they are irradiated by visible light, the oscillating electric field causes the conductive electrons to oscillate coherently. When the electron cloud is displaced relative to the nuclei, a restoring force rises from Coulomb attraction between electrons and nuclei that results in oscillation of the electron cloud relative to the nuclear framework [ 99 ]. This creates uncompensated charges at the NP surface (Fig.  5 D). As the main effect producing the restoring force is the polarization of the NP surface, these oscillations are called surface plasmons and have a well-defined resonance frequency [ 98 ].

Graphical illustration of the types of plasmons. A bulk; B surface propagating; and C surface localized plasmons (adapted from Khlebtsov et al., 2010 [ 98 ]). D graphical illustration of the localized surface plasmon resonance (LSPR) in NPs (adapted from Kelly et al., 2003 [ 99 ])

Experimental studies on Ag NPs showed significant differences in their optical properties based on the size of NPs. For Ag NPs with 30 nm radius, the main extinction peak was at 369 nm wavelength, while for Ag NPs with 60 nm radius, a totally different behavior was observed [ 99 ]. The same researchers found that the shape of the NPs also is critical for the optical properties, the plasmon resonance wavelength shifts to the red as the NPs become more oblate [ 99 ], demonstrating that plasmon resonance strongly depend on NPs shape. With respect to the dielectric environment of the NPs, both the surrounding solvent and the support (substrate) were found to be critical for the optical properties. For Ag NPs, both experimental and theorical studies on the effect of surrounding solvent show that plasmon wavelength linearly depends on the refractive index of the solvent [ 99 , 101 ]. At the same time, 10 nm Ag NPs supported on mica substrates displayed LSPR wavelength shifts to the red compared to unsupported NPs [ 102 ]. The biogenic synthesis of NPs can also improve the optical properties. Biologically produced CeO 2 NPs using Simarouba glauca leave extract were found to have different absorption bands and higher band gap energies compared to chemically produced CeO 2 NPs. These superior optical properties were attributed to the better crystallinity and small size of biogenic NPs compared to chemical NPs [ 103 ]. Biogenic NPs can also offer higher photocatalytic activities, e.g., ZnO NPs produced by Plectranthus amboinicus leaf extract had higher photocatalytic activity in the photodegradation of methyl red under UV illumination compared to chemical produced ZnO NPs [ 104 ].

Catalytic properties

Nano-catalysis, i.e., the use of NPs as catalysts, is a quickly evolving field within chemical catalysis. Significantly enhanced or novel catalytic properties such as reactivity and selectivity have been reported for NP catalysts compared to their bulk analogues. The catalytic properties of NPs depend on the size, shape, composition, interparticle spacing, the oxidation state, and the support of the NPs [ 76 ].

The dependency of catalytic activity on the size of NPs is well studied. The relation is an inverse one, i.e., the smaller the NPs the more catalytically active they are. This relationship was found e.g., in the electro-catalysis oxidation of CO by size-selected Au NPs (1.5, 4, and 6 nm) deposited on indium tin oxide. The researchers observed that the smallest NPs provided the highest normalized current densities [ 105 ]. The same relationship was also found in several other studies [ 106 , 107 , 108 , 109 , 110 ]. Goodman et al., 1998 [ 111 ] speculated originally that this behavior could be attributed to quantum-size effects generated by the confinement of electrons within a small volume. Later, size-dependent changes in the electronic structure of the clusters [ 112 ] and the resulting larger number of low-coordinated atoms available for interaction by the larger surface-to-volume ratios with smaller NPs were discussed [ 76 ].

The shape is also known to affect the reactivity and selectivity of the NPs. For the oxidation of CO by Au NPs, hemispherical NPs were found to be more active than spherical ones [ 113 ]. For the oxidation of styrene by Ag NPs, nanocubes were found to be fourteen times more efficient than nanoplates and four times more efficient than nanospheres [ 114 ]. The reason for these dramatical changes are attributed to the increase/decrease in the relative area of the catalytically active surface facets [ 76 ] or to the differences in stability for different NP shapes [ 115 ].

As for composition, several studies have shown that the use of alloys in NPs can enhance the catalytic activity as a result of the alloying effect causing changes in the electronic properties of the catalyst, decreasing poisoning effects, and providing distinct selectivities [ 76 ]. For example, the alloying of Pt with other metals such as Ru, Ni, and Co, was reported to enhance the hydrogenation and oxygen reduction activity of the NP catalyst material, as well as enhancing the resistance against CO poisoning [ 116 , 117 , 118 ]. However, the alloying of Pt with Fe, Ru, and Pd, resulted in reduced reactivity for methanol decomposition [ 119 ]. This reduction in reactivity was explained by the possible occupation of the surface with the addition metal atoms, since pure Fe, Ru, and Pd clusters are less reactive for methanol decomposition than similarly-sized pure Pt clusters. In general, the change in the composition of NPs changes the electronic structure of metal surfaces by the formation of bimetallic bonds as well as the modification of metal–metal bond lengths [ 76 ]. In addition, the charge-transfer phenomenon between different metals may favorably change the binding energy of adsorbents, lower the barriers for specific chemical reactions, and enhance resistance against poisoning [ 120 , 121 , 122 ].

The catalytic activity and stability of 2 nm Au NPs dispersed on polycrystalline TiC films displayed a strong dependence on interparticle spacing. In this study, Au NPs having two different interparticle spacing (30 and 80 nm) were analyzed by Thermal Desorption Spectroscopy. It was found that the sample with smaller interparticle spacing was poisoned and subsequently deactivated while the sample with longer interparticle spacing showed longer lifetime [ 123 ]. At the same time, the oxidation state of NPs was shown to affect the catalytic activities. Ru NPs under rich O 2 conditions and moderate temperatures oxidize and form RuO 2 , the reaction of CO oxidation was found to occur on the metal oxide surface not the metal surface [ 124 ]. A similar effect on CO oxidation was also observed with Pt NPs in which the reactivity of PtO 2 was found to be higher than Pt [ 125 ]. The reaction of CO oxidation was compared for several metal NPs (Ru, Pd, Ir, Os, and Pt) and their corresponding oxides, and the oxides were indeed more reactive than the metals [ 126 , 127 ]. The superior catalytic performance of RuO 2 over their metallic counterparts is generally agreed on, nevertheless, the same cannot be said for other catalytically active metals such as Pt [ 76 ]. In general, these differences in catalytic performance are attributed to the electron transfer processes at the metal/metal oxide interfaces. Consequently, the view that NP oxidation is an undesirable process that leads to the reduction of catalytic performance needs to be reconsidered [ 128 ].

An example for the effect of the support material is the role of the MgO support for Au NPs, where MgO was found to be important for CO oxidation and particularly, for controlling the rate of CO oxidation through oxygen vacancies [ 129 ]. Later, the process of electron charge transfer from oxygen vacancies at the metal-substrate interface of supported Au NPs was suggested to be an ideal environment for O 2 activation and oxidation reactions [ 130 ]. A similar behavior was also found in the decomposition of SO 2 and dissociation of water by Au NPs supported on CeO 2 , in which CeO 2 supports played a critical role [ 131 ]. The experiments showed that not only the chemical composition of the support affects the reactivity of the catalyst, but the crystal structure of the support, too [ 132 ]. Enhanced catalytic performance for CO oxidation and SO 2 dissociation have also been reported for Au NPs supported on metal carbides such as TiC [ 108 , 133 ]. In addition to enhanced catalytic reactivities, the support also plays an important role in NP stabilization [ 106 ], i.e., the stabilization of NPs against coarsening, the stabilization of metal oxides at the NP surface, and the stabilization of intermediate reactions species [ 76 ].

Characterization of NPs

The properties of NPs determine their potential applications. Hence, different methods and techniques are used for the analysis and characterization of the various physicochemical properties of NPs. Table 1 summarizes all characterization techniques mentioned in this review and shows what properties and features can be resolved by each technique.

Morphological and topographical characterization

The morphological and topographical features of NPs are of great interest since they influence most of the properties of NPs as described above. These features include the size, shape, dispersity, localization, agglomeration/aggregation, surface morphology, surface area, and porosity of the NPs. The following techniques are regularly used for the characterization of morphological and topographical features of NPs.

Electron microscopy (EM)

Scanning electron microscopy (SEM), scanning tunneling microscopy (STM), and transmission electron microscopy (TEM) are frequently employed for the analysis of NP size, shape, and surface. In SEM, an electron gun is used to produce a beam of electrons that is controlled by a set of lenses to follows a vertical path through the microscope until it hits the samples. Once the sample is hit by the beam, electrons and X-rays are ejected from the sample. Detectors are then used to collect the X-rays and scattered electrons in order to create a 3D image of the sample. SEM provides different information about the NPs such as size, shape, aggregation, and dispersion [ 134 ]. Similarly, TEM provides information about the size, shape, localization, dispersity, and aggregation of NPs in two-dimensional images [ 25 ]. TEM employs an electromagnetic lens that focuses a very fine beam of electrons into an ultrathin section of the sample. This beam passes through the specimen where the electrons either scatter or penetrate the sample and hit a fluorescent screen at the bottom of the microscope. The difference in electron densities is used for the contrast to create an image of the specimen. TEM can be also used for the characterization of NP crystal structure through the use of selected area electron diffraction (SAED), where the electron beam is focused on a selected area in the sample and the scattered electrons are used to obtain a diffraction pattern. STM is based on the phenomenon of quantum tunneling, where a metallic tip is brough very close to the sample surface and used to apply voltage. When voltage is applied, electrons from the sample surface are extracted creating an electrical current that is used to reconstruct an image of the surface with atomic resolution [ 135 ]. STM is mainly used to characterize the topography of NPs. For inorganic NPs, these techniques offer excellent approaches for the determination of morphological features of NPs. For organic NPs (or NPs coated with biological materials), these techniques require sophisticated sample preparations which constitute major restrictions to their use [ 136 ]. The sample preparation for these techniques might cause sample dehydration, which might lead e.g. to sample shrinking and aggregation [ 136 ].

Examples: TEM was used for the characterization of Ag NPs produced by Arbutus unedo leaf extract. In this example, the NPs have a spherical morphology with a uniform size of 30 nm. The NPs were found to agglomerate into small aggregates, each including 5–6 NPs. At the same time, the SAED approach was used to determine the crystal structure of the NPs. The majority of the NPs were found to be single crystalline cubic materials predominately oriented along their (111) direction [ 137 ]. For the characterization of Ag NPs produced by Diospyros kaki leaf extract, SEM helped to show that the NPs were also spherical and the size was 32 nm with some deviations [ 138 ]. STM is less frequently used for the characterization of biogenic NPs. The features of Ag NPs produced by lime, sweet-lime, and orange juices were compared using STM technique [ 139 ].

Dynamic light scattering (DLS)

This technique is a common approach for the analysis of NP size and size distribution. This approach involves the measurement of light interference based on the Brownian motion of NPs in suspension, and on the correlation of NP velocity (diffusion coefficient) with their size using Strokes-Einstein equation [ 140 ]. The size distribution range of NPs is shown as the polydispersity index, which is the output of an autocorrelation function [ 136 ]. The polydispersity index values lie between 0 and 1, where 0 represents a completely homogenous population and 1 represents a highly heterogeneous population. This technique also allows the analysis of non-spherical NPs through the use of multistage DLS [ 136 ]. This technique is also referred to as photon correlation spectroscopy (PCS) [ 141 ].

Examples: DLS was used to measure the size and the size distribution profile of a wide range of biogenic NPs. The average size of Ag NPs produced by Trichoderma koningii fungi was found to be around 25 nm and the size distribution profile was between 14 and 34 nm. The polydispersity index for those NPs was 0.681, which indicates that they are polydispersed [ 142 ]. While the average size of Ag NPs produced by potato ( Solanum tuberosum ) was found to be around 10–12 nm with a wider distribution profile between 3–65 nm [ 143 ]. In a different application, DLS was employed to study the size increase of biogenic MnO 2 NPs overtime, demonstrating that their size is 7.5 nm after 3 min of the initiation of the reaction, then their size grows overtime until it become 54 nm after 31 min [ 144 ].

Nanoparticle tracking analysis (NTA)

This method is used for the analysis of NP size in suspensions based on their Brownian motion. Like in DLS, the rate of NP movement is correlated with their size using Strokes-Einstein equation, allowing the measurement of size distribution profiles for NPs with 10–1000 nm diameter. Its advantage over DLS is that NP motion is analyzed by video. Individual positional changes of NPs are tracked in two dimensions, which are used to determine NP diffusion rates, and by knowing the diffusion coefficient, the hydrodynamic diameter of the particles can be calculated. In DLS, individual NPs are not visualized, but instead, the time-dependent intensity fluctuations caused by Brownian motion are used to calculate the polydispersity index [ 145 ]. NTA was found to be more precise for sizing monodisperse as well as polydisperse organic NPs compared to DLS [ 146 ].

Examples: NTA was used to measure the size and dispersity of Ag NPs produced by Camellia sinensis (green tea) powder, the NPs were found to be well dispersed in an aqueous medium with an average size of 45 ± 12 nm [ 147 ]. For Se NPs produced by lactic acid bacteria, NTA was employed to measure the size and the concentration of NPs. The average size was found to be 187 ± 56 nm with a concentration of (4.67 ± 0.30) × 10 9 Se NPs per ml [ 148 ].

Brunauer–Emmett–Teller (BET) method

This method is based on the adsorption and desorption principle developed by Stephen Brunauer, Paul Emmett, and Edward Teller, and it is considered one of the best methods for the analysis of NP surface area [ 25 ]. In BET analysis, a partial vacuum is created to produce adsorption between the sample and liquid N 2 (because the interaction between solid and gaseous phases is weak, the surface is cooled with liquid N 2 to obtain detectable amounts of adsorption). After the formation of adsorption monolayers, the sample is removed from the N 2 atmosphere and heated to cause the adsorbed N 2 to be released from the material (desorption) and quantified. The data collected is displayed in the form of isotherms (graphs representing the amount of N 2 adsorbed as a function of relative pressure at a constant temperature). The data is displayed in five isotherms where the information is used to determine the surface area of the sample [ 25 , 149 ]. Figure  6 graphically illustrates the principle of this method.

Principles of the BET and BJH methods. The BET method (steps 1–3) is based on the adsorption of nitrogen on the NP surface. After the formation of a monolayer, nitrogen is desorbed, and the surface area is calculated. The BJH method (steps 1, 2, 4, and 5) is based on the complete filling of NP pores with liquid nitrogen. When saturation is reached, nitrogen is desorbed, and pore size is calculated

Examples: The BET method was employed to measure the surface area of CeO 2 NPs produced by Eucalyptus globulus leaf extract. The surface area was found to be 40.96 m 2 /g of biogenic CeO 2 NPs, much higher than the commercial CeO 2 NPs (8.5 m 2 /g) [ 150 ]. BET was also used to measure the surface area of SiO 2 NPs produced by rice husk, CuO NPs produced by Leucaena leucocephala leaf extract, and Ag NPs produced by Acanthospermum hispidum leaf extract. In these examples, the surface area was 7.15 m 2 /g, 47.54 m 2 /g, and 9.91 m 2 /g, respectively [ 151 , 152 , 153 ].

Barrett–Joyner–Halenda (BJH) method

This method is based on the Barrett–Joyner–Halenda principle and is used for the determination of porosity (or pore size) of NPs. Similar to the BET method, this method also involves the use of N 2 gas to adsorb to the sample. In the BJH method, the process is extended so the gas condensates in the sample pores as pressure increases. The pressure is increased until a saturation point is achieved, at which all the pores of the sample are filled with liquid. Afterwards, the condensated gas is allowed to evaporate where the desorption data is calculated and correlated to the pore size using a modified Kelvin equation (Kelvin model of pore filling) [ 154 , 155 ]. Figure  6 graphically illustrates this method.

Examples: The BJH method was employed to study the pore size of a wide range of biogenic NPs, for instance, the pore size of CeO 2 NPs produced by Eucalyptus globulus leaf extract was found to be 7.8 nm [ 150 ], the pore size of CuO NPs produced by Leucaena leucocephala leaf extract was 2.13 nm [ 152 ], the pore size of SiO 2 NPs produced by rice husk and Ag NPs produced by Acanthospermum hispidum leaf extract were much larger, being 29.63 nm and 36.34 nm, respectively [ 151 , 153 ].

Structural and chemical characterization

The structural characterization of NPs and the study of their composition is of high interest due to the strong influence of these parameters on the physicochemical properties. The following techniques are commonly used for the analysis of NP composition, phase, crystallinity, functionalization, chemical state (oxidation), surface charge, polarity, bonding, and electrochemical properties.

X-ray diffraction analysis (XRD)

This technique is based on irradiating a material with incident X-rays and then measuring the intensities and scattering angles of the X-rays that leave the material [ 156 ]. This technique is widely used for the analysis of NP phase and crystallinity. However, the resolution and accuracy of XRD can be affected in cases where the samples have highly amorphous characteristics with varied interatomic distances or when the NPs are smaller than several hundreds of atoms [ 25 ].

Examples: For the characterization of biogenic Ag NPs, the XRD results of Ag NPs produced by Trichoderma koningii [ 142 ], Solanum tuberosum [ 143 ], and Acanthospermum hispidum leaf extract [ 153 ] displayed characteristic peaks occurring at roughly 2θ = 38 o , 44°, and 64 o corresponding to (111), (200), and (220) planes, respectively. These results are in good agreement with the reference to the face-centered cubic structure of crystalline silver. However, the XRD results of Ag NPs produced by Solanum tuberosum were not as clear as the other biogenic Ag NPs and had several impurities. The structural characterization of Pd NPs produced by Garcinia pedunculata Roxb leaf extract by XRD showed the distinct peaks of Pd, however, three other peaks were also observed at 2θ of 34.22˚, 55.72˚, and 86.38˚, indicating the presence of PdO phases along with Pd NPs [ 157 ].

Energy-dispersive X-ray spectroscopy (EDX)

This technique is based on the irradiation of the sample with an electron beam. Electrons of the electron beam when incident on the sample surface eject inner shell electrons, the transition of outer shell electrons to fill up the vacancy in the inner shell produces X-rays. Each element produces a characteristic X-ray emission pattern due to its unique atomic structure, and therefore can be used to perform compositional analysis [ 158 ]. The shortfall of EDX is that the resulting spectra give only qualitative compositional information (it shows the chemical elements present in the sample without quantification). However, the peak intensities to some extent give an estimate of the relative abundance of an element in a sample [ 159 ]. This technique does not require sophisticated additional infrastructures, usually it is a small device that is connected to an existing SEM or TEM. This allows the use of SEM or TEM for the morphological characterization and EDX is used simultaneously for the analysis of chemical composition [ 160 ].

Examples: The EDX technique is usually used for the confirmation of the presence of the element in question in biogenic NPs. For instance, EDX was used to confirm the presence of Au in Au NPs produced by Jasminum auriculatum leaf extract [ 161 ], the presence of Pd in Pd NPs produced by Pulicaria glutinosa extract [ 162 ], the presence of Te in Te NPs produced by Penicillium chrysogenum PTCC 5031 [ 163 ], and the presence of Ag in Ag NPs produced by Trichoderma viride [ 164 ].

High-angle annular dark-field imaging (HAADF)

This method is used for the elemental mapping of a sample using a scanning transmission electron microscope (STEM). The images are formed by the collection of incoherently scattering electrons with an annular dark-field detector [ 165 ]. This method offers high sensitivity to variations in the atomic number of elements of the sample, and it is used for elemental composition analysis usually when the NPs of interest consist of relatively heavy elements. The contrast of the images is strongly correlated with atomic number and specimen thickness [ 166 ].

Examples: The employment of HAADF-STEM in the characterization of biogenic Au–Ag–Cu alloy NPs confirmed the presence of the three elements in the same NP [ 167 ]. Similarly, this approach revealed that Ag NPs produced by Andrographis paniculata stem extract were coated with an organic polymer [ 168 ]. The employment of this approach in the characterization of Cu NPs produced by Shewanella oneidensis revealed that Cu NPs remained stable against oxidization under anaerobic conditions, but when they were exposed to air a thin shell of Cu 2 O develop around the NPs [ 169 ].

X-ray photoelectron spectroscopy (XPS)

This technique is considered the most sensitive approach for the determination of NP exact elemental ratios, chemical state, and exact bonding nature of NP materials [ 25 ]. XPS is based on the photoelectric effect that can identify the elements within a material, or covering a material, as well as their chemical state with high precision [ 170 ]. XPS can also be used to provide in-depth information on electron transfer, e.g., for Pt NPs supported on CeO 2 , it was found that per ten Pt atoms only one electron is transferred to the support [ 171 ].

Examples: The XPS technique can employed for different purposes. For instance, it was used for measuring the purity of Au NPs produced by cumin seed powder [ 172 ]. XPS was used for the determination of the oxidation states of Pt NPs produced by Nigella sativa seeds and Ag NPs produced by Rosa canina . XPS results of Pt NPs showed the presence of three oxidation states for Pt (Pt (0), Pt (II), and Pt (IV)) and two oxidation states for Ag NPs (Ag (0) and Ag (I)). In both cases, the zero-oxidation state was the abundant one, the presence of a small amount of the other oxidation states suggests that some of the NPs were oxidized or had unreduced species [ 173 , 174 ]. XPS was used for the determination of the exact elemental ratios and the bonding nature of FeS NPs produced by Shewanella putrefaciens CN32. For the exact elemental ratios, the researchers compared biogenic and abiotic FeS NPs and found that biogenic FeS NPs had a 2.3:1 Fe:S ratio while the abiotic NPs had a 1.3:1 Fe:S ratio. For the bonding nature, it was determined that the surface of NPs had Fe(II)-S, Fe(III)-S, Fe(II)-O, and Fe(III)-O bonds [ 175 ].

Fourier-transform infrared spectroscopy (FTIR)

This technique is based on irradiating a material with infrared light, where the absorbed or transmitted radiation is recorded. The resulting spectrum represents a unique fingerprint of samples, where information about the nature of the sample can be obtained such as the bonds involved, polarity, and oxidation state of the sample [ 176 , 177 ]. This technique is mainly used for the characterization of organic materials such as the surface chemical composition or functionalization of NPs. It is also used for the identification of contaminants when high purity is sought [ 178 ].

Examples: For biogenic NPs, FTIR is usually used for the identification of probable functional groups present on the surface of NPs that are responsible for the reduction and stabilization of the NPs. For plant-mediated NP synthesis, for instance for Ag NPs produced by Camellia sinensis , the FTIR results indicate the presence of Camellia sinensis phytocompounds, such as caffeine and catechin, on the surface of Ag NPs that could be responsible for the reduction of Ag or act as stabilizing agents [ 147 ]. For Ag NPs produced by Solanum tuberosum , the NPs were found to be capped by amide and amine groups [ 143 ]. For CeO 2 NPs produced by Eucalyptus globulus , the polyphenol groups present in Eucalyptus globulus extract were found on the surface of NPs suggesting their involvement in the reduction/stabilization process [ 150 ]. For microbe-mediated NP synthesis, FTIR results show the presence of protein residues on the surface of NPs confirming the involvement of different proteins in the reduction/stabilization process, such as in Ag NPs produced by Streptomyces sp. NH28 [ 179 ], in Te NPs produced by Penicillium chrysogenum PTCC 5031 [ 163 ], and in Se NPs produced by Azospirillum thiophilum [ 180 ].

Zeta potential analysis

Zeta potential measurements are used for the determination of NP surface charge in colloidal solutions. The surface charge of NPs attracts counter-ions that form a thin layer on the surface of the NPs (called Stern layer). This layer travels with the NPs as they diffuse thought the solution. The electric potential at the boundary of this layer is known as NP zeta potential [ 136 ]. The instruments used to measure this potential are called zeta potential analyzers [ 181 ]. Zeta potential values are indicative for NP stability, where higher absolute value of zeta potential indicate more stable NPs [ 136 ].

Examples: The zeta potential is a good indicator for the stability of NPs, where NPs with zeta potentials of more than + 30 mV or less than − 30 mV are considered stable. Zeta potentials have been measured for a wide range of biogenic NPs. The zeta potential for Ag NPs produced by Ziziphus jujuba leaf extract of − 26.4 mV [ 182 ]. Ag NPs produced by other organisms have different zeta potential values, for example, Ag NPs produced by Punica granatum peel extract have a zeta potential of − 40.6 mV indicating their higher stability [ 183 ], while Ag NPs produced by Aspergillus tubingensis have a zeta potential of + 8.48 indicating their relative instability [ 184 ]. The pH of the sample is another important parameter for zeta potential values, the higher pH the lower the zeta potential value [ 185 ]. Having different zeta potential values for the same type of NPs depending on the organism used for their synthesis is not unique to silver, Se NPs also show different potential values depending on the organism used for their synthesis [ 186 ].

Cyclic voltammetry (CV)

CV is an electrochemical technique for measuring the current response of redox-active solutions to a linearly cycled potential sweep between two or more set values. The CV technique involves the use of three electrodes: a working electrode, reference electrode, and counter electrode. These electrodes are introduced to an electrochemical cell filled with an electrolyte solution and where voltage is in excess, the potential of the working electrode is cycled and the resulting current is measured. This technique is used for determining information about the reduction potential of materials, the kinetics of electron transfer reactions, and the thermodynamics of redox processes [ 187 , 188 , 189 ].

Examples: The CV technique can be employed for two different purposes in the context of biogenic NP characterization. Firstly, it can be used for measuring the stability of NPs in electrocatalysis. For this purpose, the biogenic NPs are assembled on an electrode of the electrolysis cell and are tested for their electrocatalytic behavior against a redox reaction over different cycles. As an example, Ag NPs produced by Citrus sinensis were found to be stable in phenolic compounds redox reactions over multiple cycles [ 190 ]. Secondly, CV can be used for monitoring the progress of reduction of metallic NPs or for the determination of the reducing agent involved in the reduction. For example, for Ag NPs produced by Indian propolis, four cyclic voltammograms were recorded, one for a water extract of Indian propolis, another for an ethanol extract of Indian propolis, and two for the constituent flavonoids of Indian propolis (pinocembrin and galangin). The four cyclic voltammograms showed similar behaviors indicating the involvement of these flavonoids in the reduction of Ag and in forming Ag NPs [ 191 ].

Raman spectroscopy

This technique is based on irradiating a sample with monochromatic light emitted by a laser, in which the interactions between the laser light and molecular vibrations (photons and phonons) are recorded. The technique records the inelastically scattered photons, known as Raman scattering (named after the Indian physician C. V. Raman) [ 192 ]. The output of this technique is a unique fingerprint for each sample, which is used to characterize the chemical and intramolecular bonding of the sample. It can also be used to characterize the crystallographic orientation of the sample [ 193 ]. Surface-enhanced Raman spectroscopy (SERS) enhances Raman scattering of a sample and provides a more sensitive, specific, and selective technique for identifying molecular structures [ 194 ]. Both techniques are also used for the characterization of optical properties, where the recorded photons and phonons are used to understand the plasmonic resonance of NPs [ 25 ].

Examples: Raman spectroscopy was used to characterize Fe 3 O 4 NPs produced by Pisum sativum peel, the researchers found that the NPs were Fe 3 O 4 NPs with face centered cubic phase which was in agreement with their XRD measurements [ 195 ]. Other researchers used Raman spectroscopy for studying the trace deposits of carbohydrates on ferrihydrite NPs produced by Klebsiella oxytoca , the results showed that the pores of NPs had more deposits of carbohydrates that the surface of the NPs [ 196 ]. For Au NPs produced by Raphidocelis subcapitata (green algae), several biomolecules were suggested for their involvement in this process. SERS technique was used to study Au NPs surface-associated biomolecules in order to narrow down the list of biomolecules involved in the bioproduction process. The researchers found that several biomolecules such as, glutathione, β-carotene, chlorophyll a, hydroxyquinoline, and NAD were associated with Au NPs surface, thus, ruling out other molecules such as, glutaraldehyde fixing agent, saccharides, FAD, lipids, and DNA from the list [ 197 ].

Characterization of optical, electronic, and electrical properties

In addition to Raman spectroscopy and SERS, also other techniques can be employed to study and characterize the optical properties of NPs. These techniques give information about the absorption, reflectance, fluorescence, luminescence, electronic state, bandgap, photoactivity, and electrical conductance properties of NPs.

Ultraviolet–visible spectroscopy (UV–vis) and photoluminescence spectroscopy (PL)

In absorption spectroscopy such as UV–vis, the transition of electrons from the ground state to an excited state is measured, while in photoluminescence spectroscopy, the transition of electrons from the excited state to the ground state is measured [ 198 ]. UV–vis spectroscopy uses visible and UV light to measure the absorption or reflectance of a sample. In photoluminescence spectroscopy, usually UV light is used to excite the electron and then measure the luminescence or fluorescence properties of a sample [ 199 ].

Examples: UV–vis spectroscopy is a simple and common technique that is used for the characterization of the optical properties of NPs. For instance, for the characterization of the optical properties of Ag NPs produced by Trichoderma viride , the UV–vis spectrum showed that a Ag surface plasmon band occurs at 405 nm, which is a characteristic band for Ag NPs. The intensity of this band over the reaction time increased as a result of increasing Ag NP concentration in the solution. In the same study, the photoluminescence properties of these NPs were recorded, with an emission in the range between 320–520 nm, which falls in the blue-orange region [ 164 ]. For biogenic Cu NPs, the common absorption peaks are located between 530–590 nm. The difference in NP size and the bio-active molecules used for the reduction process are believed to be the reasons behind the differences in the absorption peaks [ 200 ]. For instance, 15 nm spherical Cu NPs produced by Calotropis procera have an absorption peak at 570 nm [ 201 ], while 76 nm spherical Cu NPs produced by Duranta erecta have an absorption peak at 588 nm [ 202 ]. The same applies to photoluminescence effects, where 27 nm spherical Cu NPs produced by Tilia extract emit light of 563 nm (dark brown) [ 203 ], while 19 nm spherical Cu NPs emit light of 430 nm (green) [ 204 ].

UV–vis diffuse reflectance spectroscopy (DRS)

This technique uses UV and visible light to measure the diffuse reflectance of a material (the reflection of light in many angles, as opposed to specular reflection). The resulting diffuse reflectance spectra are used to determine the electronic state of a sample, which is then used to calculate the bandgap [ 25 ]. Bandgap determination is crucial for determining conductance and photocatalytic properties especially for semiconductor NPs [ 205 ].

Examples: The DRS technique was used to calculate the bandgap for a wide range of biogenic NPs. For instance, TiO 2 NPs produced by Andrographis paniculata exhibit an optical energy bandgap of 3.27 eV [ 206 ]. Interestingly, biogenic ZnO NPs produced by different organism show different bandgaps, for example, ZnO NPs produced by Pseudomonas putida have a bandgap of 4 eV [ 207 ], while ZnO NPs produced by Calotropis procera leaf extract have a bandgap of 3.1 eV [ 208 ].

Spectroscopic ellipsometry

This technique is based on irradiating a sample with polarized light to measures changes in polarization. It is widely used to calculate the optical constants of a material (refractive index and extinction coefficient) [ 209 ]. This technique is also used to characterize the electrical conductivity and dielectric properties of materials [ 210 ].

Examples: Spectroscopic ellipsometry is not a common technique for the characterization of biogenic NPs. For chemically produced NPs, the optical properties for different-sized Au NPs partially embedded in glass substrate were measured by spectroscopic ellipsometry. In this example, a clear transition from LSPR to SPR mode was found as the thickness increases. Moreover, the partially-embedded Au NPs had much higher refractive index sensitivity compared to Au NPs fully immobilized in a glass substrate [ 211 ]. Spectroscopic ellipsometry was also used to measure the changes in the optical constants of a layer of 5 nm ZnO NPs induced by UV illumination. In this case, it was found that the UV illumination of ZnO NPs in inert atmospheres resulted in a clear blue shift in the absorption (Moss-Burstein shift). The UV illumination of ZnO NPs results in the desorption of O 2 from the NPs surface leading to the population of the lowest levels in conduction band with mobile electrons. This phenomenon is reversible, in which the exposure to O 2 from air results in the scavenging of these mobile electrons [ 212 ].

Characterization of magnetic properties

The magnetic properties of NPs are of high importance, as they potentially give NPs great advantages in catalysis, electronics, and medical applications. Several techniques were developed for the detection and quantification of small magnetic moments in NPs.

Magnetic force microscopy (MFM)

This technique is a variety of atomic force microscopy (AFM), in which a magnetic tip is used to scan the sample. The magnetic tip is approached very close to the sample, where the magnetic interactions between the tip and the sample are recorded [ 213 ]. At closer distances to the sample (0–20 nm), other forces such as van der Waals forces also interact with the tip. Therefore, MFM measurements are often operated with two-pass scanning method (also called lift height method) [ 214 ] (Fig.  7 ). In this method, the tip is firstly used to measure the topography of the sample including the molecular forces as van der Waals. Afterwards, the tip is lifted and a second scan is operated following the same topography outline. In the second scan, the short-ranged van der Waals forces disappear and the long-range magnetic forces are almost exclusively recorded. In an experimental study, researchers found that 22 nm was the optimal scanning height for the second scan, at which van der Waals forces are very weak while the distance is still small enough to measure the magnetic interactions for Pd-Fe bimetallic NPs [ 215 ].

Magnetic force microscopy lift height method. The first scan is done very close to the surface to obtain the topography of the sample. Then, the tip is lifted and a second scan is performed following the topography outline obtained in the first scan

Examples: MFM was heavily used for the characterization of magnetite NPs produced by magnetotactic bacteria. For instance, the size and orientation of the magnetic moment of magnetite NPs produced by Magnetospirillum gryphiswaldense strain MSR-1 were studied by MFM [ 216 ], in which the size of the magnetic moment was found to be 1.61 × 10 −17 Am 2 . In a different study, MFM was used to characterize the magnetic properties and to estimate the size of the magnetic kernel of the magnetosomes produced by the same strain, and it was determined that the NPs behaved like single mono-domain nanomagnets [ 217 ]. The magnetic properties of NPs made from materials such as Pd that only exhibit significant magnetism on the nanoscale can also be studied by MFM, however, the magnetic moment of these NPs is much lower than for ferromagnetic NPs. The magnetic decoration of Pd NP samples with Fe 2 O 3 NPs strongly enhances the weak magnetic signal of Pd NPs up to 15 times [ 218 ]. This approach could make the MFM technique useful for the characterization of weak magnetic NPs.

Vibrating-sample magnetometry (VSM)

This technique measures the magnetic properties of materials based on Faraday’s law of induction. In VSM, the sample is placed in a constant magnetic field in a special holder that vibrates vertically. As the holder starts vibrating, the magnetic moment of the sample creates a magnetic field that changes as function of time. The alternating magnetic field created in the sample induces an electric current that is recorded and used to calculate the magnetic properties of the sample [ 219 , 220 ].

Examples: For the characterization of Fe 2 O 3 NPs produced by Tridax leaf extract, VSM studies revealed that the NPs had a saturation magnetization of 7.78 emu/g, a remnant magnetization of 0.054 emu/g, and a coercivity of − 1.6 G [ 221 ]. In other studies, VSM was used to compare the magnetic properties of iron oxide NPs produced Moringa oleifera with the magnetic properties of the same NPs but coated with chitosan. The researchers found that saturation magnetisation, remnant magnetization, and coercivity have lower values when the NPs are coated with chitosan [ 222 ].

Superconducting quantum interference device (SQUID) magnetometry

This technique measures the magnetic properties of materials based on the Josephson effect. Niobium (Nb) or other metal alloys are used in the device which needs to be operated at temperatures very close to the absolute zero to main superconductivity, where liquid helium is used to maintain the cold environment [ 223 ]. However, other kinds of SQUID also exist where high-temperature superconductors are used [ 224 ]. After reaching superconducting environments, the Josephson junctions contained in the device help to create a supercurrent, which is recorded and used to calculate the magnetic properties of the sample [ 225 ].

Examples: For the characterization of iron oxide NPs produced by Cnidium monnieri seed extract, SQUID magnetometry revealed that the NPs had a saturation magnetization of 54.60 emu/g, a remnant magnetization of 1.15 emu/g, a coercivity of 11 Oe, and a magnetic susceptibility of + 1.69 × 10 –3 emu/ cm 3 ⋅ Oe at room temperatures, indicating the superparamagnetic behaviour of these NPs [ 226 ]. SQUID magnetometry was also used for the characterization of the magnetic properties of zinc incorporated magnetite NPs produced by Geobacter sulfurreducens , showing that the loading of only 5% zinc results in the enhancement of saturation magnetization of the NPs by more than 50% [ 227 ].

Electron spin resonance spectroscopy (ESR)

This technique measures the magnetic properties of materials by characterizing and quantifying the unpaired electrons in the sample. Electrons are charged particles that spin around their axis, which can align in two different orientations (+ ½ and − ½) when the sample is placed in strong magnetic field. These two alignments have different energies due to the Zeeman effect. Since unpaired electrons can change their spins by absorbing or emitting photons, in ESR the sample is irradiated with microwave pulses to excite electron spins until a resonance state is reached [ 228 ]. This technique is also referred to as electron paramagnetic resonance spectroscopy (EPR). It can be used to measure the ferromagnetic and antiferromagnetic properties of NPs [ 229 , 230 ].

Examples: ESR was used to characterize the magnetic properties of iron oxide NPs produced by Ficus carica . The trees naturally produce iron oxide NPs as a defence mechanism when are they are subjected to stress. The researchers found that the magnetic properties of iron oxide NPs produced by the same tree but grown in different environmental conditions have different magnetic properties. In addition, a magnetic anisotropy of the signal was visible as the magnetic properties of these NPs varied strongly at different temperatures [ 231 ]. ESR was also used to characterize the magnetic properties of Se nanomaterials produced by anaerobic granular sludge. The ESR results revealed the presence of Fe(III) atoms incorporated in the Se nanomaterial, which enhanced their overall magnetic properties, giving it ferromagnetic behaviour [ 232 ].

Characterization of thermal properties

Several techniques can be used for the characterization of the thermal properties of NPs, such as melting points, crystallization and structural-phase transition points, heat capacity, thermal conductivity, and thermal and oxidative stability.

Differential scanning calorimetry (DSC)

In this technique the analyte and a well-defined reference sample are put at the same temperature, then, the amount of heat required to increase the temperature of the sample and the reference in measured as a function of temperature. This technique is widely used to measure melting points [ 233 ], crystallization points, structural-phase transition points [ 234 ], latent heat capacity [ 235 ], heat of fusion [ 236 ], and oxidative stability [ 237 ].

Examples: For the characterization of Ag NPs produced by Rhodomyrtus tomentosa leaf extract, DSC showed three exothermic peaks at 44, 159, 243, and an endothermic peak at 441 °C. The first peak (at 44 °C) indicates that at this temperature the NPs face a gradual loss of water from their surface. The second peak (at 159 °C) shows that the thermal decomposition of the sample happens at this temperature. The last temperature (441 °C) indicates the melting temperature for those NPs [ 238 ]. For Ag NPs produced by Parthenium hysterophorus leaf extract, DSC showed that their melting temperature was at 750 °C. The researchers also found that these NPs had completely thermally decomposed and crystallized simultaneously [ 239 ].

Differential thermal analysis (DTA)

This technique is based on heating or cooling a sample and an inert reference under identical conditions, where any temperature difference between the sample and the reference is recorded. This technique is primarily used for the study of phase diagrams and transition temperatures [ 240 ]. However, it is also used to measure the melting points, thermal, and oxidative stability [ 241 , 242 ].

Thermogravimetric analysis (TGA)

This technique measures the change in the mass of a sample as a function of temperature and/or time in a controlled atmosphere [ 243 ]. This technique is mainly used to study the thermal stability of materials [ 244 ], in addition, it is also used to measure structural-phase transition points [ 245 ], thermal activation energies [ 246 ], and oxidative stability [ 247 ]. The resulting thermogram is unique for each compound and therefore can also be used for the determination of material composition [ 248 ]. TGA and DTA are usually combined in the same thermal analyzing instrument, called thermogravimetry/differential thermal analysis (TG/DTA) [ 244 ].

Examples: TG/DTA is a common technique for the characterization of thermal properties of biogenic NPs. For instance, the thermal properties of Ag NPs produced by Daphne mucronate leaf extract were studied in the range between 0–1000 °C where the sample was heated at a rate of 10 °C/min. The researchers found that between 400–500 °C the NPs faced a dominant weight loss, while the weight loss below 400 °C and above 500 °C was negligible. The DTA curve showed an intense exothermic peak in the range between 400–500 °C, this indicates that the crystallization of NPs happens in this temperature interval. Some minor weight loss events were seen below 400 °C, this may be caused by the evaporation of water or the degradation of the organic components [ 249 ]. In another study, the thermal properties of Ag NPs produced by two different plants ( Stereospermum binhchauensis and Jasminum subtriplinerve ) were compared. The researchers found that the major weight loss happens between 220–430 °C, which is attributed to the decomposition of biomolecules from the NP surface [ 250 ]. This shows that Ag NPs produced by these plants have much higher content of biomolecules on their surface than Ag NPs produced by Daphne mucronate. TG/DTA showed that Stereospermum binhchauensis Ag NPs crystallize at 315 °C and Jasminum subtriplinerve Ag NPs at 345 °C, around 100 °C less than Daphne mucronate Ag NPs [ 250 ].

Transient hot wire method (THW)

This method is used for the determination of thermal conductivity based on increasing the temperature of a material by a thin hot wire as a function of time, where the heating wire is located directly in the test sample. The advantage of this method over other thermal conductivity measurement methods is the very short measuring time, this gives high accuracy of thermal conductivity due to the negligible values of convection in such short times [ 251 ]. In this method, the NPs are added to a solution (usually water or ethylene glycol) forming a colloidal dispersion called a nanofluid. Then, the thermal conductivity of the nanofluid is measured and compared to the thermal conductivity of the base fluid, giving a thermal conductivity ratio which is used to evaluate the thermal conductivity of different NPs.

Examples: The thermal conductivity ratios of three different concentrations (0.12, 0.18, and 0.24%) of biogenic SnO 2 NPs produced by Punica granatum seed extract were measured in ethylene glycol at 303 K. The researchers found a linear relationship between NPs concentration and the thermal conductivity. The thermal conductivity enhancement of nanofluid to base fluid was between 6 and 24% [ 252 ]. In another study, the thermal conductivity of Fe 2 O 3 NPs produced by Psidium guajava leaf extract was measured in water and in ethylene glycol. The researchers found that the thermal conductivity enhancement in ethylene glycol was better than in water, the thermal conductivity enhancement for 0.025% Fe 2 O 3 NPs in water was 30% while in ethylene glycol was 34%. Moreover, the linear relationship between NPs concentration and thermal conductivity ratio was found for Fe 2 O 3 NPs in both water and ethylene glycol [ 253 ].

Characterization of mechanical properties

Several methods can be used for the characterization of mechanical properties of NPs, such as tensile and compressive strengths, elasticity, viscoelasticity, hardness, and stiffness.

Tensometery

The machine used for this method is called a universal testing machine (UTM) or a tensometer. It is used to measure the elasticity (elastic modulus), tensile and compressive strengths (Young’s modulus) of materials. In this machine, the sample is placed between grips and an extensometer, where changes in gauge length are recorded as a function of load [ 254 ]. However, other mechanical changes in addition to the change in gauge length are also recorded in this machine, such as the elasticity.

Examples: The mechanical properties of different biogenic NP-containing composites can be measured by this machine. For example, the mechanical properties of orthodontic elastic ligatures containing Ag NPs produced by Heterotheca inuloides were studied by comparing the maximum strength, tension, and displacement of the composite with and without the biogenic NPs. The researchers found that maximum strength, tension, and displacement have improved after the addition of Ag NPs [ 255 ]. Interestingly, the addition of biogenic Ag NPs produced by Diospyros lotus fruit extract to starch and polyvinyl alcohol hydrogel membranes resulted in an adverse effect. The tensile strength and modulus of the hydrogel membranes containing 50 and 100 ppm Ag NPs were much lower than of the neat hydrogel membrane. The researchers attributed this adverse effect to the possibility that the addition of Ag NPs could have resulted in blocking the crosslinking between starch and polyvinyl alcohol, or to the possibility of the formation of breakage points in the polymer matrix due to NPs agglomeration [ 256 ].

Instrumented indentation testing

This method is used to characterize the hardness features of materials by using a well-defined hard indenter tip typically made of diamond. The indenter tip is used to make an indentation in the sample by placing incremental loads on the tip, after which the area of indentation in the sample is measured and used to calculate the hardness features [ 257 ]. Light microscopy, SEM, or ATM technique are usually used to visualize the indentation in the sample. The method is also called micro- or nano-indentation testing.

Examples: This method was used to characterize the mechanical properties of calcite NPs produced by Ophiocoma wendtii brittlestar. The arm plates of this brittlestar are covered by hundreds of nanoscale calcite lenses that focus light onto photoreceptor nerve bundles positioned beneath the brittlestar. The researchers used the nanoindentation method to compare Young’s modulus, hardness and fracture toughness of biogenic calcite with geocalcite. The results showed that the biogenic calcite lenses have higher hardness and fracture toughness compared to geocalcite (more than twofold) [ 258 ]. Bamboo is well known for its high silica content in comparison to other wood species. It produces SiO 2 NPs and deposits it in its epidermis in the form of silica cells. The mechanical properties of silica cells compared to other types of cells of Moso bamboo ( Phyllostachys pubescens ) were studied by instrumented indentation testing. The researchers found that the cell wall of silica cells display higher hardness and elastic recovery compared to fibre and epidermal cells, which is attributed to the presence of biogenic SiO 2 NPs in the silica cells [ 259 ].

Dynamic mechanical analysis (DMA)

This method is used to study the mechanical properties of materials by measuring the strain of a material after applying a stress. This method helps to obtain three different values: storage modulus, loss modulus, and loss tangent. These values are important to give an overview about the stiffness and viscoelasticity behavior of materials [ 260 ].

Examples: The DMA method was used to characterize the mechanical properties of polymethyl methacrylate denture base polymer filled with Ag NPs produced by Boesenbergia rotunda . In this study frequency sweep test was used to determine the viscoelastic behavior of this nanocomposite where the temperature was constant at 37 °C and the frequency was increasing from 0.5 to 100 Hz in tension mode. The researchers found a frequency dependence for storage modulus, loss modulus, and loss tangent for the nanocomposite with various Ag NPs loading concentrations. The frequency dependence of storage modulus, loss modulus, and loss tangent indicates the viscoelastic response of this polymer. However, the results showed that the storage modulus for the nanocomposite is much higher than the loss modulus over the range of frequencies, indicating the elastic dominance of the nanocomposite. Moreover, the researchers found that storage and loss moduli increase with increasing Ag NPs loading concentrations, which is due to the interaction between polymethyl methacrylate and Ag NPs [ 261 ].

In a different study, DMA was used to determine the thermomechanical properties of pol(S-co-BuA) polymer filled with cellulose nanocrystals produced by Posidonia oceanica . In this case, the behaviour of storge modulus and loss tangent were studied as a function of temperature for different cellulose nanocrystals loading concentrations. The results showed that the unloaded polymer behaves like an amorphous polymer, the storage modulus remains constant until the temperature reaches 25 °C then it starts to sharply decrease due to glass–rubber transition. A relaxation process was also evident for the unloader polymer, where the loss tangent reaches its maximum at 35 °C then it starts to fall. The addition of cellulose nanocrystals to the polymer positively enhanced both effects. The dramatic drop of storage modulus at 25 °C was less for the nanocomposite, where the drop for the polymer loaded with 15% cellulose nanocrystals was almost cancelled. Similar positive enhancement was found for loss tangent. These enhancements could be attributed to the mechanical coupling effect, in which the NPs connect and form a stiff continuous network linked through hydrogen bonding [ 262 ].

Applications of NPs

NPs, due to their above-mentioned unique or enhanced physicochemical properties, are used in a wide range of applications in different fields. In addition, several potential applications are in research and development. Here we present some examples of these applications.

Applications in medicine and pharma

Metallic and semiconductor NPs have huge potential for cancer diagnosis and therapy based on their enhanced light scattering and absorption properties due to LSPR effect. For instance, Au NPs efficiently absorb light and convert it into localized heat, which can be exploited for selective photothermal therapy of cancer (cancer cell death by heat generated in tumor tissue) [ 263 , 264 ]. In addition, the unique optical properties of Au NPs make them a great candidate for the photodynamic therapy of cancer (the use of a drug that is activated by light to kill cancer cells) [ 265 ]. Gd based NPs have also shown great abilities in tumor growth inhibition [ 266 ], metastasis inhibition [ 267 ], and tumor-specific magnetic resonance contrast enhancement [ 268 ]. Targeted drug delivery is also an important potential application of NPs. ZnO and Fe 3 O 4 NPs were efficiently used for targeted drug delivery and selective destruction of tumor cells [ 269 , 270 , 271 ].

Moreover, NPs have been successfully used in different medical applications such as cellular imaging [ 272 ], or in biosensors for DNA, carbohydrates, proteins, and heavy metal ions [ 273 , 274 ], determination of blood glucose levels [ 275 ], and for medical diagnostics to detect bacteria [ 276 ] and viruses [ 277 ]. For instance, Au NPs were conjugated with SARS-CoV-2 antigens to rapidly detect the presence of SARS-CoV-2 IgM/IgA antibodies in blood samples within 10–15 min [ 278 ], At the same time, due to their antimicrobial and antibacterial activities, NPs such as TiO 2 , ZnO, CuO, and BiVO 4 are being increasing used in various medical products such as catheters [ 279 , 280 ].

Applications in electronics

NPs, due to their novel electronic and optical properties, have a wide range of potential applications in imaging techniques and electronics. For instance, Gd-based NPs can improve the imaging quality and the contrast agent administration dose of magnetic resonance imaging (MRI). The use of Gd 2 O 3 NPs as a contrasting agent was found to be more efficient than the commonly used agent (Gd-DOTA) at the same concentration [ 281 ]. At the same time, GdPO 4 NPs were successfully used for tumor detection using MRI in 1/10 of the dose typically used with Gd-DTPA agent [ 282 ]. Interestingly, NPs also offer the ability to image and track a single molecule, which can reveal important information about cellular processes such as membrane protein organization and interaction with other proteins. For example, Eu 3+ -doped oxide NPs were used to track a single toxin receptor with a localization precision of 30 nm [ 283 ].

Regarding applications in batteries, an important component in lithium-ion batteries is the separators. Their main function is to prevent the physical contact of anode and cathode, and to provide channels for the transport of ions. The commonly used commercial material in battery separators, a polyolefin microporous membrane, suffers from poor electrolyte uptake and poor thermal stability [ 284 ]. Due to the aerogel structure of some NPs (such as ZnO NPs), they are an ideal choice for separator plates in batteries [ 284 ]. This makes the batteries store a significantly higher amount of energy compared to traditional batteries. For lithium-air batteries, using Pt-Au bimetallic NPs strongly enhances oxygen reduction and oxygen evolution reactions [ 285 ]. Moreover, batteries made of nanocrystalline Ni and metal hydrides last longer and require less charging [ 23 ]. In addition to battery applications, several NPs such as CdS and ZnSe are also used in light-emitting diodes (LED) of modern displays to get higher brightness and bigger screens [ 23 , 286 ]. Other NPs such as CdTe NPs are also used in liquid crystal displays (LCDs) [ 287 ]. The addition of a NP layer to LED and LCD enables them to generate more light using the same amount of energy and enhances their lifetime.

Applications in agriculture

NPs have potential to benefit the agriculture field by providing new solutions to current agricultural and environmental problems [ 288 ]. NPs are mainly used in two forms in agriculture, as nanofertilizers and nanopesticides. Chemical fertilizers have poor efficiency due to leaching and volatilization. In these cases, the farmers usually react by using excessive amounts of fertilizers, which increases crops productivity but has an environmental cost [ 288 ]. In contrast, nanofertilizers are compounds that are applied in smaller amounts than regular chemical fertilizers but yet have better efficiencies [ 289 ]. The difference in efficiency comes from the fact that they are able to release the nutrients just when and where they are required by the plants. In that way, they limit the conversion of excess amounts of fertilizer to gaseous forms or from leaking into the ground water [ 290 ]. Several NPs have been employed in the development of fertilizers, including SiO 2 , ZnO, CuO, Fe, and Mg NPs [ 291 , 292 , 293 ]. These nanofertilizers provide the plants with increased nitrogen fixation, improved seed germination, amelioration to drought stress, increased seed weight, and increased photosynthesis ability [ 291 , 292 , 293 ]. The large surface area and small size of these NPs are the main reasons for the better efficiencies of nanofertilizers over conventional fertilizers [ 294 ].

Several NPs have proven antimicrobial, insecticidal, and nematicidal activities, which makes them a promising alternative to chemical pesticides and a potentially cheaper alternative to biopesticides [ 294 ]. For instance, the photocatalytic activity of TiO 2 NPs gives them a potent antimicrobial activity against Xanthomonas perforans , the causing agent of tomato spot disease [ 295 ]. CuO NPs show insecticidal activity against Spodoptera littoralis , known as African cotton leafworm [ 296 ]. Ag NPs show nematicidal activity against Meloidogyne spp. , root-knot nematodes [ 297 ].

Applications in the food industry

NPs, despite toxological concerns, have impactful applications in several food industry-related process such as food production, preservation, and packaging. TiO 2 NPs are a major promising player in this industry. Their photocatalytic antimicrobial activity makes them an interesting material for food packaging [ 298 ]. In addition, they are also used in sensors to detect volatile organic compounds [ 299 ]. Ag NPs are also promising in food packaging due to their antimicrobial activity. They play an important role in reducing the risk of pathogens and extending food shelf-life [ 294 ]. The efficiency of doping Ag and ZnO NPs to degradable and non-degradable packaging materials for meat, bread, fruit, and dairy products was tested against several yeast, molds, aerobic, and anaerobic bacteria [ 300 ]. For instance, polyvinyl chloride doped with Ag NPs was evaluated for packing minced meet at refrigerator temperature (4 °C); the results showed that Ag NPs significantly helped to slow down bacterial growth, increasing the shelf-life of minced meet from 2 to 7 days [ 301 ].

Effects of NPs on biological systems

Although the use of NPs is exponentially growing, their possible toxicological and hazardous impacts to human health and environment cannot be ignored. NPs may get released to the environment during production stages, usage, recycling, or disposal. These NPs may persist in air, soil, water, or biological systems [ 302 ]. NPs can enter the human or animal body though the skin, orally, or via the respiratory tract, and afterwards move to other parts of the body. The exposure to NPs was found to activate proinflammatory cytokines and chemokines with recruitment of inflammatory cells, which impacts the immune system homeostasis and can lead to autoimmune, allergic, or neoplastic diseases [ 302 ]. Moreover, the exposure to ultrafine particles can cause pulmonary, cardiac, and central nervous system diseases [ 303 , 304 , 305 ]. Similarly, NPs can enter plants cells and cause harmful effects [ 306 ]. For instance, the exposure of ZnO and Al NPs was found to cause root growth inhibition in plants [ 307 , 308 ].

Nanoscience and nanotechnology are inherently transdisciplinary fields of science. With new bio-based approaches, there is a need for biologists to understand not only the basic principles of nanoscience, but also the technologies and methods traditionally employed to characterize nanomaterials. We hope that this review can help to inspire new collaborations across different scientific disciplines, by helping biologists to identify the best technologies—and partners—to characterize their nanomaterials. At the same time, we recommend to take potential biological risks of these new materials into careful consideration already during the planning phase of such experiments.

Availability of data and materials

Not applicable.

https://www.etymonline.com/word/nano .

[SOURCE: ISO/TS 80,004‑2:2015, 4.4].

Abbreviations

Atomic force microscopy

Brunauer–Emmett–Teller

Barrett–Joyner–Halenda

Cyclic voltammetry

Dynamic light scattering

Derjaguin–Landau–Verwey–Overbeek

Dynamic mechanical analysis

Derjaguin–Muller–Toporov

UV–vis diffuse reflectance spectroscopy

Differential scanning calorimetry

Differential thermal analysis

Energy-dispersive X-ray spectroscopy

Electron microscopy

Electron paramagnetic resonance spectroscopy

Electron spin resonance spectroscopy

Fourier-transform infrared spectroscopy

High-angle annular dark-field imaging

International Organization for Standardization

Johnson–Kendall–Roberts

Liquid crystal display

Light-emitting diode

Localized surface plasmon resonance

Magnetic force microscopy

Magnetic resonance imaging

Nanoparticles

Nanoparticle tracking analysis

Photoluminescence spectroscopy

Critical radius

Threshold radius for superparamagnetism

Selected area electron diffraction

Scanning electron microscopy

Surface-enhanced Raman spectroscopy

Surface plasmon resonance

Superconducting quantum interference device

Scanning transmission electron microscopy

Scanning tunneling microscopy

Transmission electron microscopy

Thermogravimetry/differential thermal analysis

Thermogravimetric analysis

Transient hot wire

Universal testing machine

Ultraviolet

Ultraviolet–visible spectroscopy

Vibrating-sample magnetometry

X-ray photoelectron spectroscopy

X-ray diffraction analysis

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Acknowledgements

This work was supported by the Research Council of Norway, Grant 294605 (Center for Digital Life) to DL.

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Joudeh, N., Linke, D. Nanoparticle classification, physicochemical properties, characterization, and applications: a comprehensive review for biologists. J Nanobiotechnol 20 , 262 (2022). https://doi.org/10.1186/s12951-022-01477-8

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• Nanomaterials
• Metal nanoparticles
• Biogenic nanoparticles
• Bionanoparticles
• Nanobiotechnology
• Characterization of nanomaterials

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REVIEW article

A review on nanoparticles: characteristics, synthesis, applications, and challenges.

• Department of Biology, College of Science, University of Hafr Al Batin, Hafr Al-Batin, Saudi Arabia

The significance of nanoparticles (NPs) in technological advancements is due to their adaptable characteristics and enhanced performance over their parent material. They are frequently synthesized by reducing metal ions into uncharged nanoparticles using hazardous reducing agents. However, there have been several initiatives in recent years to create green technology that uses natural resources instead of dangerous chemicals to produce nanoparticles. In green synthesis, biological methods are used for the synthesis of NPs because biological methods are eco-friendly, clean, safe, cost-effective, uncomplicated, and highly productive. Numerous biological organisms, such as bacteria, actinomycetes, fungi, algae, yeast, and plants, are used for the green synthesis of NPs. Additionally, this paper will discuss nanoparticles, including their types, traits, synthesis methods, applications, and prospects.

1. Introduction

Nanotechnology evolved as the achievement of science in the 21st century. The synthesis, management, and application of those materials with a size smaller than 100 nm fall under the interdisciplinary umbrella of this field. Nanoparticles have significant applications in different sectors such as the environment, agriculture, food, biotechnology, biomedical, medicines, etc. like; for treatment of waste water ( Zahra et al., 2020 ), environment monitoring ( Rassaei et al., 2011 ), as a functional food additives ( Chen et al., 2023 ), and as a antimicrobial agents ( Islam et al., 2022 ). Cutting-edge properties of NPs such as; nature, biocompatibility, anti-inflammatory and antibacterial activity, effective drug delivery, bioactivity, bioavailability, tumor targeting, and bio-absorption have led to a growth in the biotechnological, and applied microbiological applications of NPs.

A particle of matter with a diameter of one to one hundred nanometers (nm) is commonly referred to as a nanoparticle or ultrafine particle. Nanoparticles frequently exhibit distinctive size-dependent features, mostly due to their tiny size and colossal surface area. The periodic boundary conditions of the crystalline particle are destroyed when the size of a particle approaches the nano-scale with the characteristic length scale close to or smaller than the de Broglie wavelength or the wavelength of light ( Guo et al., 2013 ). Because of this, many of the physical characteristics of nanoparticles differ significantly from those of bulk materials, leading to a wide range of their novel uses ( Hasan, 2015 ).

2. Emergence of nanotechnology

Nanotechnology emerged in the 1980s due to the convergence of experimental advances such as the invention of the scanning tunneling microscope in 1981 and the discovery of fullerenes in 1985 ( Bayda et al., 2019 ), with the elucidation. The popularization of a conceptual framework for nanotechnology goals began with the publication of the book Engines of Creation in 1986 ( Bayda et al., 2019 ).

2.1. Early stage of NPs

Carbon nanotubes have been discovered in pottery from Keeladi, India, dating from around 600–300 BC ( Bayda et al., 2019 ; Kokarneswaran et al., 2020 ). Cementite nanowires have been discovered in Damascus steel, a material that dates back to around 900 AD; nevertheless, its origin and creation method are unclear ( Kokarneswaran et al., 2020 ). However, it is unknown how they developed or whether the material containing them was used on purpose.

2.2. Discovery of C, Ag, Zn, Cu, and Au nanoparticles

Carbon NPs were found in 1991, and Iijima and Ichihashi announced the single-wall carbon nanotube synthesis with a diameter of 1 nanometer in 1993 ( Chen et al., 2021 ). Carbon nanotubes (CNTs), also known as Bucky tubes, are a kind of nanomaterial made up of a two-dimensional hexagonal lattice of carbon atoms. They are bent one way and joined to produce a hollow cylindrical cylinder. Carbon nanotubes are carbon allotropes that fall between Fullerene (0 dimensional) and Grapheme (2 dimensional) ( Chen et al., 2021 ).

In addition, M. C. Lea reported that the synthesis of citrate-stabilized silver colloid almost 120 years ago ( Nowack et al., 2011 ). This process produces particles with an average diameter of 7 to 9 nm. Nanoscale size and citrate stabilization are analogous to recent findings on nanosilver production employing silver nitrate and citrate ( Majeed Khan et al., 2011 ). The use of proteins to stabilize nanosilver has also been documented as early as 1902 ( Nowack et al., 2011 ; Beyene et al., 2017 ). Since 1897, a nanosilver known as “Collargol” has been made commercially and used for medicinal purposes ( Nowack et al., 2011 ). Collargol, a type of silver nanoparticle, has a particle size of about 10 nanometers (nm). This was determined as early as 1907, and it was found that the diameter of Collargol falls within the nanoscale range. In 1953, Moudry developed a different type of silver nanoparticle called gelatin-stabilized silver nanoparticles, with a diameter ranging from 2–20 nm. These nanoparticles were produced using another method than Collargol. The necessity of nanoscale silver was recognized by the creators of nanosilver formulations decades ago, as seen by the following remark from a patent: “for optimal efficiency, the silver must be disseminated as particles of colloidal size less than 25 nm in crystallite size”( Nowack et al., 2011 ).

Gold NPs (AuNPs) have a long history in chemistry, going back to the Roman era when they were used to decorate glassware by staining them. With the work of Michael Faraday, who may have been the first to notice that colloidal gold solutions have characteristics different from bulk gold, the contemporary age of AuNP synthesis began more than 170 years ago. Michael Faraday investigated the making and factors of colloidal suspensions of “Ruby” gold in 1857. They are among the magnetic nanoparticles due to their distinctive optical and electrical characteristics. Under specific illumination circumstances, Faraday showed how gold nanoparticles might create solutions of various colors ( Bayda et al., 2019 ; Giljohann et al., 2020 ).

3. Classification of NPs

Nanoparticles (NPs) are categorized into the following classes based on their shape, size, and chemical characteristics

3.1. Carbon-based NPs

Fullerenes and carbon nanotubes (CNTs) are the two essential sub-categories of carbon-based NPs. NPs of globular hollow cages, like allotropic forms of carbon, are found in fullerenes. Due to their electrical conductivity, high strength, structure, electron affinity, and adaptability, they have sparked significant economic interest. These materials have organized pentagonal and hexagonal carbon units, each of which is sp2 hybridized. While CNTs are elongated and form 1–2 nm diameter tubular structures. These fundamentally resemble graphite sheets rolling on top of one another. Accordingly, they are referred to as single-walled (SWNTs), double-walled (DWNTs), or multi-walled carbon nanotubes (MWNTs) depending on how many walls are present in the rolled sheets ( Elliott et al., 2013 ; Astefanei et al., 2015 ).

3.2. Metal NPs

Metal NPs are purely made of metals. These NPs have distinctive electrical properties due to well-known localized surface Plasmon resonance (LSPR) features. Cu, Ag, and Au nanoparticles exhibit a broad absorption band in the visible region of the solar electromagnetic spectrum. Metal NPs are used in several scientific fields because of their enhanced features like facet, size, and shape-controlled synthesis of metal NPs ( Khan et al., 2019 ).

3.3. Ceramics NPs

Ceramic NPs are tiny particles made up of inorganic, non-metallic materials that are heat-treated and cooled in a specific way to give particular properties. They can come in various shapes, including amorphous, polycrystalline, dense, porous, and hollow, and they are known for heat resistance and durable properties. Ceramic NPs are used in various applications, including coating, catalysts, and batteries ( Sigmund et al., 2006 ).

3.4. Lipid-based NPs

These NPs are helpful in several biological applications because they include lipid moieties. Lipid NPs typically have a diameter of 10–1,000 nm and are spherical. Lipid NPs, i.e., polymeric NPs, have a solid lipid core and a matrix consisting of soluble lipophilic molecules ( Khan et al., 2019 ).

3.5. Semiconductor NPs

Semiconductor NPs have qualities similar to metals and non-metals. That is why Semiconductor NPs have unique physical and chemical properties that make them useful for various applications. For example, semiconductor NPs can absorb and emit light and can be used to make more efficient solar cells or brighter light-emitting diodes (LEDs). They can make smaller and faster electronic devices, such as transistors, and can be used in bio imaging and cancer therapy ( Biju et al., 2008 ).

3.6. Polymeric NPs

Polymeric NPs with a size between 1 and 1,000 nm can have active substances surface-adsorbed onto the polymeric core or entrapped inside the polymeric body. These NPs are often organic, and the term polymer nanoparticle (PNP) is commonly used in the literature to refer to them. They resemble Nano spheres or Nano capsules for the most part ( Khan et al., 2019 ; Zielińska et al., 2020 ).

4. Types of different metal-based NPs

Metal NPs are purely made of metal precursors. Due to well-known localized surface plasmon resonance (LSPR) characteristics, these NPs possess unique optoelectrical properties. NPs of the alkali and noble metals, i.e., Cu, Ag, and Au, have a broad absorption band in the visible zone of the solar electromagnetic spectrum. The facet, size, and shape-controlled synthesis of metal NPs are essential in present-day cutting-edge materials ( Dreaden et al., 2012 ; Khan et al., 2019 ).

4.1. Silver nanoparticles (AgNPs)

AgNPs are particles with a size range of 1–100 nanometers made of silver. They have unique physical and chemical properties due to their small size, high surface area-to-volume ratio, and ability to absorb and scatter light in the visible and near-infrared range. Because of their relatively small size and high surface-to-volume ratios, which cause chemical and physical differences in their properties compared to their bulk counterparts, silver nanoparticles may exhibit additional antimicrobial capabilities not exerted by ionic silver ( Shenashen et al., 2014 ).

Besides, AgNPs can be created in various sizes and forms depending on the manufacturing process, the most common of which is chemical reduction. The AgNPs were created by chemically reducing a 12 mM AgNO3 aqueous solution. The reaction was carried out in an argon environment using 70 mL of this solution containing PVP (keeping the molar ratio of the repeating unit of PVP and Ag equal to 34) and 21 mL of Aloe Vera. The mixture was agitated in ultrasonic for 45 min at ambient temperature, then heated 2°C/min to 80°C and left for 2 h to generate a transparent solution with tiny suspended particles that must be removed by simple filtering ( Shenashen et al., 2014 ; Gloria et al., 2017 ).

4.2. Zinc nanoparticles (ZnONPs)

Zinc nanoparticles (ZnONPs) are particles with a size range of 1–100 nm made of zinc. Zinc oxide (ZnO) NPs are a wide band gap semiconductor with a room temperature energy gap of 3.37 eV. Its catalytic, electrical, optoelectronic, and photochemical capabilities have made it widely worthwhile ( Kumar S.S. et al., 2013 ). ZnO nanostructures are ideal for catalytic reaction processes ( Chen and Tang, 2007 ). Laser ablation, hydrothermal methods, electrochemical depositions, sol-gel method, chemical vapor deposition, thermal decomposition, combustion methods, ultrasound, microwave-assisted combustion method, two-step mechanochemical-thermal synthesis, anodization, co-precipitation, electrophoretic deposition, and precipitation processes are some methods for producing ZnO nanoparticles ( Madathil et al., 2007 ; Moghaddam et al., 2009 ; Ghorbani et al., 2015 ).

4.3. Copper nanoparticles (CuNPs)

Copper nanoparticles (CuNPs) comprise a size range of 1–100 nm of copper-based particles ( Khan et al., 2019 ). Cu and Au metal fluorescence have long been known to exist. For excitation at 488 nm, a fluorescence peak centering on the metals’ interband absorption edge has been noted. Additionally, it was noted that the fluorescence peaked at the same energy at two distinct excitation wavelengths (457.9–514.5 and 300–400 nm), and the high-energy tail somewhat grows with increased photon energy pumping. A unique, physical, top-down EEW approach has been used to create Cu nanoparticles. The EEW method involves sending a current of *1,010 A/m2 (1,010 A/m2) across a thin Cu wire, which explodes on a Cu plate for a duration of 10–6 s ( Siwach and Sen, 2008 ).

4.4. Gold nanoparticles (AuNPs)

Gold nanoparticles(AuNPs) are nanometers made of gold. They have unique physical and chemical properties and can absorb and scatter light in the visible and near-infrared range ( Rad et al., 2011 ; Compostella et al., 2017 ).

Scientists around the turn of the 20th century discovered anisotropic AuNPs. Zsigmond ( Li et al., 2014 ) said that gold particles “are not always spherical when their size is 40 nm or lower” in his book, released in 1909. Additionally, he found anisotropic gold particles of various colors. Zsigmondy won the Nobel Prize in 1925 for “his demonstration of the heterogeneous character of colloidal solutions and the methods he utilized” and for developing the ultramicroscope, which allowed him to see the forms of Au particles. He noticed that gold frequently crystallized into a six-sided leaf shape ( Li et al., 2014 ).

AuNPs are the topic of extensive investigation due to their optical, electrical, and molecular-recognition capabilities, with numerous prospective or promised uses in a wide range of fields, including electron microscopy, electronics, nanotechnology, materials science, and biomedicine ( Rad et al., 2011 ).

4.5. Aluminum nanoparticles (AlNPs)

Aluminum nanoparticles (AlNPs) are nanoparticles made of aluminum. Aluminum nanoparticles’ strong reactivity makes them promising for application in high-energy compositions, hydrogen generation in water processes, and the synthesis of alumina 2D and 3D structures ( Lerner et al., 2016 ).

4.6. Iron nanoparticles (FeNPs)

Iron nanoparticles(FeNPs) are particles with a size range of 1−100 nanometers ( Khan et al., 2019 ) made of iron. FeNPs have several potential applications, including their use as catalysts, drug delivery systems, sensors, and energy storage and conversion. They have also been investigated for use in photovoltaic and solar cells and water purification and environmental remediation. FeNPs can also be used in magnetic resonance imaging (MRI) as contrast agents to improve the visibility of tissues and organs. They can also be used in magnetic recording media, such as hard disk drives ( Zhuang and Gentry, 2011 ; Jamkhande et al., 2019 ).

As with any NPs, there are potential health and safety concerns associated with using FeNPs, e.g., FeNPs are used to deliver drugs to specific locations within the body, such as cancer cells and used in MRI, and used to remove contaminants from water ( Farrell et al., 2003 ; Zhuang and Gentry, 2011 ). Tables 1 , 2 show the characteristics of metal-based nanoparticles and the techniques to study their characteristics, respectively.

Table 1. Characteristics of metal based nanoparticles.

Table 2. Different analytical techniques and their purposes in studying nanoparticles.

5. Approaches for the synthesis of metal NPs

There are mainly three types of approaches for the synthesis of NPs: the physical, chemical, and biological approaches. The physical approach is also called the top-down approach, while chemical and biological approaches are collectively called the bottom-up approach. The biological approach is also named green systems of NPs. All these approaches are further sub-categorized into various types based upon their method adopted. Figure 1 illustrates each approach’s reported methods for synthesizing NPs.

Figure 1. Approaches of NPs synthesis.

5.1. Top down/physical approach

Bulk materials are fragmented in top-down methods to create nano-structured materials ( Figure 2 ). They are additionally known as physical approaches ( Baig et al., 2021 ). The following techniques can achieve a top-down approach

Figure 2. Difference between top-down and bottom-up approaches.

5.1.1. Mechanical milling

The mechanical milling process uses balls inside containers and may be carried out in various mills, typically planetary and shaker mills, which is an impact process with high energy ( Gorrasi and Sorrentino, 2015 ). Mechanical milling is a practical approach for creating materials at the nanoscale from bulk materials. Aluminum alloys that have been strengthened by oxide and carbide, spray coatings that are resistant to wear, nanoalloys based on aluminum, nickel, magnesium, and copper, and a variety of other nanocomposite materials may all be created mechanically. A unique class of nanoparticles known as ball-milled carbon nanomaterials has the potential to meet the needs for energy storage, energy conversion, and environmental remediation ( Yadav et al., 2012 ; Lyu et al., 2017 ).

5.1.2. Electrospinning

Typically, it is used to create nanofibers from various materials, most often polymers ( Ostermann et al., 2011 ). A technique for creating fibers called electrospinning draws charged threads from polymer melts or solutions up to fiber sizes of a few hundred nanometers ( Chronakis, 2010 ). Coaxial electrospinning was a significant advancement in the field of electrospinning. The spinneret in coaxial electrospinning is made up of two coaxial capillaries. Core-shell nanoarchitectures may be created in these capillaries using two viscous liquids, a viscous liquid as the shell and a non-viscous liquid as the core ( Du et al., 2012 ). Core-shell and hollow polymer, inorganic, organic, and hybrid materials have all been developed using this technique ( Kumar R. et al., 2013 ).

5.1.3. Laser ablation

A microfeature can be made by employing a laser beam to vaporize a single material ( Tran and Wen, 2014 ). Laser ablation synthesis produces nanoparticles by striking the target material with an intense laser beam. Due to the high intensity of the laser irradiation used in the laser ablation process, the source material or precursor vaporizes, causing the production of nanoparticles ( Amendola and Meneghetti, 2009 ). Laser ablation is an environmentally friendly for producing noble metal nanoparticles ( Baig et al., 2021 ). This method may be used to create a wide variety of nanomaterials, including metal nanoparticles, carbon nanomaterials, oxide composites, and ceramics ( Su and Chang, 2018 ; Baig et al., 2021 ).

5.1.4. Sputtering

Microparticles of a solid material are expelled off its surface during the phenomenon known as sputtering, which occurs when the solid substance is assaulted by intense plasma or gas particles ( Behrisch, 1981 ). According to the incident gaseous ion energy, energetic gaseous ions used in the sputtering deposition process physically expel tiny atom clusters off the target surface ( Muñoz-García et al., 2009 ). The sputtering method is intriguing because it is more affordable than electron-beam lithography, and the composition of the sputtered nanomaterials is similar to the target material with fewer contaminants ( Baig et al., 2021 ).

5.1.5. Electron explosion

In this technique, a thin metal wire is subjected to a high current pulse that causes an explosion, evaporation, and ionization. The metal becomes vaporized and ionized, expands, and cools by reacting with the nearby gas or liquid medium. The condensed vapor finally forms the nanoparticles ( Joh et al., 2013 ). Electron explosion method because it produces plasma from the electrical explosion of a metallic wire, which may produce nanoparticles from a Pt solution without using a reducing agent ( Joh et al., 2013 ).

5.1.6. Sonication

The most crucial step in the creation of nanofluids is sonication. After the mixture has been magnetically stirred in a magnetic stirrer, sonication is performed in an ultrasonication path, ultrasonic vibrator, and mechanical homogenizer. Sonicators have become the industry standard for Probe sonication and are noticeably more powerful and effective when compared to ultrasonic cleaner baths for nanoparticle applications. Probe sonication is highly effective for processing nanomaterials (carbon nanotubes, graphene, inks, metal oxides, etc.) ( Zheng et al., 2010 ).

5.1.7. Pulsed wire discharge method

This is the most used method for creating metal nanoparticles. A pulsating current causes a metal wire to evaporate, producing a vapor that is subsequently cooled by an ambient gas to form nanoparticles. This plan may quickly produce large amounts of energy ( Patil et al., 2021 ).

5.1.8. Arc discharge method

Two graphite rods are adjusted in a chamber with a constant helium pressure during the Arc Discharge procedure. It is crucial to fill the chamber with helium because oxygen or moisture prevents the synthesis of fullerenes. Arc discharge between the ends of the graphite rods drives the vaporization of carbon rods. Achieving new types of nanoparticles depends significantly on the circumstances in which arc discharge occurs. The creation of several nanostructured materials may be accomplished with this technique ( Berkmans et al., 2014 ). It is well-recognized for creating carbon-based materials such as fullerenes, carbon nanohorns (CNHs), carbon nanotubes ( Shi et al., 2000 ), few-layer graphene, and amorphous spherical carbon nanoparticles ( Kumar R. et al., 2013 ).

5.1.9. Lithography

Lithography typically uses a concentrated beam of light or electrons to create nanoparticles, a helpful technique ( Pimpin and Srituravanich, 2012 ). Masked and maskless lithography are the two primary categories of lithography. Without a mask, arbitrary nano-pattern printing is accomplished in maskless lithography. Additionally, it is affordable and easy to apply ( Brady et al., 2019 ).

5.2. Bottom-up approach

Tiny atoms and molecules are combined in bottom-up methods to create nano-structured particles ( Figure 2 ; Baig et al., 2021 ). These include chemical and biological approaches:

5.2.1. Chemical vapor deposition (CVD)

Through a chemical process involving vapor-phase precursors, a thin coating is created on the substrate surface during CVD ( Dikusar et al., 2009 ). Precursors are deemed appropriate for CVD if they exhibit sufficient volatility, high chemical purity, strong evaporation stability, cheap cost, a non-hazardous nature, and long shelf life. Additionally, its breakdown should not leave behind any contaminants. Vapor phase epitaxy, metal-organic CVD, atomic layer epitaxy, and plasma-enhanced CVD are only a few CVD variations. This method’s benefits include producing very pure nanoparticles that are stiff, homogeneous, and strong ( Ago, 2015 ). CVD is an excellent approach to creating high-quality nanomaterials ( Machac et al., 2020 ). It is also well-known for creating two-dimensional nanoparticles ( Baig et al., 2021 ).

5.2.2. Sol-gel process

A wet-chemical approach, called the sol-gel method, is widely utilized to create nanomaterials ( Das and Srivasatava, 2016 ; Baig et al., 2021 ). Metal alkoxides or metal precursors in solution are condensed, hydrolyzed, and thermally decomposed. The result is a stable solution or sol. The gel gains greater viscosity as a result of hydrolysis or condensation. The particle size may be seen by adjusting the precursor concentration, temperature, and pH levels. It may take a few days for the solvent to be removed, for Ostwald ripening to occur, and for the phase to change during the mature stage, which is necessary to enable the growth of solid mass. To create nanoparticles, the unstable chemical ingredients are separated. The generated material is environmentally friendly and has many additional benefits thanks to the sol-gel technique ( Patil et al., 2021 ). The uniform quality of the material generated, the low processing temperature, and the method’s ease in producing composites and complicated nanostructures are just a few of the sol-gel technique’s many advantages ( Parashar et al., 2020 ).

5.2.3. Co-precipitation

It is a solvent displacement technique and is a wet chemical procedure. Ethanol, acetone, hexane, and non-solvent polymers are examples of solvents. Polymer phases can be either synthetic or natural. By mixing the polymer solution, fast diffusion of the polymer-solvent into the non-solvent phase of the polymer results. Interfacial stress at two phases results in the formation of nanoparticles ( Das and Srivasatava, 2016 ). This method’s natural ability to produce high quantities of water-soluble nanoparticles through a straightforward process is one of its key benefits. This process is used to create many commercial iron oxide NP-based MRI contrast agents, including Feridex, Reservist, and Combidex ( Baig et al., 2021 ; Patil et al., 2021 ).

5.2.4. Inert gas condensation/molecular condensation

Metal NPs are produced using this method in large quantities. Making fine NPs using the inactive gas compression approach has been widespread, which creates NPs by causing a metallic source to disappear in an inert gas. At an attainable temperature, metals evaporate at a tolerable pace. Copper metal nanoparticles are created by vaporizing copper metal inside a container containing argon, helium, or neon. The atom quickly loses its energy by cooling the vaporized atom with an inert gas after it boils out. Liquid nitrogen is used to cool the gases, forming nanoparticles in the range of 2–100 nm ( Pérez-Tijerina et al., 2008 ; Patil et al., 2021 ).

5.2.5. Hydrothermal

In this method, for the production of nanoparticles, hydrothermal synthesis uses a wide temperature range from ambient temperature to extremely high temperatures. Comparing this strategy to physical and biological ones offers several benefits. At higher temperature ranges, the nanomaterials produced by hydrothermal synthesis could become unstable ( Banerjee et al., 2008 ; Patil et al., 2021 ).

5.2.6. Green/biological synthesis

The synthesis of diverse metal nanoparticles utilizing bioactive agents, including plant materials, microbes, and various biowastes like vegetable waste, fruit peel waste, eggshell, agricultural waste, algae, and so on, is known as “green” or “biological” nanoparticle synthesis ( Kumari et al., 2021 ). Developing dependable, sustainable green synthesis technologies is necessary to prevent the formation of undesirable or dangerous byproducts ( Figure 3 ). The green synthesis of nanoparticles also has several advantages, including being straightforward, affordable, producing NPs with high stability, requiring little time, producing non-toxic byproducts, and being readily scaled up for large-scale synthesis ( Malhotra and Alghuthaymi, 2022 ).

Figure 3. Schematic diagram for biosynthesis of NPs.

5.2.6.1. Biological synthesis using microorganisms

Microbes use metal capture, enzymatic reduction, and capping to create nanoparticles. Before being converted to nanoparticles by enzymes, metal ions are initially trapped on the surface or interior of microbial cells ( Ghosh et al., 2021 ). Use of microorganisms (especially marine microbes) for synthesis of metalic NPs is environmental friendly, fast and economical ( Patil and Kim, 2018 ). Several microorganisms are used in the synthesis of metal NPs, including:

Biosynthesis of NPs by bacteria: A possible biofactory for producing gold, silver, and cadmium sulfide nanoparticles is thought to be bacterial cells. It is known that bacteria may produce inorganic compounds either inside or outside of their cells ( Hulkoti and Taranath, 2014 ). Desulforibrio caledoiensis ( Qi et al., 2013 ), Enterococcu s sp. ( Rajeshkumar et al., 2014 ), Escherichia coli VM1 ( Maharani et al., 2016 ), and Ochrobactrum anhtropi ( Thomas et al., 2014 ) based metal NPs are reported previously for their potential photocatalytic properties ( Qi et al., 2013 ), antimicrobial activity ( Rajeshkumar et al., 2014 ), and anticancer activity ( Maharani et al., 2016 ).

Extracellular synthesis of NPs by bacteria: The microorganisms’ extracellular reductase enzymes shrink the silver ions to the nanoscale range. According to protein analysis of microorganisms, the NADH-dependent reductase enzyme carries out the bio-reduction of silver ions to AgNPs. The electrons for the reductase enzyme come from NADH, which is subsequently converted to NAD+. The enzyme is also oxidized simultaneously when silver ions are reduced to nanosilver. It has been noted that bio-reduction can occasionally be caused by nitrate-dependent reductase. The decline occurs within a few minutes in the quick extracellular creation of nanoparticles ( Mathew et al., 2010 ). At pH 7, the bacterium R. capsulata produced gold nanoparticles with sizes ranging from 10−20 nm. Numerous nanoplates and spherical gold nanoparticles were produced when the pH was changed to four ( Sriram et al., 2012 ). By adjusting the pH, the gold nanoparticles’ form may be changed. Gold nanoparticle shape was controlled by regulating the proton content at various pH levels. The bacteria R. capsulata ’s release cofactor NADH and NADH-dependent enzymes may cause the bioreduction of Au (3+) to Au (0) and the generation of gold nanoparticles. By using NADH-dependent reductase as an electron carrier, it is possible to start the reduction of gold ions ( Sriram et al., 2012 ).

Intracellular synthesis of NPs by bacteria: Three processes are involved in the intracellular creation of NPs: trapping, bioreduction, and capping. The cell walls of microorganisms and ions charge contribute significantly to creating NPs in the intracellular route. This entails specific ion transit in the presence of enzymes, coenzymes, and other molecules in the microbial cell. Microbes have a range of polysaccharides and proteins in their cell walls, which function as active sites for the binding of metal ions ( Slavin et al., 2017 ). Not all bacteria can produce metal and metal oxide nanoparticles. The only ions that pose a significant hazard to microorganisms are heavy metal ions, which, in response to a threat, cause the germs to react by grabbing or trapping the ions on the cell wall via electrostatic interactions. This occurs because a metal ion is drawn to the cell wall’s carboxylate groups, including cysteine and polypeptides, and certain enzymes with a negative charge ( Zhang et al., 2011 ).

Additionally, the electron transfers from NADH via NADH-dependent educates, which serves as an electron carrier and is located inside the plasma membrane, causing the trapped ions to be reduced into the elemental atom. The nuclei eventually develop into NPs and build up in the cytoplasm or the pre-plasmic space. On the other hand, the stability of NPs is provided by proteins, peptides, and amino acids found inside cells, including cysteine, tyrosine, and tryptophan ( Mohd Yusof et al., 2019 ).

Biosynthesis of NPs by fungi: Because monodisperse nanoparticles with distinct dimensions, various chemical compositions, and sizes may be produced, the biosynthesis of nanoparticles utilizing fungus is frequently employed. Due to the existence of several enzymes in their cells and the ease of handling, fungi are thought to be great candidates for producing metal and metal sulfide nanoparticles ( Mohanpuria et al., 2008 ).

The nanoparticles were created on the surface of the mycelia. After analyzing the results and noting the solution, it was determined that the Ag + ions are initially trapped on the surface of the fungal cells by an electrostatic interaction between gold ions and negatively charged carboxylate groups, which is facilitated by enzymes that are present in the mycelia’s cell wall. Later, the enzymes in the cell wall reduce the silver ions, causing the development of silver nuclei. These nuclei then increase as more Ag ions are reduced and accumulate on them.

The TEM data demonstrate the presence of some silver nanoparticles both on and inside the cytoplasmic membrane. The findings concluded that the Ag ions that permeate through the cell wall were decreased by enzymes found inside the cytoplasm and on the cytoplasmic membrane. Also possible is the diffusion of some silver nanoparticles over the cell wall and eventual cytoplasmic entrapment ( Mukherjee et al., 2001 ; Hulkoti and Taranath, 2014 ).

It was observed that the culture’s age does not affect the shape of the synthesized gold nanoparticles. However, the number of particles decreased when older cells were used. The different pH levels produce a variety of shapes of gold nanoparticles, indicating that pH plays a vital role in determining the shape. The incubation temperature also played an essential role in the accumulation of the gold nanoparticles. It was observed that the particle growth rate was faster at increased temperature levels ( Mukherjee et al., 2001 ; Ahmad et al., 2003 ). The form of the produced gold nanoparticles was shown to be unaffected by the age of the culture. However, when older cells were utilized, the particle count fell. The fact that gold nanoparticles take on various forms at different pH levels suggests that the pH is crucial in determining the shape. The incubation temperature significantly influenced the accumulation of the gold nanoparticles. It was found that higher temperatures caused the particle development rate to accelerate ( Mukherjee et al., 2001 ; Ahmad et al., 2003 ). Verticillium luteoalbum is reported to synthesize gold nanoparticles of 20–40 nm in size ( Erasmus et al., 2014 ). Aspergillus terreus and Penicillium brevicompactum KCCM 60390 based metal NPs are reported for their antimicrobial ( Li G. et al., 2011 ) and cytotoxic activities ( Mishra et al., 2011 ), respectively.

Biosynthesis of NPs using actinomycetes: Actinomycetes have been categorized as prokaryotes since they share significant traits with fungi. They are sometimes referred to as ray fungi ( Mathew et al., 2010 ). Making NPs from actinomycetes is the same as that of fungi ( Sowani et al., 2016 ). Thermomonospora sp., a new species of extremophilic actinomycete, was discovered to produce extracellular, monodispersed, spherical gold nanoparticles with an average size of 8 nm ( Narayanan and Sakthivel, 2010 ). Metal NPs synthesized by Rhodococcus sp. ( Ahmad et al., 2003 ) and Streptomyces sp. Al-Dhabi-87 ( Al-Dhabi et al., 2018 ) are reported for their antimicrobial activities.

Biosynthesis of NPs using algae: Algae have a high concentration of polymeric molecules, and by reducing them, they may hyper-accumulate heavy metal ions and transform them into malleable forms. Algal extracts typically contain pigments, carbohydrates, proteins, minerals, polyunsaturated fatty acids, and other bioactive compounds like antioxidants that are used as stabilizing/capping and reducing agents ( Khanna et al., 2019 ). NPs also have a faster rate of photosynthesis than their biosynthetic counterparts. Live or dead algae are used as model organisms for the environmentally friendly manufacturing process of bio-nanomaterials, such as metallic NPs ( Hasan, 2015 ). Ag and Au are the most extensively researched noble metals to synthesized NPs by algae either intracellularly or extracellularly ( Dahoumane et al., 2017 ). Chlorella vulgaris ( Luangpipat et al., 2011 ), Chlorella pyrenoidosa ( Eroglu et al., 2013 ), Nanochloropsis oculata ( Xia et al., 2013 ), Scenedesmus sp. IMMTCC-25 ( Jena et al., 2014 ) based metal NPs are reported for their potential catalytic ( Luangpipat et al., 2011 ; Eroglu et al., 2013 ) and, antimicrobial ( Eroglu et al., 2013 ; Jena et al., 2014 ) activities along with their use in Li-Ion batteries ( Xia et al., 2013 ).

Intracellular synthesis of NPs using algae: In order to create intracellular NPs, algal biomass must first be gathered and thoroughly cleaned with distilled water. After that, the biomass (living algae) is treated with metallic solutions like AgNO3. The combination is then incubated at a specified pH and a specific temperature for a predetermined time. Finally, it is centrifuged and sonicated to produce the extracted stable NPs ( Uzair et al., 2020 ).

Extracellular synthesis of NPs using algae: Algal biomass is first collected and cleaned with distilled water before being used to synthesize NPs extracellularly ( Uzair et al., 2020 ). The following three techniques are frequently utilized for the subsequent procedure:

(i) A particular amount of time is spent drying the algal biomass (dead algae), after which the dried powder is treated with distilled water and filtered.

(ii) The algal biomass is sonicated with distilled water to get a cell-free extract.

(iii) The resultant product is filtered after the algal biomass has been rinsed with distilled water and incubated for a few hours (8–16 h).

5.2.6.2. Biological synthesis using plant extracts

The substance or active ingredient of the desired quality extracted from plant tissue by treatment for a particular purpose is a plant extract ( Jadoun et al., 2021 ). Plant extracts are combined with a metal salt solution at room temperature to create nanoparticles. Within minutes, the response is finished. This method has been used to create nanoparticles of silver, gold, and many other metals ( Li X. et al., 2011 ). Nanoparticles are biosynthesized using a variety of plants. It is known that the kind of plant extract, its concentration, the concentration of the metal salt, the pH, temperature, and the length of contact time all have an impact on how quickly nanoparticles are produced as well as their number and other properties ( Mittal and Chisti, 2013 ). A leaf extract from Polyalthia longifolia was used to create silver nanoparticles, the average particle size was around 58 nm ( Kumar and Yadav, 2009 ; Kumar et al., 2016 ).

Acacia auriculiformis ( Saini et al., 2016 ), Anisomeles indica ( Govindarajan et al., 2016 ), Azadirachta indica ( Velusamy et al., 2015 ), Bergenia ciliate ( Phull et al., 2016 ), Clitoria ternatea , Solanum nigrum ( Krithiga et al., 2013 ), Coffea arabica ( Dhand et al., 2016 ), Coleus forskohlii ( Naraginti et al., 2016 ), Curculigo orchioides ( Kayalvizhi et al., 2016 ), Digitaria radicosa ( Kalaiyarasu et al., 2016 ), Dioscorea alata ( Pugazhendhi et al., 2016 ), Diospyros paniculata ( Rao et al., 2016 ), Elephantopus scaber ( Kharat and Mendhulkar, 2016 ), Emblica officinalis ( Ramesh et al., 2015 ), Euphorbia antiquorum L. ( Rajkuberan et al., 2017 ), Ficus benghalensis ( Nayak et al., 2016 ), Lantana camara ( Ajitha et al., 2015 ), Cinnamomum zeylanicum ( Soni and Sonam, 2014 ), and Parkia roxburghii ( Paul et al., 2016 ) are the few examples of plants which are reported for the green synthesis of metal NPs (i.e., AgNPs). These were evaluated for their antifilaria activity ( Saini et al., 2016 ), mosquitocidal activity ( Govindarajan et al., 2016 ), antibacterial activity ( Velusamy et al., 2015 ), catalytic activity ( Edison et al., 2016 ), antioxidant activity ( Phull et al., 2016 ), and Cytotoxicity ( Patil et al., 2017 ).

5.2.6.3. Biological synthesis using biomimetic

“Biomimetic synthesis” typically refers to chemical processes that resemble biological synthesis carried out by living things ( Dahoumane et al., 2017 ). In the biomimetic approach, proteins, enzymes, cells, viruses, pollen, and waste biomass are used to synthesize NPs. Two categories are used to classify biomimetic synthesis:

Functional biomimetic synthesis uses various materials and approaches to emulate particular characteristics of natural materials, structures, and systems ( Zan and Wu, 2016 ).

Process biomimetic synthesis is a technique that aims to create different desirable nanomaterials/structures by imitating the synthesis pathways, processes, or procedures of natural chemicals and materials/structures. For instance, several distinctive nano-superstructures (such as satellite structures, dendrimer-like structures, pyramids, cubes, 2D nanoparticle arrays, 3D AuNP tubes, etc.) have been put together in vitro by simulating the protein manufacturing process ( Zan and Wu, 2016 ).

6. Applications of NPs

6.1. applications of nps in environment industry.

Due to their tiny size and distinctive physical and chemical characteristics, NPs appeal to various environmental applications. The properties of nanoparticals and their advantages are illustrated in Figure 4 . The following are some possible NP uses in the environment.

Figure 4. Properties of nanoparticals and their advantages.

6.1.1. Bioremediation

Nanoparticles (NPs) can remove environmental pollutants, such as heavy metals from water or organic contaminants from soil ( Zhuang and Gentry, 2011 ). For example, silver nanoparticles (AgNPs) effectively degrade certain pollutants, such as organic dyes and compounds found in wastewater. Several nanomaterials have been considered for remediation purposes, such as nanoscale zeolites, metal oxides, and carbon nanotubes and fibers ( Zhuang and Gentry, 2011 ). Nanoscale particles used in remediation can access areas that larger particles cannot. They can be coated to facilitate transport and prevent reaction with surrounding soil matrices before reacting with contaminants. One widely used nanomaterial for remediation is Nanoscale zerovalent iron (nZVI). It has been used at several hazardous waste sites to clean up chlorinated solvents that have contaminated groundwater ( Elliott et al., 2013 ). Removing heavy metals such as mercury, lead, thallium, cadmium, and arsenic from natural water has attracted considerable attention because of their adverse effects on environmental and human health. Superparamagnetic iron oxide NPs are an effective sorbent material for this toxic soft material. So, no measurements of engineered NPs in the environment have been available due to the absence of analytical methods able to quantify the trace concentration of NPs ( Elliott et al., 2013 ).

6.1.2. Sensors in environment

Nanotechnology/NPs are already being used to improve water quality and assist in environmental clean-up activities ( Pradeep, 2009 ). Their potential use as environmental sensors to monitor pollutants is also becoming viable NPs can be used as sensors to detect the presence of certain compounds in the environment, such as heavy metals or pollutants. The nano-sensors small size and wide detection range provide great flexibility in practical applications. It has been reported that nanoscale sensors can be used to detect microbial pathogens and biological compounds, such as toxins, in aqueous environments ( Yadav et al., 2010 ). NPS can be designed to selectively bind to specific types of pollutants, allowing them to be detected at low concentrations. For example, gold nanoparticles (AuNPs) have been used as sensors for the detection of mercury in water ( Theron et al., 2010 ).

6.1.3. Catalysts in environment

Nanoparticles (NPs) are used as catalysts in chemical reactions, such as in the production of biofuels or environmental remediation processes, and to catalyze biomass conversion into fuels, such as ethanol or biodiesel. For example, platinum nanoparticles (PtNPs) have been explored for use in the production of biofuels due to their ability to catalyze the conversion of biomass into fuels ( Lam and Luong, 2014 ). PtNPs also showed promising sensing properties; for example, Using Pt NPs, the Hg ions were quantified in the range of 50–500 nM in MilliQ, tap, and groundwater samples, and the limit of quantifications for Hg ions were 16.9, 26, and 47.3 nM. The biogenic PtNPs-based probe proved to be applicable for detecting and quantifying Hg ions ( Kora and Rastogi, 2018 ).

Overall, NPs have significant potential for use in the environment and are being actively researched for a variety of applications.

6.2. Applications of NPs in medicine industry

Nanoparticles (NPs) have unique physical and chemical properties due to their small size, making them attractive for use in various applications, including the medicine industry. Some potential applications of NPs in medicine include:

6.2.1. Drug delivery

Technological interest has been given to AuNPs due to their unique optical properties, ease of synthesis, and chemical stability. The particles can be used in biomedical applications such as cancer treatment ( Sun et al., 2014 ), biological imaging ( Abdulle and Chow, 2019 ), chemical sensing, and drug delivery. Sun et al. (2014) mentioned in detail about two different methods of controlled release of drugs associated with NPs, which were (1) sustained (i.e., diffusion-controlled and erosion-controlled) and (2) stimuli-responsive (i.e., pH-sensitive, enzyme-sensitive, thermoresponsive, and photosensitive). Figure 5 illustrates that how NPs acts as targeted delivery of medicines to treat cancer cells ( Figure 5A ) and therapeutic gene delivery to synthesis proteins of interests in targeted cells ( Figure 5B ). NPs can deliver drugs to specific body areas, allowing for more targeted and effective treatment ( Siddique and Chow, 2020 ). For example AgNPs have been explored for use in drug delivery due to their stability and ability to accumulate in certain types of cancerous tumors ( Siddique and Chow, 2020 ). ZnONPs have also been explored for drug delivery due to their ability to selectively target cancer cells ( Anjum et al., 2021 ). CuNPs have been shown to have antimicrobial properties and are being explored for drug delivery to treat bacterial infections ( Yuan et al., 2018 ). AuNPs have unique optical, electrical, and catalytic properties and are being explored for drug delivery due to their ability to accumulate in certain cancerous tumors. Silver NPs (AgNPs) have been incorporated into wound dressings, bone cement, and implants ( Schröfel et al., 2014 ).

Figure 5. Application of nanoparticles as; targated drug delivery (A) , and therapeutic protein generation in targated cells (B) .

6.2.2. Diagnostics

Nanoparticles (NPs) can be used as imaging agents to help visualize specific body areas. For example, iron oxide nanoparticles (Fe 3 O 4 NPs) have been used as magnetic resonance imaging (MRI) contrast agents to help visualize tissues and organs ( Nguyen et al., 2013 ). AuNPs have unique optical, electrical, and catalytic properties and are being explored for diagnostics due to their ability to accumulate in certain cancerous tumors ( Siddique and Chow, 2020 ).

6.2.3. Tissue engineering

Nanoparticles (NPs) can help stimulate the growth and repair of tissues and organs. For example, titanium dioxide nanoparticles (TiO2 NPs) have been explored for tissue engineering due to their ability to stimulate the growth of bone cells ( Kim et al., 2014 ).

6.2.4. Antimicrobials

Some NPs, such as silver nanoparticles (AgNPs) and copper nanoparticles (CuNPs), have strong antimicrobial properties and are being explored for use in a variety of medical products, such as wound dressings and medical devices ( Hoseinzadeh et al., 2017 ).

Overall, NPs have significant potential for use in the medical industry and are being actively researched for various applications. However, it is essential to carefully consider the potential risks and benefits of using NPs in medicine and ensure their safe and responsible use.

6.3. Applications of NPs in agriculture industry

There are several ways in which nanoparticles (NPs) have the potential to alter the agricultural sector. NPs may be used in agriculture for a variety of reasons, including:

6.3.1. Pesticides and herbicides

Nanoparticles (NPs) can be used to deliver pesticides and herbicides in a targeted manner, reducing the number of chemicals needed and minimizing the potential for environmental contamination ( Khan et al., 2019 ). AgNPs and CuNPs have antimicrobial properties, making them potentially useful for controlling pests and diseases in crops. They can also be used as delivery systems for active ingredients, allowing for more targeted application and reducing the potential for environmental contamination ( Hoseinzadeh et al., 2017 ; Dangi and Verma, 2021 ).

It is important to note that using metal NPs in pesticides and herbicides is still in the early stages of development. More research is needed to understand their potential impacts on human health and the environment ( Dangi and Verma, 2021 ).

6.3.2. Fertilizers and plant growth

Nano fertilizers offer an opportunity for efficiently improving plant mineral nutrition. Some studies have shown that nanomaterials can be more effective than conventional fertilizers, with a controlled release of nutrients increasing the efficiency of plant uptake and potentially reducing adverse environmental outcomes associated with the loss of nutrients in the broader environment. However, other studies have found that nanomaterial has the same or even less effective effectiveness than conventional fertilizers. NPs used to deliver fertilizers to plants more efficiently, reducing the amount of fertilizer needed, and reducing the risk of nutrient runoff ( Kopittke et al., 2019 ).

Ag ( Jaskulski et al., 2022 ), Zn ( Song and Kim, 2020 ), Cu, Au, Al, and Fe ( Kopittke et al., 2019 ) based NPs have been shown to have fertilizing properties and plant growth-promoting properties, and may help provide essential nutrients to plants and improve plant growth and yield. It is important to note that the use of NPs in fertilizers is still in the early stages of development. More research is needed to understand their potential impacts on human health and the environment.

6.3.3. Food safety

Nanoparticles (NPs) can detect and eliminate pathogens in food products, improving food safety, and reducing the risk of foodborne illness ( Zhuang and Gentry, 2011 ).

6.3.4. Water purification

Nanoparticles (NPs) can purify irrigation water, reducing the risk of crop contamination and improving crop yield ( Zhuang and Gentry, 2011 ). Using NPs in agriculture can improve crop yields, reduce agriculture’s environmental impact, and improve food products’ safety and quality.

6.4. Applications of NPs in food industry

Numerous applications for nanoparticles (NPs) in the food sector are possible, including:

6.4.1. Food processing and food preservation/food packaging

Nanoparticles (NPs) can be used to improve the efficiency and performance of food processing operations, such as grinding, mixing, and drying, e.g., AgNPs have been used as a natural antimicrobial agent in food processing operations, helping to prevent the growth of bacteria and other microorganisms ( Dangi and Verma, 2021 ) and also NPs are used to enhance the performance of materials used in food packaging, making them more resistant to pollutants like moisture and gases.

6.4.2. Food fortification

Nanoparticles (NPs) can deliver essential nutrients to food products, such as vitamins and minerals, more efficiently and effectively. e.g., Fe 2 O 3 , and CuNPs have been used to fortify food products with iron, and Cu is an essential nutrient necessary for the metabolism of iron and other nutrients. Iron is an essential nutrient often lacking in many people’s diets, particularly in developing countries ( Kopittke et al., 2019 ).

6.4.3. Sensors

Nanoparticles (NPs) used to improve the sensitivity and specificity of food sensors, allowing them to detect a broader range of substances or signals ( Yadav et al., 2010 ).

Overall, using NPs in the food industry can improve the performance, safety, and nutritional value of a wide range of food products and processes.

6.5. Applications of NPs in electronics industry and automotive industry

In many aspects, nanoparticles (NPs) can transform the electronics sector. NPs may be used in a variety of electrical applications, such as:

6.5.1. Display technologies/storage devices

Nanoparticles (NPs) can be used to improve the performance of displays ( Park and Choi, 2019 ; Bahadur et al., 2021 ; Triana et al., 2022 ), such as LCD and OLED displays, by enhancing the brightness, color, and contrast of the image, such as silver NPs and gold NPs, have been explored for use in LCD and OLED displays as a means of improving the conductivity of the display ( Gwynne, 2020 ). NPs improve the performance and durability of energy storage devices, such as batteries and supercapacitors, by increasing energy density and charging speed. Zinc oxide nanoparticles (ZnO NPs) have the potential to be used in energy storage devices, such as batteries and supercapacitors, due to their ability to store and release energy ( Singh et al., 2011 ).

6.5.2. Data storage

Nanoparticles (NPs) can improve the capacity and speed of data storage devices, such as hard drives and flash drives. Magnetic NPs, such as iron oxide NPs, have been explored for use in data storage devices, such as hard drives, due to their ability to store, and retrieve data using magnetism. These NPs are often composed of a magnetic metal, such as iron, cobalt, or nickel. They can be magnetized and demagnetized, allowing them to store and retrieve data ( Ahmad et al., 2021 ).

Overall, the use of NPs in electronics has the potential to improve the performance and efficiency of a wide range of electronic devices and systems.

Applications of NPs in chemical industry: The chemical industry might be entirely transformed by nanoparticles (NPs) in various ways. The following are potential uses for NPs in the chemical industry ( Salem and Fouda, 2021 ).

6.5.3. Chemical processing/catalysis

Nanoparticles (NPs) can be used as catalysts in chemical reactions, allowing them to be carried out more efficiently and at lower temperatures. Some examples of metal NPs that have been used as catalysts in the chemical industry include: PtNPs have been used as catalysts in a variety of chemical reactions, including fuel cell reactions ( Bhavani et al., 2021 ), hydrogenation reactions, and oxidation reactions ( Lara and Philippot, 2014 ), PdNPs have been used as catalysts in a variety of chemical reactions, including hydrogenation reactions and cross-coupling reactions ( Pérez-Lorenzo, 2012 ), FeNPs have been used as catalysts in a variety of chemical reactions, including hydrolysis reactions ( Jiang and Xu, 2011 ), and oxygen reduction reactions, NiNPs have been used as catalysts in a variety of chemical reactions, including hydrogenation reactions, and hydrolysis reactions ( Salem and Fouda, 2021 ).

6.5.4. Separation and purification

NPs are used to separate and purify chemicals and other substances, such as gases and liquids, by exploiting their size-based properties ( Hollamby et al., 2010 ). Several types of metal nanoparticles (NPs) have been explored for use in separation and purification processes in the chemical industry, including Fe 2 O 3 NPs have been used to separate and purify gases, liquids, and chemicals. They have also been used to remove contaminants from water ( Pradeep, 2009 ; Siddique and Chow, 2020 ). AgNPs have been used to purify water and remove contaminants ( Pradeep, 2009 ), such as bacteria and viruses. They have also been used to remove heavy metals from water and other substances ( Zhuang and Gentry, 2011 ). AuNPs have been used to purify water and remove contaminants, such as bacteria and viruses ( Siddique and Chow, 2020 ). They have also been used to separate and purify gases and liquids ( Zhuang and Gentry, 2011 ). AlNPs have been used to remove contaminants from water and other substances, such as oils and fuels. They have also been used to purify gases ( Zhuang and Gentry, 2011 ).

6.6. Applications of NPs in defense industry

Nanoparticles (NPs) can be used to improve the efficiency and performance of chemical processing operations, such as refining and synthesizing chemicals ( Schröfel et al., 2014 ). Nanoparticles (NPs) have the potential to be used in the defense industry in several ways, including:

6.6.1. Sensors

Nanoparticles (NPs) can improve the sensitivity and specificity of sensors used in defense systems, such as sensors for detecting chemical, biological, or radiological threats ( Zheng et al., 2010 ).

6.6.2. Protective coatings

Nanoparticles (NPs) can improve the performance and durability of protective coatings applied to defense equipment, such as coatings resistant to chemical or biological agents. For example, metal NPs can improve the mechanical properties and durability of the coating, making it more resistant to wear and corrosion. For example, adding Al or Zn based NPs to a polymer coating can improve its corrosion resistance. In contrast, adding Ni or Cr-based NPs can improve their wear resistance ( Rangel-Olivares et al., 2021 ).

6.6.3. Weapons

Nanoparticles (NPs) are used as weapons against viruses, bacteria, etc, ( Ye et al., 2020 ) and as well as in the development of armor and protective materials. There have been some reports of the potential use of NPs in military and defense applications, such as in the development of armor and protective materials. For example, adding nanoparticles, such as ceramic or metal NPs, to polymers or other materials can improve their mechanical properties and make them more resistant to damage. In addition, there have been reports of the use of NPs in developing sensors and detection systems for defense purposes.

6.6.4. Manufacturing

Nanoparticles (NPs) can improve the performance and durability of materials used in defense equipment, such as armor or structural materials. Metal NPs can be used in materials by adding them as a filler or reinforcement in polymers. For example, the addition of metal NPs such as aluminum (Al), copper (Cu), or nickel (Ni) to polymers can improve the mechanical properties, thermal stability, and electrical conductivity of the resulting composite material ( Khan et al., 2019 ).

Metal NPs can also make functional materials, such as catalysts and sensors. For example, metal NPs, such as gold (Au), and platinum (Pt), can be used as catalysts in various chemical reactions due to their high surface area and ability to adsorb reactants ( Zheng et al., 2010 ).

6.6.5. Energy storage

Nanoparticles (NPs) can improve the performance and efficiency of energy storage systems used in defense systems, such as batteries or fuel cells ( Morsi et al., 2022 ). In batteries, nanoparticles can be used as a cathode material to increase the battery’s energy density, rate capability, and cycling stability. For example, lithium cobalt oxide (LiCoO 2 ) nanoparticles have been used as cathode materials in lithium-ion batteries due to their high capacity and good rate performance. In addition, nanoparticles of transition metal oxides, such as iron oxide (Fe 2 O 3 ), and manganese oxide (MnO 2 ), have been used as cathode materials in rechargeable lithium batteries due to their high capacity and good rate performance. In supercapacitors, nanoparticles can be used as the active material in the electrodes to increase the specific surface area, leading to an increase in the device’s capacitance ( Morsi et al., 2022 ). Using NPs in the defense industry can improve defense systems’ performance, efficiency, and safety.

7. Future perspectives

Metal nanoparticles (NPs) have many potential applications in various fields, including electronics, energy storage, catalysis, and medicine. However, there are also several challenges and potential future directions for developing and using metal NPs.

One major challenge is synthesizing and processing metal NPs with precise size and shape control. Many methods for synthesizing metal NPs involve high temperatures and harsh chemical conditions, which can be challenging to scale up for large-scale production. In addition, the size and shape of metal NPs can significantly impact their properties and potential applications, so it is essential to synthesize NPs with precise size and shape control.

Another challenge is the environmental impact of metal NPs. Some metal NPs, such as silver NPs, can be toxic to aquatic life and may have other environmental impacts. There is a need for more research on the environmental effects of metal NPs and the development of more environmentally friendly (Green) synthesis and processing methods.

In terms of future directions, one promising area is the use of metal NPs for energy storage, conversion, and protection of the environment. For example, metal NPs could be used to improve batteries’ performance or develop more efficient solar cells. In addition, metal NPs could be used in catalysis to improve the efficiency of chemical reactions. There is also ongoing research on metal NPs in medicine, including drug delivery and cancer therapy.

Author contributions

KAA: conceptualization, methodology, validation, formal analysis, investigation, writing – original draft, writing – review and editing, and visualization.

Acknowledgments

The author thanks Prof. Dr. Mona M. Sobhy, Department of Reproductive Diseases, Animal Reproduction Research Institute, ARC, Giza, Egypt, and Dr. Omar Hewedy, University of Guelph, Canada, for the critical reading of the manuscript.

Conflict of interest

The author declares that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

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Keywords : green synthesis, nanoparticles, nanotechnology, biological synthesis, microbial nanotechnology, bionanotechnology

Citation: Altammar KA (2023) A review on nanoparticles: characteristics, synthesis, applications, and challenges. Front. Microbiol. 14:1155622. doi: 10.3389/fmicb.2023.1155622

Received: 31 January 2023; Accepted: 21 March 2023; Published: 17 April 2023.

Reviewed by:

Copyright © 2023 Altammar. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY) . The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Khadijah A. Altammar, [email protected] ; orcid.org/0000-0002-8691-086X

Disclaimer: All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.

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Nanotechnology: A Revolution in Modern Industry

Shiza malik.

1 Bridging Health Foundation, Rawalpindi 46000, Pakistan

Khalid Muhammad

2 Department of Biology, College of Science, UAE University, Al Ain 15551, United Arab Emirates

Yasir Waheed

3 Office of Research, Innovation, and Commercialization (ORIC), Shaheed Zulfiqar Ali Bhutto Medical University (SZABMU), Islamabad 44000, Pakistan

4 Gilbert and Rose-Marie Chagoury School of Medicine, Lebanese American University, Byblos 1401, Lebanon

Associated Data

Not applicable.

Nanotechnology, contrary to its name, has massively revolutionized industries around the world. This paper predominantly deals with data regarding the applications of nanotechnology in the modernization of several industries. A comprehensive research strategy is adopted to incorporate the latest data driven from major science platforms. Resultantly, a broad-spectrum overview is presented which comprises the diverse applications of nanotechnology in modern industries. This study reveals that nanotechnology is not limited to research labs or small-scale manufacturing units of nanomedicine, but instead has taken a major share in different industries. Companies around the world are now trying to make their innovations more efficient in terms of structuring, working, and designing outlook and productivity by taking advantage of nanotechnology. From small-scale manufacturing and processing units such as those in agriculture, food, and medicine industries to larger-scale production units such as those operating in industries of automobiles, civil engineering, and environmental management, nanotechnology has manifested the modernization of almost every industrial domain on a global scale. With pronounced cooperation among researchers, industrialists, scientists, technologists, environmentalists, and educationists, the more sustainable development of nano-based industries can be predicted in the future.

1. Introduction

Nanotechnology has slowly yet deeply taken over different industries worldwide. This rapid pace of technological revolution can especially be seen in the developed world, where nano-scale markets have taken over rapidly in the past decade. Nanotechnology is not a new concept since it has now become a general-purpose technology. Four generations of nanomaterials have emerged on the surface and are used in interdisciplinary scientific fields; these are active and passive nanoassemblies, general nanosystems, and small-scale molecular nanosystems [ 1 ].

This rapid development of nanoscience is proof that, soon, nano-scale manufacturing will be incorporated into almost every domain of science and technology. This review article will cover the recent advanced applications of nanotechnology in different industries, mainly agriculture, food, cosmetics, medicine, healthcare, automotive, oil and gas industries, chemical, and mechanical industries [ 2 , 3 ]. Moreover, a brief glimpse of the drawbacks of nanotechnology will be highlighted for each industry to help the scientific community become aware of the ills and benefits of nanotechnology side by side. Nanotechnology is a process that combines the basic attributes of biological, physical, and chemical sciences. These processes occur at the minute scale of nanometers. Physically, the size is reduced; chemically, new bonds and chemical properties are governed; and biological actions are produced at the nano scale, such as drug bonding and delivery at particular sites [ 4 , 5 ].

Nanotechnology provides a link between classical and quantum mechanics in a gray area called a mesoscopic system. This mesoscopic system is being used to manufacture nanoassemblies of nature such as agricultural products, nanomedicine, and nanotools for treatment and diagnostic purposes in the medical industry [ 6 ]. Diseases that were previously untreatable are now being curtailed via nano-based medications and diagnostic kits. This technology has greatly affected bulk industrial manufacturing and production as well. Instead of manufacturing materials by cutting down on massive amounts of material, nanotechnology uses the reverse engineering principle, which operates in nature. It allows the manufacturing of products at the nano scale, such as atoms, and then develops products to work at a deeper scale [ 7 ].

Worldwide, millions and billions of dollars and euros are being spent in nanotechnology to utilize the great potential of this new science, especially in the developed world in Europe, China, and America [ 8 ]. However, developing nations are still lagging behind as they are not even able to meet the industrial progression of the previous decade [ 9 ]. This lag is mainly because these countries are still fighting economically, and they need some time to walk down the road of nanotechnology. However, it is pertinent to say that both the developed and developing world’s scientific communities agree that nanotechnology will be the next step in technological generation [ 10 ]. This will make further industrial upgrading and investment in the field of nanotechnology indispensable in the coming years.

With advances in science and technology, the scientific community adopts technologies and products that are relatively cheap, safe, and cleaner than previous technologies. Moreover, they are concerned about the financial standing of technologies, as natural resources in the world are shrinking excessively [ 11 ]. Nanotechnology thus provides a gateway to this problem. This technology is clear, cleaner, and more affordable compared to previous mass bulking and heavy machinery. Moreover, nanotechnology holds the potential to be implemented in every aspect of life. This will mainly include nanomaterial sciences, nanoelectronics, and nanomedicine, being inculcated in all dimensions of chemistry and the physical and biological world [ 12 ]. Thus, it is not wrong to predict that nanotechnology will become a compulsory field of study for future generations [ 13 ]. This review inculcates the basic applications of nanotechnology in vital industries worldwide and their implications for future industrial progress [ 14 ].

2. Nanotechnology Applications

2.1. applications of nanotechnology in different industries.

After thorough and careful analyses, a wide range of industries—in which nanotechnology is producing remarkable applications—have been studied, reviewed, and selected to be made part of this review. It should be notified that multiple subcategories of industrial links may be discussed under one heading to elaborate upon the wide-scale applications of nanotechnology in different industries. A graphical abstract at the beginning of this article indicates the different industries in which nanotechnology is imparting remarkable implications, details of which are briefly discussed under different headings in the next session.

2.2. Nanotechnology and Computer Industry

Nanotechnology has taken its origins from microengineering concepts in physics and material sciences [ 15 ]. Nanoscaling is not a new concept in the computer industry, as technologists and technicians have been working for a long time to design such modified forms of computer-based technologies that require minimum space for the most efficient work. Resultantly, the usage of nanotubes instead of silicon chips is being increasingly experimented upon in computer devices. Feynman and Drexler’s work has greatly inspired computer scientists to design revolutionary nanocomputers from which wide-scale advantages could be attained [ 13 ]. A few years ago, it was an unimaginable to consider laptops, mobiles, and other handy gadgets as thin as we have today, and it is impossible for even the common man to think that with the passage of time, more advanced, sophisticated, and lighter computer devices will be commonly used. Nanotechnology holds the potential to make this possible [ 16 ].

Energy-efficient, sustainable, and urbanized technologies have been emerging since the beginning of the 21st century. The improvement via nanotechnology in information and communication technology (ICT) is noteworthy in terms of the improvements achieved in interconnected communities, economic competitiveness, environmental stability during demographic shifts, and global development [ 17 ]. The major implications of renewable technology incorporate the roles of ICT and nanotechnology as enablers of environmental sustainability. The traditional methods of product resizing, re-functioning, and enhanced computational capabilities, due to their expensiveness and complicated manufacturing traits, have slowly been replaced by nanotechnological renovations. Novel technologies such as smart sensors logic elements, nanochips, memory storage nanodevices, optoelectronics, quantum computing, and lab-on-a-chip technologies are important in this regard [ 18 ].

Both private and public spending are increasing in the field of nanocomputing. The growth of marketing and industrialization in the biotechnology and computer industries are running in parallel, and their expected growth rates for the coming years are far higher. Researchers and technologists believe that by linking the advanced field of nanotechnology and informatics and computational industries, various problems in human society such as basic need fulfillment can be easily accomplished in line with the establishment of sustainable goals by the end of this decade [ 19 ]. The fourth industrial revolution is based upon the supporting pillars derived from hyperphysical systems including artificial intelligence, machine learning, the internet of things, robots, drones, cloud computing, fast internet technologies (5G and 6G), 3D printing, and block chain technologies [ 20 ].

Most of these technologies have a set basis in computing, nanotechnology, biotechnology, material science renovations, and satellite technologies. Nanotechnology offers useful alterations in the physiochemical, mechanical, magnetic, electrical, and optical properties of computing materials which enable innovative and newer products [ 21 ]. Thus, nanotechnology is providing a pathway for another broad-spectrum revolution in the field of automotive, aerospace, renewable energy, information technology, bioinformatics, and environmental management, all of which have root origins from nanotechnological improvements in computers. Sensors involved in software and data algorithms employ nanomaterials to induce greater sensitivity and processabilities with minimal margin-to-machine errors [ 22 ]. Nanomaterials provide better characteristics and robustness to sensor technologies which mean they are chemically inert, corrosion-resistant, and have greater tolerance profiles toward temperature and alkalinity [ 22 ].

Moreover, the use of semiconductor nanomaterials in the field of quantum computing has increased overall processing speeds with better accuracy and transmissibility. These technologies offer the creation of different components and communication protocols at the nano level, which is often called the internet of nano things [ 23 ]. This area is still in a continuous development and improvement phase with the potential for telecommunication, industrial, and medical applications. This field has taken its origin from the internet of things, which is a hyperphysical world of sensors, software, and other related technologies which allow broad-scale communication via internet operating devices [ 17 ]. The applications of these technologies range from being on the simple home scale to being on the complex industrial scale. The internet of things is mainly capable of gathering and distributing large-scale data via internet-based equipment and modern gadgets. In short, the internet of nano things is applicable to software, hardware, and network connection which could be used for data manipulation, collection, and sharing across the globe [ 24 ].

Another application of nanotechnology in the computer and information industry comes in the form of artificial intelligence, machine learning, and big data platforms which have set the basis for the fourth industrial revolution. Vast amounts of raw data are collected through interconnected robotic devices, sensors, and machines which have properties of nanomaterials [ 18 ]. After wide-scale data gathering, the next step is the amalgamation of the internet of things and the internet of people to prepare a greater analysis, understanding, and utilization of the gathered information for human benefit [ 4 ]. Such data complications can be easily understood through the use of big data in the medical industry, in which epidemiological data provide benefits for disease management [ 2 ]. Yet another example is the applications in business, where sales and retail-related data help to elucidate the target markets, sales industry, and consumer behavioral inferences for greater market consumption patterns [ 19 ].

Similarly, an important dimension of nanotechnology and computer combination comes in the form of drone and robotics technology. These technologies have a rising number of applications in maintenance, inspections, transportation, deliverability, and data inspection [ 25 ]. Drones, robots, and the internet of things are being perfectly amalgamated with the industrial sector to achieve greater goals. Drones tend to be more mobile but rely more on human control as compared to robots, which are less mobile but have larger potential for self-operation [ 26 ]. However, now, more mobile drones with better autonomous profiles are being developed to help out in the domain of manufacturing industries. These devices intensify and increase the pace of automation and precision in industries along with providing the benefits of lower costs and fewer errors [ 24 ]. The integrated fields of robotics, the internet of things, and nanotechnology are often called the internet of robotics and nano things. This field of nanorobotics is increasing the flexibility and dexterity in manufacturing processes compared to traditional robotics [ 25 ].

Drones, on the contrary, help to manage tasks that are otherwise difficult or dangerous to be managed by humans, such as working from a far distance or in dangerous regions. Nanosensors help to equip drones with the qualities of improved detection and sensation more precisely than previous sensor technologies [ 21 , 27 ]. Moreover, the over-potential of working hours, battery, and maintenance have also been improved with the operationalization of nano-based sensors in drone technology. These drones are inclusively used for various purposes such as maintaining operations, employing safety profiling, security surveys, and mapping areas [ 18 ]. However, limitations such as high speed, legal and ethical limitations, safety concerns, and greater automobility are some of the drawbacks of aerial and robotic drone technologies [ 26 ].

Three-dimensional printing is yet another important application of the nanocomputer industry, in which an integrated modus operandi works to help in production management [ 28 ]. Nanotechnology-based 3D printing offers the benefits of an autonomous, integrated, intelligent exchange network of information which enables wide-scale production benefits. These technologies have enabled a lesser need for industrial infrastructure, minimized post-processing operations, reduced waste material generation, and reduced need for human presence for overall industrial management [ 28 , 29 ]. Moreover, the benefits of 3D printing and similar technologies have potentially increased flexibility in terms of customized items, minimal environmental impacts, and sustainable practices with lower resource and energy consumption. The use of nano-scale and processed resins, metallic raw material, and thermoplastics along with other raw materials allow for customized properties of 3D printing technology [ 29 ].

The application of nanotechnology in computers cannot be distinguished from other industrial applications, because everything in modern industries is controlled by a systemic network in association with a network of computers and similar technologies. Thus, the fields of electronics, manufacturing, processing, and packaging, among several others, are interlinked with nanocomputer science [ 11 , 15 ]. Silicon tubes have had immense applications that revolutionized the industrial revolution in the 20th century; now, the industrial revolution is in yet another revolutionary phase based on nanostructures [ 16 ]. Silicon tubes have been slowly replaced with nanotubes, which are allowing a great deal of improvement and efficiency in computing technology. Similarly, lab-on-a-chip technology and memory chips are being formulated at nano scales to lessen the storage space but increase the storage volume within a small, flexible, and easily workable chip in computers for their subsequent applications in multiple other industries.

Hundreds of nanotechnology computer-related products have been marketed in the last 20 years of the nanotechnological revolution [ 30 ]. Modern industries such as textiles, automotive, civil engineering, construction, solar technologies, environmental applications, medicine, transportation agriculture, and food processing, among others are largely reaping the benefits of nano-scale computer chips and other devices. In simple terms, everything out there in nanoindustrial applications has something to do with computer-based applications in the nanoindustry [ 31 , 32 , 33 ]. Thus, all the applications discussed in this review more or less originate from nanocomputers. These applications are enabling considerable improvement and positive reports within the industrial sector. Having said that, it is hoped that computer scientists will remain engaged and will keep on collaborating with scientists in other fields to further explore the opportunities associated with nanocomputer sciences.

2.3. Nanotechnology and Bioprocessing Industries

Scientific and engineering rigor is being carried out to the link fields of nanotechnology with contributions to the bioprocessing industry. Researchers are interested in how the basics of nanomaterials could be used for the high-quality manufacturing of food and other biomaterials [ 15 , 34 ]. Pathogenic identification, food monitoring, biosensor devices, and smart packaging materials, especially those that are reusable and biodegradable, and the nanoencapsulation of active food compounds are only a few nanotechnological applications which have been the prime focus of the research community in recent years. Eventually, societal acceptability and dealing with social, cultural, and ethical concerns will allow the successful delivery of nano-based bio-processed products into the common markets for public usage [ 20 , 35 ].

With the increasing population worldwide, food requirements are increasing in addition to the concerns regarding the production of safe, healthy, and recurring food options. Sensors and diagnostic devices will help improve the sensitivity in food quality monitoring [ 36 ]. Moreover, the fake industrial application of food products could be easily scanned out of a system with the application of nanotechnology which could control brand protection throughout bio-processing [ 6 ]. The power usage in food production might also be controlled after a total nanotechnological application in the food industry. The decrease in power consumption would ultimately be positive for the environment. This could directly bring in the interplay of environment, food, and nanotechnology and would help to reduce environmental concerns in future [ 37 ].

One of the important implications of nanotechnology in bioprocessing industries can be accustomed to fermentation processes; these technologies are under usage for greater industrial demand and improved biomolecule production at a very low cost, unlike traditional fermentation processes [ 35 ]. The successful implementation and integration of fermentation and nanotechnology have allowed the development of biocompatible, safe, and nontoxic substances and nanostructures with wide-scale application in the field of food, bioprocessing, and winemaking industries [ 38 ]. Another important application is in the food monitoring and food supply chain management, present in various subsectors such as production, storage, distribution, and toxicity management. Nanodevices and nanomaterials are incorporated into chemical and biological sensor technologies to improve overall analytical performance with regard to parameters such as response time, sensitivity, selectivity, accuracy, and reliability [ 39 ]. The conventional methods of food monitoring are slowly being replaced with modern nano-based materials such as nanowires, nanocomposites, nanotubes, nanorods, nanosheets, and other materials that function to immobilize and label components [ 40 ]. These methods are either electrochemically or optically managed. For food monitoring, several assays are proposed and implemented with their roots in nano-based technologies; they may include molecular and diagnostic assays, immunological assays, and electrochemical and optical assays such as surface-enhanced Raman scattering and colorimetry technologies [ 34 ]. Materials ranging from heavy materials to microorganisms, pesticides, allergens, and antibiotics are easily monitored during commercial processing and bioprocessing in industries.

Additionally, nanotechnology has presented marvelous transformations in bio-composting materials. With the rising demand for biodegradable composites worldwide to reduce the environmental impact and increase the efficiency of industrial output, there is an increasing need for sustainable technologies [ 41 ]. Nanocomposites are thus being formulated with valuable mechanical properties better than conventional polymers, thus establishing their applicability in industries. The improved properties include optical, mechanical, catalytic, electrochemical, and electrical ones [ 42 ]. These biodegradable polymers are not only used in bioprocessing industries to create food products with relevant benefits but are also being deployed in the biomedical field, therapeutic industries, biotechnology base tissue engineering field, packing, sensor industries, drug delivery technology, water remediation, food industries, and cosmetics industries as well [ 2 , 24 , 34 , 43 ]. These nanocomposites have outstanding characteristics of biocompatibility, lower toxicities, antimicrobial activity, thermal resistance, and overall improved biodegradation properties which make them worthy of applications in products [ 44 ]. However, it is still imperative to conduct wide-scale toxicity and safety profiling for these and other nanomaterials to ensure the safety requirements, customer satisfaction, and public benefit are met [ 44 ].

Moreover, the advancement of nanotechnology has also been conferred to the development of functional food items. The exposure and integration of nanotechnology and the food industry have resulted in larger quantities of sustainable, safer, and healthier food products for human consumption, which is a growing need for the rising population worldwide [ 45 ]. The overall positive impact of nanotechnology in food processing, manufacturing, packing, pathogenic detection, monitoring, and production profiles necessitates the wide-scale application of this technology in the food industry worldwide [ 4 , 41 ]. Recent research has shown how the delivery of bioactive compounds and essential ingredients is and can be improved by the application of nanomaterials (nanoencapsulation) in food products [ 46 ]. These technologies improve the protection performance and sensitivity of bioactive ingredients while preventing unnecessary interaction with other constituents of foods, thus establishing clear-cut improved bioactivity and solubility profiles of nanofoods, thereby improving human health benefits. However, it should be kept in mind that the safety regards of these food should be carefully regulated with safety profiling, as they directly interact with human bodies [ 47 ].

2.4. Nanotechnology and Agri-Industries

Agriculture is the backbone of the economies of various nations around the globe. It is a major contributing factor to the world economy in general and plays a critical role in population maintenance by providing nutritional needs to them. As global weather patterns are changing owing to the dramatic changes caused by global warming, it is accepted that agriculture will be greatly affected [ 48 ]. Under this scenario, it is always better to take proactive measures to make agricultural practices more secure and sustainable than before. Modern technology is thus being employed worldwide. Nanotechnology has also come to play an effective role in this interplay of sustainable technologies. It plays an important role during the production, processing, storing, packaging, and transport of agricultural industrial products [ 49 ].

Nanotechnology has introduced certain precision farming techniques to enhance plant nutrients’ absorbance, alongside better pathogenic detection against agricultural diseases. Fertilizers are being improved by the application of nanoclays and zeolites which play effective roles in soil nutrient broths and in the restoration soil fertility [ 49 ]. Modern concepts of smart seeds and seed banks are also programmed to germinate under favorable conditions for their survival; nanopolymeric mixtures are used for coating in these scenarios [ 50 ]. Herbicides, pesticides, fungicides, and insecticides are also being revolutionized through nanotechnology applications. It has also been considered to upgrade linked fields of poultry and animal husbandry via the application of nanotechnology in treatment and disinfection practices.

2.5. Nanotechnology and Food Industry

The applications of nanotechnology in the food industry are immense and include food manufacturing, packaging, safety measures, drug delivery to specific sites [ 51 ], smart diets, and other modern preservatives, as summarized in Figure 1 . Nanomaterials such as polymer/clay nanocomposites are used in packing materials due to their high barrier properties against environmental impacts [ 52 ]. Similarly, nanoparticle mixtures are used as antimicrobial agents to protect stored food products against rapid microbial decay, especially in canned products. Similarly, several nanosensor and nano-assembly-based assays are used for microbial detection processes in food storage and manufacturing industries [ 53 ].

Nanotechnology applications in food and interconnected industries.

Nanoassemblies hold the potential to detect small gasses and organic and inorganic residues alongside microscopic pathogenic entities [ 54 ]. It should, however, be kept in mind that most of these nanoparticles are not directly added to food species because of the risk of toxicity that may be attached to such metallic nanoparticles. Work is being carried out to predict the toxicity attached, so that in the future, these products’ market acceptability could be increased [ 55 ]. With this, it is pertinent to say that nanotechnology is rapidly taking steps into the food industry for packing, sensing, storage, and antimicrobial applications [ 56 ].

Nanotechnology is also revolutionizing the dairy industry worldwide [ 57 ]. An outline of potential applications of nanotechnology in the dairy industry may include: improved processing methods, improved food contact and mixing, better yields, the increased shelf life and safety of dairy-based products, improved packaging, and antimicrobial resistance [ 58 ]. Additionally, nanocarriers are increasingly applied to transfer biologically active substances, drugs, enhanced flavors, colors, odors, and other food characteristics to dairy products [ 59 ].

These compounds exhibit higher delivery, solubility, and absorption properties to their targeted system. However, the problem of public acceptability due to the fear of unknown or potential side effects associated with nano-based dairy and food products needs to be addressed for the wider-scale commercialization of these products [ 60 ].

2.5.1. Nanotechnology, Poultry and Meat Industry

The poultry industry is a big chunk of the food industry and contributes millions of dollars every year to food industries around the world. Various commercial food chains are running throughout the world, the bases of which start from healthy poultry industries. The incidence of widespread foodborne diseases that originate from poultry, milk, and meat farms is a great concern for the food industry. Nanobiotechnology is certainly playing a productive role in tackling food pathogens such as those which procreate from Salmonella and Campylobacter infections by allowing increased poultry consumption while maintaining the affordability and safety of manufactured chicken products [ 61 ]. Several nano-based tools and materials such as nano-enabled disinfectants, surface biocides, protective clothing, air and water filters, packaging materials, biosensors, and detective devices are being used to confirm the authenticity and traceability of poultry products [ 62 ]. Moreover, nano-based materials are used to reduce foodborne pathogens and spoilage organisms before the food becomes part of the supply chain [ 63 ].

2.5.2. Nanotechnology—Fruit and Vegetable Industry

As already described, nanotechnology has made its way far ahead in the food industry. The agricultural, medicinal, and fruit and vegetable industries cannot remain unaffected under this scenario. Scientists are trying to increase the shelf life of fresh organic products to fulfill the nutritional needs of a growing population. From horticulture to food processing, packaging, and pathogenic detection technology, nanotechnology plays a vital role in the safety and production of vegetables and fruits [ 64 ].

Conventional technologies are now being replaced with nanotechnology due to their benefits of cost-effectiveness, satisfactory results, and overall shelf life improvement compared to past practices. Although some risks may be attached, nanotechnology has not yet reported high-grade toxicity to organic fresh green products. These technologies serve the purpose of providing safe and sufficient food sources to customers while reducing postharvest wastage, which is a major concern in developing nations [ 55 ]. Nanopackaging provides the benefits of lower humidity, oxygen passage, and optimal water vapor transmission rates. Hence, in the longer run, the shelf life of such products is increased to the desired level using nanotechnology [ 65 ].

2.5.3. Nanotechnology and Winemaking Industry

The winemaking industry is a big commercial application of the food industry worldwide. The usage of nanotechnology is also expanding in this industry. Nanotechnology serves the purpose of sensing technology through employment as nanoelectronics, nanoelectrochemical, and biological, amperometric, or fluorimetric sensors. These nanomaterials help to analyze the wine components, including polyphenols, organic acids, biogenic amines, or sulfur dioxide, and ensure they are at appropriate levels during the production of wine and complete processing [ 66 ].

Efforts are being made to further improve sensing nanotechnology to increase the accuracy, selectivity, sensitivity, and rapid response rate for wine sampling, production, and treatment procedures [ 53 ]. Specific nanoassemblies that are used in winemaking industries include carbon nanorods, nanodots, nanotubes, and metallic nanoparticles such as gold, silver, zinc oxide, iron oxide, and other types of nanocomposites. Recent research studies have introduced the concept of electronic tongues, nanoliquid chromatography, mesoporous silica, and applications of magnetic nanoparticles in winemaking products [ 67 ]. An elaborative account of these nanomaterials is out of the scope of the present study; however, on a broader scale, it is not wrong to say that nanotechnology is successfully reaping in the field of enology.

2.6. Nanotechnology and Packaging Industries

The packaging industry is continuously under improvement since the issue of environmentalism has been raised around the globe. Several different concerns are linked to the packaging industry; primarily, packaging should provide food safety to deliver the best quality to the consumer end. In addition, packaging needs to be environmentally friendly to reduce the food-waste-related pollution concern and to make the industrial processes more sustainable. Trials are being carried out to reduce the burden by replacing non-biodegradable plastic packaging materials with eco-friendly organic biopolymer-based materials which are processed at the nano scale to incur the beneficial properties of nanotechnology [ 68 ].

The nanomanufacturing of packaging biomaterials has proven effective in food packaging industries, as nanomanufacturing not only contributes to increasing food safety and production but also tackles environmental issues [ 69 ]. Some examples of these packaging nanomaterials may include anticaking agents, nanoadditives, delivery systems for nutraceuticals, and many more. The nanocompositions of packing materials are formed by mixing nanofillers and biopolymers to enhance packaging’s functionality [ 70 ]. Nanomaterials with antimicrobial properties are preferred in these cases, and they are mixed with a polymer to prevent the contamination of the packaged material. It is important to mention here that this technology is not only limited to food packaging; instead, packaging nanotechnology is now also being introduced in certain other industries such as textile, leather, and cosmetic industries in which it is providing large benefits to those industries [ 64 ].

2.7. Nanotechnology and Construction Industry and Civil Engineering

Efficient construction is the new normal application for sustainable development. The incorporation of nanomaterials in the construction industry is increasing to further the sustainability concern [ 71 ]. Nanomaterials are added to act as binding agents in cement. These nanoparticles enhance the chemical and physical properties of strength, durability, and workability for the long-lasting potential of the construction industry. Materials such as silicon dioxide which were previously also in use are now manufactured at the nano scale [ 71 ]. These nanostructures along with polymeric additives increase the density and stability of construction suspension [ 72 ]. The aspect of sustainable development is being applied to the manufacture of modern technologies coupled with beneficial applications of nanotechnology. This concept has produced novel isolative and smart window technologies which have driven roots in nanoengineering, such as vacuum insulation panels (VIPs) and phase change materials (PCMs), which provide thermal insulation effects and thus save energy and improve indoor air quality in homes [ 73 ].

A few of the unique properties of nanomaterials in construction include light structure, strengthened structural composition, low maintenance requirements, resistant coatings, improved pipe and bridge joining materials, improved cementitious materials, extensive fire resistance, sound absorption, and insulation properties, as well as the enhanced reflectivity of glass surfaces [ 74 ]. As elaborated under the heading of civil engineering applications, concrete’s properties are the most commonly discussed and widely changing in the construction industry because of concrete’s minute structure, which can be easily converted to the nano scale [ 75 ]. More specifically, the combination of nano-SiO 2 in cement could improve its performance in terms of compressiveness, large volumes with increased compressiveness, improved pore size distribution, and texture strength [ 76 ].

Moreover, some studies are also being carried out to improve the cracking properties of concrete by the application of microencapsulated healing polymers, which reduce the cracking properties of cement [ 77 ]. Moreover, some other construction materials, such as steel, are undergoing research to change their structural composites through nano-scale manufacturing. This nanoscaling improves steel’s properties such as improved corrosion resistance, increased weldability, the ease of handling for designing building materials, and construction work [ 78 ]. Additionally, coating materials have been improved by being manufactured at the nano scale. This has led to different improved coating properties such as functional improvement; anticorrosive action; high-temperature, fire, scratch, and abrasion resistance; antibacterial and antifouling self-healing capabilities; and self-assembly, among other useful applications [ 79 ].

Nanotechnology improves the compressive flexural properties of cement and reduces its porosity, making it absorb less water compared to traditional cementation preparations. This is because of the high surface-to-volume ratio of nanosized particles. Such an approach helps in reducing the amount of cement in concrete, making it more cost-effective, more strengthening, and eco-friendly, known as ‘green concrete’. Besides concrete, the revolutionary characteristics of nanotechnology are now also being adopted in other construction materials such as steel, glass, paper, wood, and multiple other engineering materials to upgrade the construction industry [ 80 ].

Similarly, carbon nanotubes, nanorods, and nanofibers are rapidly replacing steel constructions. These nanostructures along with nanoclay formations increase the mechanical properties and thus have paved the way for a new branch of civil engineering in terms of nanoengineering [ 80 ]. Apart from cement formulations, nanoparticles are included in repair mortars and concrete with healing properties that help in crack recovery in buildings. Furthermore, nanostructures, titanium dioxide, zinc, and other metallic oxides are being employed for the production of photocatalytic products with antipathogenic, self-cleaning, and water- and germ-repellent built-in technologies [ 33 ]. Similarly, quantum dot technologies are progressively employed for solar energy generation (a concept discussed later). These photovoltaic cells contribute to saving the maximum amount of solar energy [ 81 ].

2.8. Nanotechnology and Textiles Industry

The textile industry achieved glory in the 21st century with enormous outgrowth through social media platforms. Large brands have taken over the market worldwide, and millions are earned every year through textile industries. With the passing of time, nanotechnology is being slowly incorporated into the textile fiber industry owing to its unique and valuable properties. Previously, fabrics manufactured via conventional methods often curtailed the temporary effects of durability and quality [ 82 ]. However, the age of nanotechnology has allowed these fabric industries to employ nanotechnology to provide high durability, flexibility, and quality to clothes which is not lost upon laundering and wearing. The high surface-to-volume ratio of nanomaterials keeps high surface energy and thus provides better affinity to their fabrics, leading to long-term durability [ 82 ]. Moreover, a thin layering and coating of nanoparticles on the fabric make them breathable and make them smooth to the touch. This layering is carried out by processes such as printing, washing, padding, rinsing, drying, and curing to attach nanoparticles on the fabric surface. These processes are carried out to impart the properties of water repellence, soil resistance, flame resistance, hydrophobicity, wrinkle resistance, antibacterial and antistatic properties, and increased dyeability to the clothes [ 83 ].

The unique properties of nanomaterials in textile industries have attracted large-scale businesses for the financial benefits attached to their application. For this reason, competitors are increasing in nanotextile industry speedily, which may make the conventional textile industry sidelined in the near future [ 84 ]. Some benefits associated with nanotextile engineering and industry may include: improved cleaning surfaces, soil, wrinkle, stain, and color damage resistance, higher wettability and strike-through characteristics, malodor- and soil-removal abilities, abrasion resistance, a modified version of surface friction, and color enhancement through nanomaterials [ 85 ].

These characteristics have hugely improved the functionality and performance characteristics of textile and fiber materials [ 86 ]. Based upon the numerous advantages, nanotextile technology is increasingly being used in various inter-related fields, including in medical clothes, geotextiles, shock-resistant textiles, and fire-resistant and water-resistant textiles [ 87 ]. These textiles and fibers help overcome severe environmental conditions in special industries where high temperatures, pressure, and other conditions are adjusted for manufacturing purposes. These textiles are now increasingly called smart clothes due to renewed nanotechnological application to traditional methods [ 88 ].

The increasing demand for durable, appealing, and functionally outstanding textile products with a couple of factors of sustainability has allowed science to incorporate nanotechnology in the textile sector. These nano-based materials offer textile properties such as stain-repellent, wrinkle-free textures and fibers’ electrical conductivity alongside guaranteeing comfort and flexibility in clothing [ 82 ]. The characteristics of nanomaterials are also exhibited in the form of connected garments creation that undergo sensations to respond to external stimuli through electrical, colorant, or physiological signals. Thus, a kind of interconnection develops between the fields of photonic, electrical, textile and nanotechnologies [ 89 ]. Their interconnected applications confer the properties of high-scale performance, lasting durability, and connectivity in textile fibers. However, the concerns of nanotoxicity, the chances of the release of nanomaterials during washing, and the overall environmental impact of nanotextiles are important challenges that need to be ascertained and dealt with successfully in the coming years to ensure wide-scale acceptance and the global broad-spectrum application of nanotextiles [ 90 ].

The global market for the textile industry is constantly on the rise; with so many new brands, the competition is rising in regard to pricing, material, product outlook, and market exposure. Under this scenario, nanotechnology has contributed in terms of value addition to textiles by contributing the properties of water repellence, self-cleaning, and protection from radiation and UV light, along with safety against flames and microorganisms [ 82 ]. A whole new market of smart clothes is slowly taking our international markets along with improvements in textile machinery and economic standing. These advances have effectively established the sustainable character of the textile industry and have created grounds to meet the customer’s demand [ 91 ]. Some important examples of smart clothing originating from the nanotextile industry can be seen in products such as bulletproof jackets, fabric coatings, and advanced nanofibers. Fabric coatings and pressure pads can exhibit characteristics of invisibility and entail a silver, nickel, or gold nanoparticle-based material with inherent antimicrobial properties [ 92 ]. Such materials are effectively being utilized and introduced into the medical industry for bandages, dressings, etc. [ 92 ].

Similarly, woven optical fibers are already making progress in the textile and IT industry. With the incorporation of nanomaterials, optical fibers are being utilized for a range of purposes such as light transmission, sensing technologies, deformation, improved formational characteristic detection, and long-range data transmission. These optical fibers with phase-changing material properties can also be utilized for thermostability maintenance in the fiber industry. Thus, these fibers have combined applications in the computer, IT, and textile sectors [ 93 ]. In addition, the nano cellulosic material that is naturally obtained from plants confers properties of stiffness, strength, durability, and large surface area to volume ratios, which is acquired through the large number of surface hydroxyl groups embedded in nanocellulose particles [ 94 ]. Moreover, the characteristics of high resistance, lower weight, cost-effectiveness, and electrical conductivity are some additional benefits which are also linked to these nanocellulosic fibers [ 93 ]. The aforementioned technologies will allow industrialists to manufacture fabrics based on nanomaterials through a variety of chemical, physical, and biological processes. The scope of improvement in the textile properties, cost, and production methods is making the nanotextile industry a strong field of interest for future industrial investments.

2.9. Nanotechnology and Transport and Automobile Industry

The automotive industry is always improving its production. Nanotechnology is one such tool that could impart the automotive industry with a totally new approach to manufacturing. Automobile shaping could be improved greatly without any changes to the raw materials used. The replacement of conventional fabrication procedures with advanced nanomanufacturing is required to achieve the required outcome. Nanotechnology intends to partly renovate the automobile industry by enhancing the technical performance and reducing production costs excessively. However, there is a gap in fully harnessing the potential of nanomaterials in the automotive industry. Industrialists who were previously strict about automotive industrial principles are ready to employ novelties attached to nanotechnology to create successful applications to automobiles in the future [ 95 ]. Nanotechnology could provide assistance in manufacturing methods with an impartment of extended life properties. Cars that have been manufactured with nanotechnology applications have shown lower failure rates and enhanced self-repairing properties. Although the initial investment in the nanoautomated industry is high, the outcomes are enormous.

The concept of sustainable transport could also be applied to the manufacturing of such nano-based technology which is CO 2 free and imparts safe driving and quiet, clean, and wider-screen cars, which, in the future, may be called nanocars. The major interplay of nanotechnology and the automotive industry comes in the manufacturing of car parts, engines, paints, coating materials, suspensions, breaks, lubrication, and exhaust systems [ 32 ]. These properties are largely imparted via carbon nanotubes and carbon black, which renders new functionalities to automobiles. These products were previously in use, but nanoscaling and nanocoating allow for enhanced environmental, thermal, and mechanical stability to be imparted to the new generation of automobiles. In simple terms, automobiles manufactured with principal nanonovelties could result in cars with less wearing risk, better gliding potential, thinner coating lubrication requirements, and long service bodies with weight reductions [ 31 ]. These properties will ultimately reduce costs and will impart more space for improved automobile manufacturing in the future. Similarly, the development of electric cars and cars built on super capacitor technology is increasingly based on nanotechnology. The implications of nanotechnology in the form of rubber fillers, body frames made of light alloys, nanoelectronic components, nanocoatings of the interior and exterior of cars, self-repairing materials against external pressure, nanotextiles for interiors, and nanosensors are some of the nanotechnological-based implications of the automotive industry [ 96 ]. Owing to these properties, nanotechnology ventures are rapidly progressing in the automobile industry. It is expected that, soon, the automobile industry will commercialize nanotechnological perspectives on their branding strategies.

2.10. Nanotechnology, Healthcare, and Medical Industry

The genesis of nanomedicine simply cannot be ignored when we talk about the large fields of biological sciences, biotechnology, and medicine. Nanotechnology is already making its way beyond the imagination in the broader vision of nanobiotechnology. The quality of human life is continuously improved by the successful applications of nanotechnology in medicine, and resultantly, the entire new field of nanomedicine has come to the surface, which has allowed scientists to create upgraded versions of diagnostics, treatment, screening, sequencing, disease prevention, and proactive actions for healthcare [ 97 ]. These practices may also involve drug manufacturing, designing, conjugation, and efficient delivery options with advances in nano-based genomics, tissue engineering, and gene therapy. With this, it could be predicted that soon, nanomedicine will be the foremost research interest for the coming generation of biologists to study the useful impacts and risks that might be associated with them [ 98 ]. As illustrated in Figure 2 , we summarized the applications of nanotechnology in different subfields of the medical industry.

Nanotechnology applications in medical industry. Nanotechnology has a broad range of applications in various diagnostics and treatments using nanorobotics and drug delivery systems.

In various medical procedures, scientists are exploring the potential benefits of nanotechnology. In the field of medical tools, various robotic characters have been applied which have their origins in nano-scale computers, such as diagnostic surfaces, sensor technologies, and sample purification kits [ 99 ]. Similarly, some modifications are being accepted in diagnostics with the development of devices that are capable of working, responding, and modifying within the human body with the sole purpose of early diagnosis and treatment. Regenerative medicine has led to nanomanufacturing applications in addition to cell therapy and tissue engineering [ 100 ]. Similarly, some latest technologies in the form of ‘lab-on-a-chip’, as elaborated upon earlier, are being introduced with large implications in different fields such as nanomedicine, diagnostics, dentistry, and cosmetics industries [ 101 ]. Some updated nanotechnology applications in genomics and proteomics fields have developed molecular insights into antimicrobial diseases. Moreover, medicine, programming, nanoengineering, and biotechnology are being merged to create applications such as surgical nanorobotics, nanobioelectrics, and drug delivery methods [ 102 ]. All of these together help scientists and clinicians to better understand the pathophysiology of diseases and to bring about better treatment solutions in the future.

Specifically, the field of nanocomputers and linked devices help to control activation responses and their rates in mechanical procedures [ 2 ]. Through these mechanical devices, specific actions of medical and dental procedures are executed accurately. Moreover, programmed nanomachines and nanorobots allow medical practitioners to carry out medical procedures precisely at even sub-cellular levels [ 4 ]. In diagnostics fields, the use of such nanodevices is expanding rapidly, which allows predictions to be made about disease etiology and helps to regulate treatment options [ 103 ]. The use of in vitro diagnosis allows increased efficiency in disease apprehension. Meanwhile, in in vivo diagnoses, such devices have been made which carry out the screening of diseased states and respond to any kind of toxicities or carcinogenic or pathological irregularities that the body faces [ 104 ].

Similarly, the field of regenerative medicine is employing nanomaterials in various medical procedures such as cell therapy, tissue engineering, and gene sequencing for the greater outlook of treatment and reparation of cells, tissues, and organs. Nanoassemblies have been recorded in research for applications in powerful tissue regeneration technologies with properties of cell adhesion, migration, and cellular differentiation [ 102 ]. Additionally, nanotechnology is being applied in antimicrobial (antibacterial and antiviral) fields. The microscopic abilities of these pathogens are determined through nano-scale technologies [ 100 ]. Greek medicinal practices have long been using metals to cure pathogenic diseases, but the field of nanotechnology has presented a new method to improve such traditional medical practices; for example, nanosized silver nanomaterials are being used to cure burn wounds owing to the easy penetration of nanomaterials at the cellular level [ 102 , 105 ].

In the field of bioinformatics and computational biology, genomic and proteomic technologies are elucidating molecular insights into disease management [ 106 ]. The scope of targeted and personalized therapies related to pathogenic and pathophysiological diseases have greatly provided spaces for nanotechnological innovative technologies [ 107 , 108 ]. They also incorporate the benefits of cost-effectiveness and time saving [ 109 ]. Similarly, nanosensors and nanomicrobivores are utilized for military purposes such as the detection of airborne chemical agents which could cause serious toxic outcomes otherwise [ 102 ]. Some nanosensors also serve a purpose similar to phagocytes to clear toxic pathogens from the bloodstream without causing septic shock conditions, especially due to the inhalation of prohibited drugs and banned substances [ 100 , 105 , 110 ]. These technologies are also used for dose specifications and to neutralize overdosing incidences [ 110 ] Nano-scale molecules work as anticancer and antiviral nucleoside analogs with or without other adjuvants [ 21 ].

Another application of nanotechnology in the medical industry is in bone regeneration technology. Scientists are working on bone graft technology for bone reformation and muscular re-structuring [ 111 , 112 ]. Principle investigations of biomineralization, collagen mimic coatings, collagen fibers, and artificial muscles and joints are being conducted to revolutionize the field of osteology and bone tissue engineering [ 113 , 114 ]. Similarly, drug delivery technologies are excessively considering nanoscaling options to improve drug delivery stability and pharmacodynamic and pharmacokinetic profiles at a large scale [ 110 ]. The use of nanorobots is an important step that allows drugs to travel across the circulatory system and deliver drug entities to specifically targeted sites [ 99 , 115 ]. Scientists are even working on nanorobots-based wireless intracellular and intra-nucleolar nano-scale surgeries for multiple malignancies, which otherwise remain incurable [ 102 ]. These nanorobotics can work at such a minute level that they can even cut a single neuronic dendrite without causing harm to complex neuronal networks [ 116 ].

Another important application of nanotechnology in the medical field is oncology. Nanotechnology is providing a good opportunity for researchers to develop such nanoagents, fluorescent materials, molecular diagnostics kits, and specific targeted drugs that may help to diagnose and cure carcinogenesis [ 104 ]. Scientists are trying various protocols of adjoining already-available drugs with nanoparticulate conjugation to enhance drug specificity and targeting in organs [ 104 , 107 , 117 ]. Nanomedicine acts as the carrier of hundreds of specific anticancerous molecules that could be projected at tumor sites; moreover, the tumor imaging and immunotherapy approaches linked with nanomedicine are also a potential field of interest when it comes to cancer treatment management [ 112 , 117 ]. A focus is also being drawn toward lessening the impact of chemotherapeutic drugs by increasing their tumor-targeting efficiency and improving their pharmacokinetic and pharmacodynamic properties [ 112 ]. Similarly, heat-induced ablation treatment against cancer cells alongside gene therapy protocols is also being coupled with nanorobotics [ 99 , 118 ]. Anticancerous drugs may utilize the Enhanced Permeation and Retention Effect (EPR effect) by applications of nano assemblies such as liposomes, albumin nanospheres, micelles, and gold nanoparticles, which confirms effective treatment strategies against cancer [ 119 ]. Such advances in nanomedicine will bring about a more calculated, outlined, and technically programmed field of nanomedicine through association and cooperation between physicians, clinicians, researchers, and technologies.

2.10.1. Nanoindustry and Dentistry

Nanodentistry is yet another subfield of nanomedicine that involves broad-scale applications of nanotechnology ranging from diagnosis, prevention, cure, prognosis, and treatment options for dental care [ 120 ]. Some important applications in oral nanotechnology include dentition denaturalization, hypersensitivity cure, orthodontic realignment problems, and modernized enameling options for the maintenance of oral health [ 2 , 121 ]. Similarly, mechanical dentifrobots work to sensitize nerve impulse traffic at the core of a tooth in real-time calculation and hence could regulate tooth tissue penetration and maintenance for normal functioning [ 122 ]. The functioning is coupled with programmed nanocomputers to execute an action from external stimuli via connection with localized internal nerve stimuli. Similarly, there are other broad-range applications of nanotechnology in tooth repair, hypersensitivity treatment, tooth repositioning, and denaturalization technologies [ 4 , 118 , 120 , 121 ]. Some of the applications of nanotechnology in the field of dentistry are elaborated upon in Figure 3 .

Nanotechnology applications in field of dentistry. Nanotechnology can be largely used in dentistry to repair and treat dental issues.

2.10.2. Nanotechnology and Cosmetics Industry

The cosmetics industry, as part of the greater healthcare industry, is continuously evolving. Nanotechnology-based renovations are progressively incorporated into cosmetics industries as well. Products are designed with novel formulations, therapeutic benefits, and aesthetic output [ 123 ]. The nanocosmetics industry employs the usage of lipid nanocarrier systems, polymeric or metallic nanoparticles, nanocapsules, nanosponges, nanoemulsions, nanogels, liposomes, aquasomes, niosomes, dendrimers, and fullerenes, etc., among other such nanoparticles [ 101 ]. These nanomaterials bring about specific characteristics such as drug delivery, enhanced absorption, improved esthetic value, and enhanced shelf life. The benefits of nanotechnology are greatly captured in the improvement of skin, hair, nail, lip, and dental care products, and those associated with hygienic concerns. Changes to the skin barrier have been largely curtailed owing to the function of the nano scale of materials. The nanosize of active ingredients allows them to easily permeate skin barriers and generate the required dermal effect [ 124 ].

More profoundly, nanomaterials’ application is encouraged in the production of sun-protective cosmetics products such as sunblock lotions and creams. The main ingredient used is the rational combination of cinnamates (derived from carnauba wax) and titanium dioxide nanosuspensions which provide sun-protective effects in cosmetics products [ 125 ]. Similarly, nanoparticle suspensions are being applied in nanostructured lipid carriers (NLCs) for dermal and pharmaceutical applications [ 126 ]. They exhibit the properties of controlled drug-carrying and realizing properties, along with direct drug targeting, occlusion, and increased penetration and absorption to the skin surface. Moreover, these carrier nanoemulsions exhibit excellent tolerability to intense environmental and body conditions [ 127 ]. Moreover, these lipid nanocarriers have been researched and declared safe for potential cosmetic and pharmaceutical applications. However, more research is still required to assess the risk/benefit ratio of their excessive application [ 128 ].

2.11. Nanotechnology Industries and Environment

The environment, society, and technology are becoming excessively linked under a common slogan of sustainable development. Nanotechnology plays a key role in the 21st century to modify the technical and experimental outlook of various industries. Environmental applications cannot stand still against revolutionary applications of nanotechnology. Since the environment has much to do with the physical and chemical world around a living being, the nano scale of products greatly changes and affects environmental sustainability [ 129 ]. The subsequent introduction of nanomaterials in chemistry, physics, biotechnology, computer science, and space, food, and chemical industries, in general, directly impacts environmental sciences.

With regard to environmental applications, the remarkable research and applications of nanotechnology are increasing in the processing of raw materials, product manufacturing, contaminate treatment, soil and wastewater treatment, energy storage, and hazardous waste management [ 130 ]. In developed nations, it is now widely suggested that nanotechnology could play an effective role in tackling environmental issues. In fact, the application of nanotechnology could be implemented for water and cell cleaning technologies, drinking safety measures, and the detoxification of contaminants and pollutants from the environment such as heavy metals, organochlorine pesticides, and solvents, etc., which may involve reprocessing although nanofiltration. Moreover, the efficiency and durability of materials can be increased with mechanical stress and weathering phenomena. Similarly, the use of nanocage-based emulsions is being used for optical imaging techniques [ 131 ].

In short, the literature provides immense relevance to how nanotechnology is proving itself through groundbreaking innovative technologies in environmental sciences. The focus, for now, is kept on remediation technologies with prime attention on water treatment, since water scarcity is being faced worldwide and is becoming critical with time. There is a need for the scientific community to actively conduct research on comprehending the properties of nanomaterials for their high surface area, related chemical properties, high mobility, and unique mechanical and magnetic properties which could be used for to achieve a sustainable environment [ 132 ].

2.12. Nanotechnology—Oil and Gas Industry

The oil and gas industry makes up a big part of the fossil industry, which is slowly depleting with the rising consumption. Although nanotechnology has been successfully applied to the fields of construction, medicine, and computer science, its application in the oil and gas industry is still limited, especially in exploration and production technologies [ 133 ]. The major issue in this industry is to improve oil recovery and the further exploitation of alternative energy sources. This is because the cost of oil production and further purification is immense compared to crude oil prices. Nanotechnologists believe that they could overcome the technological barriers to developing such nanomaterials that would help in curtailing these problems.

Governments are putting millions of dollars into the exploration, drilling, production, refining, wastewater treatment, and transport of crude oil and gas. Nanotechnology can provide assistance in the precise measurement of reservoir conditions. Similarly, nanofluids have been proven to exhibit better performance in oil production industries. Nanocatalyses enhance the separation processing of oil, water, and gases, thus bringing an efficient impurity removal process to the oil and gas industry. Nanofabrication and nanomembrane technologies are excessively being utilized for the separation and purification of fossil materials [ 134 ]. Finally, functional and modified nanomaterials can produce smart, cost-effective, and durable equipment for the processing and manufacturing of oil and gas. In short, there is immense ground for the improvement of the fossil fuel industry if nanotechnology could be correctly directed in this industry [ 135 ].

2.13. Nanotechnology and Renewable Energy (Solar) Industry

Renewable energy sources are the solutions to many environmental problems in today’s world. This makes the renewable energy industry a major part of the environmental industry. Subsequently, nanotechnology needs to be considered in the energy affairs of the world. Nanotechnologies are increasingly applied in solar, hydrogen, biomass, geothermal, and tidal wave energy production. Although, scientists are convinced that much more needs to be discovered before enhancing the benefits of coupled nanotechnology and renewable energy [ 136 ].

Nanotechnology has procured its application way down the road of renewable energy sources. Solar collectors have been specifically given much importance since their usage is encouraged throughout the world, and with events of intense solar radiation, the production and dependence of solar energy will be helpful for fulfilling future energy needs. Research data are available regarding the theoretical, numerical, and experimental approaches adopted for upgrading solar collectors with the employment of nanotechnologies [ 137 ].

These applications include the nanoengineering of flat solar plates, direct absorption plates, parabolic troughs, and wavy plates and heat pipes. In most of these instruments and solar collection devices, the use of nanofluids is becoming common and plays a crucial role in increasing the working efficiency of these devices. A gap, however, exists concerning the usage of nanomaterials in the useful manufacturing design of solar panels and their associated possible efficiencies which could be brought to the solar panel industry. Moreover, work needs to be done regarding the cost-effectiveness and efficiency analyses of traditional and nanotechnology-based solar devices so that appropriate measures could be adopted for the future generation of nanosolar collectors [ 138 ].

2.14. Nanotechnology and Wood Industry

The wood industry is one of the main economic drivers in various countries where forest growth is immense and heavy industrial setups rely on manufacturing and selling wood-based products [ 139 ]. However, the rising environmental concerns against deforestation are a major cause for researchers to think about a method for the sustainable usage of wood products. Hence, nanotechnology has set its foot in the wood industry in various applications such as the production of biodegradable materials in the paper and pulp industry, timber and furniture industry, wood preservatives, wood composites, and applications in lignocellulosic-based materials [ 140 ]. Resultantly, new products are introduced into the market with enhanced performance (stronger yet lighter products), increased economic potential, and reduced environmental impact.

One method of nano-based application in the wood industry is the derivation of nanomaterials directly from the forest, which is now called nanocellulose material, known broadly for its sustainable characteristics [ 141 ]. This factor has pushed the wood industry to convert cellulosic material to nanocellulose with increased strength, low weight, and increased electromagnetic response along with a larger surface area [ 142 ]. These characteristics are then further used as reinforcing agents in different subcategories of wood-based industries, including substrate, stabilizer, electronics, batteries, sensor technologies, food, medicine, and cosmetics industries [ 143 ]. Moreover, functional characteristics such as the durability, UV absorption, fire resistance, and decreased water absorption of wood-based biodegradable products are also being improved with the application of nanomaterials such as nanozinc oxide or nanotitanium oxide [ 144 ]. Similarly, wood biodegradable properties are reduced through the application of nanoencapsulated preservatives to improve the impregnation of wood with the increasing penetration of applied chemicals and a reduced leaching effect.

Cellulosic nanomaterials exhibit nanofibrillar structures which can be made multifunctional for application in construction, furniture, food, pharmaceuticals, and other wood-based industries [ 145 ]. Research is emerging in which promising results are predicted in different industries in which nanofibers, nanofillers, nanoemulsions, nanocomposites, and nano-scaled chemical materials are used to increase the potential advantages of manufactured wood products [ 146 ]. The outstanding properties of nanocellulusice materials have largely curtailed the environmental concerns in the wood industry in the form of their potential renewable characteristics, self-assembling properties, and well-defined architecture. However, there are a few challenges related to such industries, such as cost/benefit analyses, a lack of compatibility and acceptability from the public owing to a lack of proper commercialization, and a persistent knowledge gap in some places [ 145 ]. Therefore, more effort is required to increase the applications and acceptability of nano-based wood products in the market worldwide.

2.15. Nanotechnology and Chemical Industries

Nanotechnology can be easily applied to various chemical compositions such as polymeric substances; this application can bring about structural and functional changes in those chemical materials and can address various industrial applications including medicine, physics, electronics, chemical, and material industries, among others [ 76 , 132 , 138 ]. One such industrial application is in electricity production, in which different nanomaterials driven from silver, golden, and organic sources could be utilized to make the overall production process cheaper and effective [ 147 ]. Another effective application is in the coatings and textile industry, which has already been discussed briefly. In these industries, enzymatic catalysis in combination with nanotechnology accelerates reaction times, saving money and bringing about high-quality final products. Similarly, the water cleaning industry can utilize the benefits of nanomaterials in the form of silver and magnetic nanoparticles to create strong forces of attraction that easily separate heavy material from untreated water [ 148 ]. Similarly, there is a wide range of chemicals that can be potentially upgraded, although the nano scale for application in biomedical industries is discussed under the heading of nanotechnology and medicine.

Another major application of nanotechnology in the chemical industry includes the surfactant industry, which is used for cleaning paper, inks, agrochemicals, drugs, pharmaceuticals, and some food products [ 149 ]. The traditional surfactant application was of great environmental and health concern, but with the newer and improved manufacturing and nanoscaling of surfactants, environmentally friendly applications have been made possible. These newer types may include biosurfactants obtained via the process of fermentation and bio-based surfactants produced through organic manufacturing. More research is required to establish the risks and side effects of these nanochemical agents [ 3 ].

3. Closing Remarks

Nanotechnology, within a short period, has taken over all disciplinary fields of science, whether it is physics, biology, or chemistry. Now, it is predicted to enormously impact manufacturing technology owing to the evidential and proven benefits of micro scaling. Every field of industry, such as computing, information technology, engineering, medicine, agriculture, and food, among others, is now originating an entire new field in association with nanotechnology. These industries are widely known as nanocomputer, nanoengineering, nanoinformatics, nanobiotechnology, nanomedicine, nanoagriculture, and nanofood industries. The most brilliant discoveries are being made in nanomedicine, while the most cost-effective and vibrant technologies are being introduced in materials and mechanical sciences.

The very purpose of nanotechnology, in layman’s terms, is to ease out the manufacturing process and improve the quality of end products and processes. In this regard, it is easy and predictable that it is not difficult for nanotechnology to slowly take out most of the manufacturing process for industrial improvement. With every coming year, more high-tech and more effective-looking nanotechnologies are being introduced. This is smoothing out the basis of a whole new era of nanomindustries. However, the constructive need is to expand the research basis of nanoapplications to entail the rigorous possible pros of this technology and simultaneously figure out a method to deal with the cons of the said technology.

The miniaturization of computer devices has continued for many years and is now being processed at the nanometer scale. However, a gap remains to explore further options for the nanoscaling of computers and complex electronic devices, including computer processors. Moreover, there is an immense need to enable the controlled production and usage of such nanotechnologies in the real world, because if not, they could threaten the world of technology. Scientists should keep on working on producing nanoelectronic devices with more power and energy efficiency. This is important in order to extract the maximum benefits from the hands of nanotechnology and computer sciences [ 5 ].

Under the influence of nanotechnology, food bioprocessing is showing improvement, as proven by several scientific types of research and industrial applications in food chain and agricultural fields. Moreover, the aspect of sustainability is being introduced to convert the environment, food chains, processing industries, and production methods to save some resources for future generations. The usage of precision farming technologies based upon nanoengineering, modern nano-scale fertilizers, and pesticides are of great importance in this regard. Moreover, a combined nanotechnological aspect is also being successfully applied to the food industry, affecting every dimension of packing, sensing, storage, manufacturing, and antimicrobial applications. It is pertinent to say that although the applications of nanotechnology in the food, agriculture, winemaking, poultry, and associated packaging industries are immense, the need is to accurately conduct the risk assessment and potential toxicity of nanomaterials to avoid any damage to the commercial food chains and animal husbandry practices [ 63 ].

The exposure of the nano-based building industry is immense for civil and mechanical engineers; now, we need to use these technologies to actually bring about changes in those countries in which the population is immense, construction material is depleting, and environmental sustainability problems are hovering upon the state. By carefully assessing the sustainability potential of these nanomaterials, their environmental, hazardous, and health risks could be controlled, and they could likely be removed from the construction and automobile industry all over the world with sincere scientific and technical rigor [ 150 ]. It is expected that soon, the construction and automobile industry will commercialize the nanotechnological perspectives alongside sustainability features in their branding strategies. These nano-scale materials could allow the lifecycle management of automotive and construction industries with the provision of sustainable, safe, comfortable, cost-effective, and more eco-friendly automobiles [ 32 ]. The need is to explore the unacknowledged and untapped potential of nanotechnology applications in these industry industries.

Similarly, nanotechnology-based applications in consumer products such as textile and esthetics industries are immense and impressive. Professional development involves the application of nanotechnology-based UV-protective coatings in clothes which are of utmost need with climatic changes [ 73 ]. The application of nanotechnology overcomes the limitations of conventional production methods and makes the process more suitable and green-technology-based. These properties have allowed the textile companies to effectively apply nanotechnology for the manufacture of better products [ 90 ]. With greater consumer acceptability and market demand, millions are spent in the cosmetic industry to enable the further usage of nanotechnology. Researchers are hopeful that nanotechnology would be used to further upgrade the cosmetics industry in the near future [ 123 ].

Furthermore, the breakthrough applications of nanomedicine are not hidden from the scientific community. If nanomedicine is accepted worldwide in the coming years, then the hope is that the domain of diagnosis and treatment will become more customized, personalized, and genetically targeted for individual patients. Treatment options will ultimately become excessive in number and more successful in accomplishment. However, these assumptions will stay a dream if the research remains limited to scientific understanding.

The real outcome will be the application of this research into the experimental domain and clinical practices to make them more productive and beneficial for the medical industry. For this cause, a combined effort of technical ability, professional skills, research, experimentation, and the cooperation of clinicians, physicians, researchers, and technology is imperative. However, despite all functional beneficial characteristics, work needs to be done and more exploration is required to learn more about nanotechnology and its potential in different industries, especially nanomedicine, and to take into account and curtail the risks and harms attached to the said domain of science.

Additionally, climatic conditions, as mentioned before, along with fossil fuel depletion, have pushed scientists to realize a low-energy-consuming and more productive technological renovation in the form of nanoengineered materials [ 48 ]. Now, they are employing nanomaterials to save energy and harvest the maximum remaining natural resources. There is immense ground for the improvement of the fossil fuel industry if nanotechnology could be correctly directed in this industry [ 135 ]. The beneficial applications within the solar industry, gas and oil industry, and conversion fields require comparative cost-effectiveness and efficiency analyses of traditional and nano-based technologies so that appropriate measures could be adopted for the future generation of nano-based products in said industries [ 138 ].

As every new technology is used in industries, linked social, ethical, environmental, and human safety issues arise to halt the pace of progress. These issues need to be addressed and analyzed along with improving nanotechnology so that this technology easily incorporates into different industries without creating social, moral, and ethical concerns. Wide-scale collaboration is needed among technologists, engineers, biologists, and industrials for a prospective future associated with the wide-scale application of nanotechnology in diversified fields.

4. Conclusions

Highly cost-effective and vibrant nanotechnologies are being introduced in materials and mechanical sciences. A comprehensive overview of such technologies has been covered in this study. This review will help researchers and professionals from different fields to delve deeper into the applications of nanotechnology in their particular areas of interest. Indeed, the applications of nanotechnology are immense, yet the risks attached to unlimited applications remain unclear and unpronounced. Thus, more work needs to be linked and carefully ascertained so that further solutions can be determined in the realm of nanotoxicology. Moreover, it is recommended that researchers, technicians, and industrialists should cooperate at the field and educational level to explore options and usefully exploit nanotechnology in field experiments. Additionally, more developments should be made and carefully assessed at the nano scale for a future world, so that we are aware of this massive technology. The magnificent applications of nanotechnology in the industrial world makes one think that soon, the offerings of nanotechnology will be incorporated into every possible industry. However, there is a need to take precautionary measures to be aware of and educate ourselves about the environmental and pollution concerns alongside health-related harms to living things that may arise due to the deviant use of nanotechnology. This is important because the aspect of sustainability is being increasingly considered throughout the world. So, by coupling the aspect of sustainability with nanotechnology, a prosperous future of nanotechnology can be guaranteed.

Funding Statement

K.M.’s work is supported by United Arab Emirates University-UPAR-Grant#G3458, SURE plus Grant#3908 and SDG research programme grant#4065.

Author Contributions

Conceptualization, Y.W. methodology, S.M. validation, S.M., K.M. and Y.W. formal analysis, S.M., K.M. and Y.W. investigation, S.M., K.M. and Y.W. resources, K.M. and Y.W. data curation, S.M., K.M. and Y.W. writing—original draft preparation, S.M. writing—review and editing, S.M., K.M. and Y.W. supervision, Y.W. project administration, K.M. and Y.W. funding acquisition, Y.W. and K.M. All authors have read and agreed to the published version of the manuscript.

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Green Synthesis of Titanium dioxide Nanoparticles by utilizing Marchantia polymorpha and their Application in Methylene Blue Dye Removal

• Published: 26 April 2024

Cite this article

• Anu Dadwal 1 ,
• Pooja Kumari 1 ,
• Tabassum Nike 1 ,
• Vinay Chauhan 2 ,
• Rajender Kumar 1 ,
• Deepika Kaushal 3 ,
• Vivek Sheel Jaswal 1 ,
• Aditi Koundal 1 &
• Manish Kumar   ORCID: orcid.org/0000-0002-1942-3463 1  

This research work involves the bio-mediated production of titanium dioxide (TiO 2 ) nanoparticles (NPs) using a bio-precipitation approach and the whole plant extract of Marchantia polymorpha , popularly known as common liverwort. In this study TTIP (Titaniumisopropoxide) was used as precursor of titanium and the function of reduction and capping of NPs was done by whole plant extract. The extract stabilizes the form and size of TiO 2 NPs along with their synthesis. The formation of TiO 2 NPs was confirmed by using various characterization techniques that are Ultraviolet–Visible (UV–Visible) spectroscopy, Fourier-Transform Infrared (FT-IR), Field Emission Scanning Electron Microscopy (FESEM) and X-ray diffraction (XRD). The UV–Visible analysis and energy band value confirms the synthesis of anatase type of TiO 2 NPs. The XRD analysis also validates the formation of crystalline anatase phase of TiO 2 NPs with crystallite size of 23 nm. FESEM analysis confirmed spherical shape of TiO 2 NPs with average diameter of 28.6 nm. These biomediated TiO 2 NPs were being utilized for the photocatalytic methylene blue dye degradation at different parameters like varied concentrations of dye, different amounts of TiO 2 NPs and different pH. The optimum results were found to be at 5 ppm initial dye concentration, 40 mg catalyst, and at pH-6. The results indicated that these bio-mediated TiO 2 NPs are suitable for photocatalytic degradation of methylene blue dye.

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Acknowledgements

Authors are thankful to Central University of Himachal Pradesh for the financial help and laboratory facility support. The authors sincerely acknowledge Malviya National Institute of Technology, Materials Research Centre (MNIT, MRC) Jaipur, Indian Institute of Technology, Central Instrumentation Facility SAPTARISHI Jammu, for providing instrumentation facilities.

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Anu Dadwal, Pooja Kumari, Tabassum Nike, Rajender Kumar, Vivek Sheel Jaswal, Aditi Koundal & Manish Kumar

School of Advanced Chemical Sciences, Shoolini University, Solan, Himachal Pradesh, 173229, India

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Anu Dadwal: Experimental, Investigation, Pooja Kumari: Writing—Original Draft, Conceptualization, Formal analysis Manish Kumar: Conceptualization, Writing—Review & Editing, Supervision, Project administration, Visualization, Aditi Koundal: Formal analysis, Tabassum Nike: Formal analysis, Rajender Kumar: Editing and Checking, Vivek Sheel Jaswal: Visualization, Vinay Chauhan: Formal analysis, Deepika Kaushal: Visualization.

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• Biosynthesis of Titanium dioxide nanoparticles by utilizing extract of whole plant of Marchantia polymorpha .

• Characterization results of UV-Visible, FT-IR, XRD and FESEM-EDS analysis assuring the formation of TiO 2 NPs.

• Photocatalytic efficiency of bio mediated TiO 2 NPs with various parameters for the degradation of methylene blue.

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Dadwal, A., Kumari, P., Nike, T. et al. Green Synthesis of Titanium dioxide Nanoparticles by utilizing Marchantia polymorpha and their Application in Methylene Blue Dye Removal. Catal Lett (2024). https://doi.org/10.1007/s10562-024-04690-2

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Nature 628 , 724-725 (2024)

doi: https://doi.org/10.1038/d41586-024-01015-6

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