Abstract
The recent years have seen a significant interest in the applications of nanotechnology in various facets of our lives. Due to their increasingly widespread use, human exposure to nanoparticles (NPs) is fast becoming unavoidable. Among the wide group of nanoparticles currently employed in industry, titanium dioxide nanoparticles, TiO2 NPs, are particularly popular. Due to its white colour, TiO2 is widely used as a whitening food additive (E 171). Yet, there have been few studies aimed at determining its direct impact on bacteria, while the available data suggest that TiO2 NPs may influence microbiota causing problems such as inflammatory bowel disease, obesity, or immunological disorders. Indeed, there are increasing concerns that its presence may lead to intestinal barrier impairment, including dysbiosis of intestinal microbiota. This article aims to present an overview of studies conducted to date with regard to the impact of TiO2 NPs on human microbiota as well as factors that can affect the same. Such information is necessary if we are to conclusively determine the potential toxicity of inorganic nanoparticles.
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Introduction
In recent years, the use of nanomaterials in food products has been observed to grow rapidly on a continuous basis, which inevitably increases the risk of adverse health effects resulting from their uncontrolled release [1, 2].
Numerous in vitro and in vivo studies conducted to date have confirmed the toxicity of TiO2 NPs against a human organism, including effects related to cellular cycle alterations, nuclear envelope contraction, and apoptosis [3, 4]. In vivo studies further demonstrated that after inhalation or oral exposure, TiO2 NPs accumulate in, e.g. the lungs, heart, alimentary tract, liver, spleen, kidneys, and myocardium, as well as upset the homeostasis of glucose and lipid metabolism in mice and rats [5,6,7]. Other possible effects include dyspepsia and nutrient absorption disorders after exposure to TiO2 NPs, which may be a consequence of micro- and macro-elements in the organism [8]. In the brain, TiO2 NPs can trigger protein oxidation, oxidative damage, reduction of antioxidative capacity, and increased production of ROS (reactive oxygen species) [9, 10].
TiO2 NPs (nanoparticles) are used as whitening or brightening additive in the food industry (coded—E171). They are commonly added to a number of products including sauces, cheeses, skimmed milk, ice-cream, and confectionary products—e.g. as coating for sweets and chewing gum [11,12,13,14]. They are also utilised in food processing and packaging, as well as added to pharmaceuticals, cosmetics, and toothpastes [11, 15, 16]. Owing to their antibacterial properties, TiO2 NPs may also serve as food preservatives [17, 18].
TiO2 content in confectionary products, particularly in sweets, chewing gum, chocolate, and other white-coated products, can be very high, reaching up to 2.5 mg Ti/g of food [14, 19]. The lack of sufficient research data prevents the determination of the admissible, daily consumption of TiO2 NPs [19]. Based on studies conducted on animals, a safety margin of 2.25 mg TiO2 NPs/kg bm/day was suggested [19]. Its daily consumption varies depending on age, body weight, and place of residence. It is nonetheless estimated that a child is likely to ingest up to 2–4 times more TiO2 NPs per 1 kg of body mass (Table 1) [14, 19, 20] compared to an adult. In Great Britain, children under 10 years old consume, on average, approximately 2–3 mg of TiO2/kg bm/day, while in adults this value is estimated at 1 mg TiO2/kg bm/day [14].
The impact of TiO2 NPs on the human organism has been debated for years. Both the levels of its exposure and toxicity to a human/animal organism have been subject to in-depth study and discussion. The wide-spread use of TiO2 NPs in the food industry has raised considerable safety concerns and controversy [11, 21]. Some studies conclude that TiO2 NPs may be toxic towards and have adverse effects on the cardiovascular system. Elevated expression of inflammatory cytokines such as TNF-α, INF-g, and IL-8 in the blood, after the ingestion of TiO2 NPs, was reported in studies by Gui et al. [22] and Trouiller et al. [23]. When studying the in vivo toxicity of TiO2 NPs in mice, Chen et al. [24] observed strong symptoms of toxicity, including loss of appetite, tremors, passive behaviour, or lethargy. Furthermore, in a study on rats, Wang et al. [25] observed hepatic oedema, heart damage, and non-allergic activation of mast cells in stomach tissue. Human organism is strongly dependant on its microbiota in terms of, e.g. the ability to digest dietary fibre and other nutrients, modulation of the host immunological response, food transit in the intestines, and defence against pathogens [26].
Interactions between gastrointestinal microbiota and NPs may affect the host’s health directly, through NPs-induced modification of the microbiota (increased toxicity), or indirectly, due to dysbiosis of gastrointestinal microorganisms [27]. One should also take into account the fact that various interactions between NPs and gastrointestinal bacteria may be dependent of a wide range of factors, e.g. the surface charge of nanoparticles and bacteria, the surface charge of the digested food, the chemical composition of respective substances and diet components [28], as well as the physicochemical conditions inside the alimentary canal (pH, enzymes, salts, etc.) [29].
As single-cell organisms, bacteria provide a very good test model for analysing the toxicity of nanoparticles, e.g. to determine their impact on the functional health of a cell organism [30]. Nanoparticles interact with bacteria producing reactive oxygen species (ROS), which in turn can damage DNA, RNA, and proteins [31] (Fig. 1). As follows from research, among the TiO2NPs, the anatase TiO2 forms are more toxic towards bacteria than rutile NPs as they cause greater oxidative stress [32, 33]. As reported by Kim et.al [34], mobile (•) OH is generated in anatase; hence, photocatalytic oxidation therein is easier compared to rutile which can only adsorb a substrate. TiO2 NPs mainly generate electrons and superoxide ions (O2 • -) in the conduction band, as well as positive holes and hydroxyl radicals (• OH) in the valence band. Next, the generated ROS can lead to oxidation of the TiO2 NPs adsorbed on the surfaces of bacteria, leading to their death [35].
Researching the interactions between bacteria and NPs may provide us with a lot of valuable information [30]. There have only been a handful of studies exploring the interactions between NPs and gastrointestinal microbiota, and the resulting impact on the host’s health, with most of the same focusing on the direct interactions with the cells of intestinal epithelium [36, 37], as well as photocatalytic applications in UV light (ultraviolet filter) [38].
This review aims to present detailed results of recent studies pertaining to the effects of TiO2 NPs exposure on human intestinal microbiota, as well as factors that may influence the same.
Material and Methods
A systematic literature survey up to August 2020 was conducted in the following databases: Scopus, PubMed, Web of Science, and Google Scholar (Fig. 2). The following inclusion criteria were employed: studies reporting significant information about the impact of TiO2 nanoparticles on the intestinal microbiota, available in the English language. Articles that did not meet the criteria were excluded. Classical and the newest papers were selected preferentially. The literature search entailed in the separate and joint use of a combination or keywords: “bacteria”, microbiota, TiO2 NPs, “impact of TiO2 on bacteria”, “impact of TiO2 on microbiota”, “interactions between TiO2 NPs and microbiota”. The literature included the following categories of papers: experimental studies and reviews. The obtained literature was manually reviewed, and the cited references were analyzed to identify the relevant studies. The search conducted at the highest sensitivity yielded 291 papers from external databases, which were subsequently collected. Next, after reviewing the titles and synopses, papers not related to the subject matter criteria were excluded, and the remaining texts were analyzed in depth to select the most relevant publications. Eventually, after identifying related papers and studies employing adequate research strategies, a total of 62 articles were analyzed.
Causes and Consequences of Intestinal Microbiota Alterations Due to TiO2 NPs Exposure
The physiological environment has a considerable significance to the interaction between inorganic nanoparticles and microorganisms [36]. Microorganism colonies can only prosper under specific microenvironmental conditions (e.g. pH, oxygen concentration, symbiotic proximity, nutrient availability) [39]. In the gastrointestinal tract, the environment is shaped by the presence of enzymes, bile, and regions with distinct pH, all of which influence the stability as well as aggregation (and size) of inorganic nanoparticles [29]. The mucous barrier, transit time, and unpredictable peristalsis will condition the transport of food, medicines, as well as the ways in which NPs may potentially interact with our alimentary tract and the microbiota present therein [39] (Fig. 3) [40]. Increased consumption of TiO2 NPs can have a negative impact on the human microbiome in the process of direct food consumption and/or during its passage through the intestine. Commensal bacteria and in-transit bacteria carried with the food can come into contact with TiO2 NPs, which can influence the resident microbiota, and consequently the host’s health [16, 41]. This may lead to inhibition of the growth and activity of gastrointestinal bacteria, in particular of the probiotic type [2]. Microbiota changes can lead to specific health problems including obesity, inflammatory bowel disease, diabetes, and rheumatoid arthritis [36, 42, 43].
Exposure to nanoparticles can take place while consuming food (it is used as pigment, filler, preservative), via the respiratory system or skin [27, 37]. In the gastrointestinal tract, nanoparticles are first acidized in the stomach, which increases their toxicity due to ion release [37]. In the small intestine, they come in contact with a variety of compounds: proteins and peptides—which can interact with the NPs forming agglomerates as well as changing their charge [44].
There have been reports on the adverse effects of E171 against intestinal epithelial bacteria in vitro [41, 45]. Agans et al. [27] did not exclude potential changes to human intestines following exposure to TiO2 NPs as the combination of agglomerates in cellular membranes can inhibit cells’ ability to divide or disturb the processes of absorbing nutrients. Taylor et al. [46], in a study involving 1-week in vitro exposure to TiO2 NPs (dosed at, respectively, 3 μg/L, 0.01 μg/L, and 0.01 g/L) observed, in the model colon, changes to multiple characteristics of bacteria phenotypes, including the production of short-chain fatty acids. Pignet et al. [47] analyzed the impact of TiO2 NPs (2 and 10 mg TiO2/kg bm/day and 50 mg TiO2/kg bm/day) on the large and small intestine in mice. After oral administration of TiO2 NPs, they reported minimum impact of NPs on the composition of gastrointestinal microbiota in mice, but at the same time observed that the same can modify the release of bacterial metabolites in vivo and influence commensal bacteria in vitro by promoting the formation of biofilm. Khan et al. [2] used TiO2 NPs from purified chocolate and studied its in vitro and in vivo influence on a commercial probiotic preparation typically used in the treatment of diarrhoea in children (it contained Bacillus coagulans, Enterococcus faecalis, and Enterococcus). The researchers demonstrated that TiO2 NPs obtained from chocolate inhibited the growth and activity of the probiotic preparation within the concentration range of 125–500 μg/mL in vitro. Based on the obtained results, they concluded that 20 g of the analyzed chocolate contained sufficient amounts of TiO2 NPs to upset the microbiological balance in the intestines of children between 2 and 8 years of age and with a stomach capacity of between 0.5 and 0.9 L; similar effects were observed in an in vivo study on white albino mice dosed at 50–100 μg/day/mouse. Pagnout et al. [48] demonstrated that the toxicity of TiO2 NPs is related to electrostatic interactions between bacteria (Escherichia coli (E. coli)) and nanoparticles, which lead to adsorption of the latter on the cell surface. Planchon et al. [49] corroborated the thesis on the heterogeneity of bacteria populations. In their studies, they demonstrated that after exposure to TiO2 NPs some bacteria were fully covered with the same, while most of the population remained free from nanoparticles, which resulted in differences in terms of proteome and metabolome. Similarly, Radziwill-Bienkowska et al. [50] observed that a part of the bacterial population remained free form TiO2 NPs, while another part of the same very strongly interacted with the nanoparticles. Furthermore, Waller et al. [28] demonstrated that exposure to TiO2 NPs caused changes to the composition of microorganisms (i.e. a shift from Proteobacteria to Firmicutes phyla) as well as lowered the colonic pH (< 5) relative to the control (> 5).
At the same time, there have been studies that revealed a limited influence of TiO2 NPs on human microbiota. For example, Dudefoi et al. [12] reported that TiO2 NPs had no significant in vitro impact on gastrointestinal microbiota. Using concentrations that simulated the one observed in an adult intestine after chewing a single piece of chewing gum (100–250 mg/L), they revealed no impact on gas production and only a negligible effect in terms of fatty acid profiles (C16: 00, C18: 00, 15: 1 w5c, 18: 1 w9c and 18: 1 w9c, p < 0.05) and phylogenetic composition. Agans et al. [27] demonstrated that TiO2 nanoparticles had limited direct influence on human gastrointestinal microbiota. After adding TiO2 NPs to a microorganic community, some slight reduction was observed but without changes to the overall diversity or balance thereof.
Factors Influencing the Interaction of TiO2 NPs with the Microbiota, and Their Consequences
In determining the toxicity of TiO2 NPs, interfacial electrostatic interaction as well as physicochemical parameters of the medium (pH, ionic strength, electrolyte composition, size, temperature, light exposure) can play a rather significant role [29, 48].
UV
TiO2 NPs are considered to be chemically inert without photoactivation, but they do show strong photocatalytic and antibacterial properties under UV light as they produce reactive oxygen species (ROS). Anatase is believed to be the most photocatalytically active of all titanium oxides due to its significant mobility of the electron-hole pairs and wider bandwidth range [34].
The mechanism of TiO2 NPs antibacterial activity under UV light has been fairly thoroughly researched [35, 51]. Planchon et al. [49] studied the proteome and metabolome of E. coli bacteria after exposure to TiO2 NPs under ultraviolet radiation and in normal light. They observed an ununiform bacterial response to the exposure from E. coli cells. A part of the population was able to adapt to the stress and survive for a time; the other part gradually died. The authors believe that some protein and metabolites may be used as biomarker of particle stress, e.g. chaperonin 1 and isocitrate dehydrogenase, as their content was respectively decreased and increased significantly in the presence of TiO2 NPs. Joost et al. [52] demonstrated in their study on living bacteria cells (E. coli) that exposure to TiO2 NPs resulted in enlargement of the cells, deformation of their membranes, and possible cytoplasm leakage after 10 min of exposure. The complete inactivation of the bacteria in thin TiO2 NPs layers took place after 20 min UV-A irradiation. The researchers also studied saturated and unsaturated fatty acids present in bacterial plasma membranes, which disintegrated within 10 min of exposure on photoactivated thin layers of TiO2 NPs. Priyadarshini et al. [53] demonstrated the inhibitive effects of TiO2 NPs in darkness, and enhanced effects under UV light (365 nm), on Gram-positive and Gram-negative bacteria (Staphylococcus aureus (S. aureus), Bacillus subtilis (B. subtilis), and E. coli). The significant bactericidal activity observed already for the minimum TiO2 NPs concentration (dosed at 0.5 mg/mL), and the enhancement thereof after photo-stimulation was explained by the loss of membrane integrity and increased oxidative stress on the surface of bacteria.
Some researchers have reported moderate toxicity of TiO2 NPs towards bacteria, even in the absence of UV radiation [54]. Dark incubation of Gram-negative E. coli and Gram-positive B. subtilis bacteria with TiO2 nanoparticles reduced the CFU (colony-forming units) index by, respectively, 25% and 30% [55]. Also in other studies [56], it was shown that dark incubation of E. coli cells with TiO2 NPs reduced the respective CFU by approximately four orders of magnitude in acidic pH. Zhukova et al. [57] demonstrated that 60-min exposure of E. coli to TiO2 NPs (concentrated at 0.02–0.2 mg/mL) resulted in a decrease in cell viability from 108 to 104 CFU/mL (colony-forming unit) in the absence of UV radiation. Qiu et al. [39] demonstrated that TiO2 nanoparticles (10, 50, and 100 nm in size) can inhibit the growth of commensal in vitro (Lactobacilli, Enterobacteria and Acetobacter) with no access to light. Radziwill-Bienkowska et al. [50] studied the interactions, under conditions with no UV radiation, between TiO2 NPs (food grade E171 and TiO2—P25) and gastrointestinal microbiota bacteria (e.g. E. coli) as well as those swallowed with food (e.g. Lactococcus lactis (L. lactis)). They demonstrated that bacterial growth was inhibited by TiO2 NPs in all the tested bacterial strains (E. coli, L. lactis, Lactobacillus rhamnosus, Lactobacillus sakei, and Streptococcus thermophilus), particularly by the food grade TiO2 NPs. They further observed that E171 may be retained in the intestine by commensal as well as in-transit bacteria carried in food. As a result, physiological changes may occur in more susceptible species.
pH
Changes in pH significantly impact the surface charge, size, and aggregation speed of NP. Studies indicate that aggregation and stability of food grade and industrial grade TiO2 NPs is susceptible to solution pH in terms of particle IEP (isoelectric points) [58, 59], where industrial grade particles show IEP at approximately pH 6.8, while food grade particles at approximately pH 3.5 [59]. Lin et al. [60] demonstrated in their study that the toxicity of TiO2 NPs tends to decrease with growing pH. The antibacterial activity of TiO2 NPs (25 nm, P25) against E. coli was stronger at pH 5.5 than at 7.0 or 9.5. Pagnout et al. [48] observed that the viability of E. coli cells was significantly lowered at pH 5.5 compared to pH 7.0 or pH 9.5. Waller et al. [28] studied, during a 5-day experiment, the impact of exposure to TiO2 NPs (food and industrial grade) on various bacteria groups from Proteobacteria to Firmicutes phyla. They demonstrated that TiO2 NPs had only a slight impact on microbiological stability. They also observed that in both cases, exposure to TiO2 NPs resulted in decreased values of pH in the colon (< 5) compared to the control (> 5), with the exposure to food grade TiO2 nanoparticles inducing the highest reduction (~ pH 4) [28].
Size
It is suspected that the size of the nano-fraction also influences disorders of gastrointestinal homeostasis as well as the development of intestinal microbiota dysbiosis [59]. Lin et al. [60] studied the toxicity of five types of TiO2 nanoparticles of different sizes (anatase TiO2 NPs with particles sizes of 10, 25, and 50 nm; rutile TiO2 NPs—50 nm; and mixed anatase and rutile TiO2 NPs—25 nm in length). The concentration of anatase TiO2 NPs was observed to increase, particularly for smaller particles, on the surface of Escherichia coli cells. It was also reported that compared to rutile NPs, anatase TiO2 NPs forms were more likely to bind with cell surfaces. Xiong et al. [61] demonstrated that smaller TiO2 NPs after UV–Vis activation of a larger surface area had a tendency to produce higher cytotoxicity. The same could be caused by generation of ROS and adsorption of bioparticles, as observed by the authors in whose study, both under biotic and abiotic conditions; ROS production was observed to increase in smaller particles. Ederm et al. [62] demonstrated higher microbiological toxicity for particles under 40 nm. In their study, the highest toxicity was reported for TiO2 NPs of 16.2 nm and 21.4 nm in size, which caused growth inhibition by 80% (E. coli) and 65% (B. subtilis) in the absence of light. Under light exposure, TiO2 nanoparticles of the same two sizes also proved to have the highest antibacterial potential.
Conclusion
The use of titanium dioxide nanoparticles continues to give rise to controversy around the world and is subject to extensive study regarding their impact on the alimentary tract and its functioning. Currently available reports provide contradictory evidence in terms of the impact of inorganic nanoparticles on our microbiota due to the application of varying experimental models and frameworks. Advanced in vivo models need to be developed in experimental conditions to allow a more systematic study necessary for a better understanding of the variations in toxicity observed between NPs and the human microbiota.
Future Perspective
The review discusses the impact of TiO2 nanoparticles on only a small group of selected bacterial strains. This was a deliberate decision that allowed me to focus on the strains directly related to my currently ongoing studies (research project - MINIATURE 3 grant (2019/03/X/NZ9/01032), “Influence of TiO2 nanoparticles on selected lactic and pathogenic bacterial strains, living in the human large intestine”). I aim to study the impact of TiO2 nanoparticles on a dozen or so selected lactic and pathogenic bacterial strains living in the human large intestine. In the study, I also employ an in vitro model of the alimentary tract to determine how the presence of TIO2 NPs influences the growth of the respective bacteria. This is to allow me to determine the risks related to the presence of those nanoparticles in food. The results detailing the impact of TiO2 NPs on the respective strains will be presented in the subsequent papers scheduled for publication next year. In the future, I intend to extend the scope of the in vitro studies using bacterial strains obtained from the intestine (Caco-2/HT29-MTX). It is my considered belief that this line of research may contribute to the minimization or even elimination of the side effects related to the use of TIO2 nanoparticles.
References
Kumar A, Pandey AK, Singh SS, Shanker R, Dhawan A (2011) Engineered ZnO and TiO2 nanoparticles induce oxidative stress and DNA damage leading to reduced viability of Escherichia coli. Free Radic Biol Med 51:1872–1881
Khan ST, Saleem S, Ahamed M, Ahmad J (2019) Survival of probiotic bacteria in the presence of food grade nanoparticles from chocolates: an in vitro and in vivo study. Appl Microbiol Biot 103:6689–6700. https://doi.org/10.1007/s00253-019-09918-5
Acar MS, Bulut ZB, Ates A, Nami B, Koçak N, Yildiz B (2015) Titanium dioxide nanoparticles induce cytotoxicity and reduce mitotic index in human amniotic fluid-derived cells. Hum Exp Toxicol 34:174–182
Coccini T, Grandi S, Lonati D, Locatelli C, De Simone U (2015) Comparative cellular toxicity of titanium dioxide nanoparticles on human astrocyte and neuronal cells after acute and prolonged exposure. NeuroToxicology 48:77–89
Bahadar H, Maqbool F, Niaz K, Abdollahi M (2016) Toxicity of nanoparticles and an overview of current experimental models. Iran Biomed J 20(1):1–11
Song B, Zhang Y, Liu J, Feng X, Zhou T, Shao L (2016) Is neurotoxicity of metallic nanoparticles the cascades of oxidative stress? Nanoscale Res Lett 11:291
Faddah LM, Abdel Baky NA, Al-Rasheed NM, Al-Rasheed NM (2013) Full length research paper: biochemical responses of nanosize titanium dioxide in the heart of rats following administration of idepenone and quercetin. AJPP 7:2639–2651
McClements DJ, DeLoid G, Pyrgiotakis G, Shatkin JA, Xiao H, Demokritou P (2016) The role of the food matrix and gastrointestinal tract in the assessment of biological properties of ingested engineered nanomaterials (iENMs): state of the science and knowledge gaps. NanoImpact 3:47–57
Allen R (2016) The cytotoxic and genotoxic potential of titanium dioxide (TiO2) nanoparticles on human SH-SY5Y neuronal cells in vitro. The Plymouth Student Scientist 9:5–28
Feng X, Chen A, Zhang Y, Wang J, Shao L, Wei L (2015) Central nervous system toxicity of metallic nanoparticles. Int J Nanomedicine 10:4321–4340
Baranowska-Wójcik E, Szwajgier D, Oleszczuk P, Winiarska-Mieczan A (2020) Effects of titanium dioxide nanoparticles exposure on human health—a review. Biol Trace Elem Res 193:118–129
Dudefoi W, Moniz K, Allen-Vercoe E, Ropers MH, Walker VK (2017) Impact of food grade and nano-TiO2 particles on a human intestinal community. Food Chem Toxicol 106:242–249
Bachler G, von Goetz N, Hungerbuhler K (2015) Using physiologically based pharmacokinetic (PBPK) modeling for dietary risk assessment of titanium dioxide (TiO2) nanoparticles. Nanotoxicology 9:373–380
Weir A, Westerhoff P, Fabricius L, Hristovski K, Von Goetz N (2012) Titanium dioxide nanoparticles in food and personal care products. Environ Sci Technol 46:2242–2250
Sadeghi R, Rodriquez RJ, Yao Y, Kokini JL (2017) Advances in nanotechnology as they pertain to food and agriculture: benefits and risks. Annu Rev Food Sci Technol 8:467–492
Zhang C, Derrien M, Levenez F, Brazeilles R, Ballal SA, Kim J, Degivry MC, Quéré G, Garault P, van Hylckama Vlieg JET, Garrett WS, Doré J, Veiga P (2016) Ecological robustness of the gut microbiota in response to ingestion of transient food-borne microbes. Isme J 10:2235–2245
Venkatasubbu GD, Baskar R, Anusuya T, Seshan CA, Chelliah R (2016) Toxicity mechanism of titanium dioxide and zinc oxide nanoparticles against food pathogens. Colloid Surface B 148:600–606
Rhim JW, Park HM, Ha CS (2013) Bio-nanocomposites for food packaging applications. Prog Polym Sci 38:1629–1652
EFSA ANS Panel (2016) EFSA panel on food additives and nutrient sources added to food. Scientific opinion on the re-evaluation of titanium dioxide (E171) as a food additive. EFSA J 14:4545
Chen Z, Han S, Zhou S, Feng H, Liu Y, Jia G (2020) Review of health safety aspects of titanium dioxide nanoparticles in food application. NanoImpact. 18:100224
Brand W, Peters RJB, Braakhuis HM, Maślankiewicz L, Oomen AG (2020) Possible effects of titanium dioxide particles on human liver, intestinal tissue, spleen and kidney after oral exposure. Nanotoxicology:1–23
Gui S, Zhang Z, Zheng L, Cui Y, Liu X, Li N, Sang X, Sun Q, Gao G, Cheng Z, Cheng J, Wang L, Tang M, Hong F (2011) Molecular mechanism of kidney injury of mice caused by exposure to titanium dioxide nanoparticles. J Hazard Mater 195:365–370
Trouiller B, Reliene R, Westbrook A, Solaimani P, Schiestl RH (2009) Titanium dioxide nanoparticles induce DNA damage and genetic instability in vivo in mice. Cancer Res 69:8784–878969
Chen J, Dong X, Zhao J, Tang G (2009) In vivo acute toxicity of titanium dioxide nanoparticles to mice after intraperitioneal injection. J Appl Toxicol 29:330–337
Wang Y, Chen Z, Ba T, Pu J, Chen T, Song Y, Gu Y, Qian Q, Xu Y, Xiang K, Wang H, Jia G (2013) Susceptibility of young and adult rats to the oral toxicity of titanium dioxide nanoparticles. Small 9:1742–1752
Sekirov I, Russell SL, Antunes LC, Finlay BB (2010) Gut microbiota in health and disease. Physiol Rev 90:859–904
Agans RT, Gordon A, Hussain S, Paliy O (2019) Titanium dioxide nanoparticles elicit lower direct inhibitory effect on human gut microbiota than silver nanoparticles. Toxicol Sci 172:411–416. https://doi.org/10.1093/toxsci/kfz183
Waller T, Chen C, Walker SL (2017) Food and industrial grade titanium dioxide impacts gut microbiota. Environ Eng Sci 34:537–550
Jones K, Morton J, Smith I, Jurkschat K, Harding AH, Evans G (2015) Human in vivo and in vitro studies on gastrointestinal absorption of titanium dioxide nanoparticles. Toxicol Lett l233:95–101
Jiang W, Mashayekhi H, Xing B (2009) Bacterial toxicity comparison between nano- and micro-scaled oxide particles. Environ Pollut 157:1619–1625
Cabiscol E, Tamarit J, Ros J (2000) Oxidative stress in bacteria and protein damage by reactive oxygen species. Int Microbiol 3:3–8
Planchon M, Ferrari R, Guyot F, Gélabert A, Menguy N, Chanéac C, Thill A, Benedetti MF, Spalla O (2013) Interaction between Escherichia coli and TiO2 nanoparticles in natural and artificial waters. Colloid Surface B 102:158–164
Jin C, Tang Y, Yang FG, Li XL, Xu S, Fan XF et al (2011) Toxicity of TiO2 nanoparticles in anatase and rutile crystal phase. Biol Trace Elem Res 141:3–15
Kim W, Tachikawa T, Moon G, Majima T, Choi W (2014) Molecular-level understanding of the photocatalytic activity difference between anatase and rutile nanoparticles. Angew Chem Int Ed Engl 15:14036–14041
Sohm B, Immel F, Bauda P, Pagnout C (2014) Insight into the primary mode of action of TiO2 nanoparticles on Escherichia coli in the dark. Proteomics 15:98–113
Pietroiusti A, Magrini A, Campagnolo L (2016) New frontiers in nanotoxicology: gut microbiota/microbiome-mediated effects of engineered nanomaterials. Toxicol Appl Pharmacol 299:90–95
Pietroiusti A, Bergamaschi E, Campagna M, Campagnolo L, De Palma G, Iavicoli S et al (2017) The unrecognized occupational relevance of the interaction between engineered nanomaterials and the gastro-intestinal tract: a consensus paper from a multidisciplinary working group. Part Fibre Toxicol 14:47
Pigeot-Rémy S, Simonet F, Errazuriz-Cerda E, Lazzaroni JC, Atlan D, Guillard C (2011) Photocatalysis and disinfection of water: identification of potential bacterial targets. Appl Catal B Environ 104:390–398
Qiu K, Durham PG, Anselmo AC (2018) Inorganic nanoparticles and the microbiome. Nano Res 11:4936–4954. https://doi.org/10.1007/s12274-018-2137-2
Riasat R, Guangjun N, Riasat Z, Aslam I, Sakeena M (2016) Effects of nanoparticles on gastrointestinal disorders and therapy. J Clin Toxicol 6
Derrien M, van Hylckama Vlieg JET (2015) Fate, activity, and impact of ingested bacteria within the human gut microbiota. Trends Microbiol 23:354–366
Marchesi JR, Adams DH, Fava F, Hermes GD, Hirschfield GM, Hold G et al (2016) The gut microbiota and host health: a new clinical frontier. Gut 65:330–339
Liu LY, Sun L, Zhong ZT, Zhu J, Song HY (2016) Effects of titanium dioxide nanoparticles on intestinal commensal bacteria. Nucl Sci Tech 27:1–5
Gunawan C, Lim M, Marquis CP, Amal R (2014) Nanoparticle–protein corona complexes govern the biological fates and functions of nanoparticles. J Mater Chem B 2:2060–2083
Proquin H, Rodríguez-Ibarra C, Moonen CG, Urrutia Ortega IM, Briedé JJ, de Kok TM et al (2017) Titanium dioxide food additive (E171) induces ROS formation and genotoxicity: contribution of micro and nano-sized fractions. Mutagenesis 32:139–149
Taylor AA, Marcus IM, Guysi RL, Walker SL (2015) Metal oxide nanoparticles induce minimal phenotypic changes in a model colon gut microbiota. En Eng Sci 32:602–612
Pinget GV, Tan JK, Janac B, Kaakoush NO, Angelatos A, O’sullivan J et al (2019) Impact of the food additive titanium dioxide (E171) on gut microbiota-host interaction. Front Nutr 6:57
Pagnout C, Jomini S, Dadhwal M, Caillet C, Thomas F, Bauda P (2012) Role of electrostatic interactions in the toxicity of titanium dioxide nanoparticles toward Escherichia coli. Colloid Surface B 92:315–321
Planchon M, LeÂger T, Spalla O, Huber G, Ferrari R (2017) Metabolomic and proteomic investigations of impacts of titanium dioxide nanoparticles on Escherichia coli. PLoS One 12:e0178437
Radziwill-Bienkowska JM, Talbot P, Kamphuis JBJ, Véronique R, Cartier C, Fourquaux I et al (2018) Toxicity of food-grade TiO2 to commensal intestinal and transient food-borne bacteria: new insights using nano-SIMS and synchrotron UV fluorescence imaging. Front Microbiol 9
Khan ST, Musarrat J, Al-Khedhairy AA (2016) Countering drug resistance, infectious diseases, and sepsis using metal and metal oxides nanoparticles: current status. Colloid Surface B 146:70–83
Joost U, Juganson K, Visnapuu M, Mortimer M Kahru A Nõmmiste E, et al. (2015) Photocatalytic antibacterial activity of nano-TiO2 (anatase)-based thin films: effects on Escherichia coli cells and fatty acids. J Photoch Photobi B 142:178–185
Priyadarshini S, Mainal A, Sonsudin F, Yahya R, Alyousef AA, Mohammed A (2019) Biosynthesis of TiO2 nanoparticles and their superior antibacterial effect against human nosocomial bacterial pathogens. Res Chem Intermediat 46:1077–1089. https://doi.org/10.1007/s11164-019-03857-6
Mallevre F, Fernandes TF, Aspray TJ (2014) Silver, zinc oxide and titanium dioxide nanoparticle ecotoxicity to bioluminescent Pseudomonas putida in laboratory medium and artificial wastewater. Environ Pollut 195:218–225
Adams LK, Lyon DY, Alvarez PJJ (2006) Comparative eco-toxicity of nanoscale TiO2, SiO2, and ZnO water suspensions. Water Res 40:3527–3532
Zhukova LV, Kiwi J, Nikandrov VV (2010) Nanoparticles of TiO2 cause aggregation of Escherichia coli cells and suppress their division at pH 4.0–4.5 in the absence of UV irradiation. Dokl Chem 435:279–282
Zhukova LV, Kiwi J, Nikandrov V (2012) TiO2 nanoparticles suppress Escherichia coli cell division in the absence of UV irradiation in acidic conditions. Colloid Surface B 97:240–247
Chowdhury I, Hong Y, Honda RJ, Walker SL (2011) Mechanisms of TiO2 nanoparticle transport in porous media: role of solution chemistry, nanoparticle concentration, and flowrate. J Colloid Interface Sci 360:548–555
Yang Y, Doudrick K, Bi X, Hristovski K, Herckes P, Westerhoff P, Kaegi R (2014) Characterization of food-grade titanium dioxide: the presence of nanosized particles. Environ Sci Technol 48:6391–6400
Lin X, Li J, Ma S, Liu G, Yang K, Tong M, Lin D (2014) Toxicity of TiO2 nanoparticles to Escherichia coli: effects of particle size, crystal phase and water chemistry. PLoS One 9:e110247
Xiong S, George S, Ji Z, Lin S, Yu H, Damoiseaux R et al (2012) Size of TiO2 nanoparticles influences their phototoxicity: an in vitro investigation. Arch Toxicol 87:99–109
Erdem A, Metzler D, Cha DK, Huang CP (2015) The short-term toxic effects of TiO2 nanoparticles toward bacteria through viability, cellular respiration, and lipid peroxidation. Environ Sci Pollut R 22:17917–17924
Funding
This study was supported by National Science Centre (Poland) in the frame of MINIATURE 3 grant (2019/03/X/NZ9/01032), “Influence of TiO2 nanoparticles on selected bacterial strains lactic and pathogenic, living in the human large intestine”.
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Baranowska-Wójcik, E. Factors Conditioning the Potential Effects TiO2 NPs Exposure on Human Microbiota: a Mini-Review. Biol Trace Elem Res 199, 4458–4465 (2021). https://doi.org/10.1007/s12011-021-02578-5
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DOI: https://doi.org/10.1007/s12011-021-02578-5