ArticlePDF Available

Use of Food Additive Titanium Dioxide (E171) before the Introduction of Regulatory Restrictions Due to Concern for Genotoxicity

MDPI
Foods
Authors:
  • National Institute of Public Health, Slovenia, Ljubljana
  • Nutrition institute, Ljubljana, Slovenia
  • Nutrition institute, Ljubljana, Slovenia

Abstract and Figures

Food-grade titanium dioxide (TiO2; E171) is a coloring food additive. In May 2021, a scientific opinion was published by the European Food Safety Authority concluding that TiO2 can no longer be considered as a safe food additive. Our aim was to investigate the trends in the use of TiO2 in the food supply. A case study was conducted in Slovenia using two nationally representative cross-sectional datasets of branded foods. Analysis was performed on N = 12,644 foods (6012 and 6632 in 2017 and 2020, respectively) from 15 food subcategories where TiO2 was found as a food additive. A significant decrease was observed in the use of TiO2 (3.6% vs. 1.8%; p < 0.01). TiO2 was most often used in the chewing gum category (36.3%) in 2017, and chocolate and sweets category (45.9%) in 2020. Meanwhile, in 2017, the largest share of TiO2-containing foods was observed in the chewing gum category, namely, 70.3%, and these products presented over 85% of the market share. In 2020, only 24.6% of chewing gums contained TiO2, which accounted for only 3% of the market share. In conclusion, we showed an overall decrease in TiO2 use, even though it has not yet been officially removed from the list of authorized food additives.
Content may be subject to copyright.
Foods 2021, 10, 1910. https://doi.org/10.3390/foods10081910 www.mdpi.com/journal/foods
Communication
Use of Food Additive Titanium Dioxide (E171) before the
Introduction of Regulatory Restrictions Due to Concern for
Genotoxicity
Urška Blaznik 1, Sanja Krušič 2, Maša Hribar 2, Anita Kušar 2, Katja Žmitek 2,3 and Igor Pravst 2,3,4,*
1 National Institute of Public Health, Trubarjeva 2, SI-1000 Ljubljana, Slovenia; urska.blaznik@nijz.si
2 Nutrition Institute, Tržaška Cesta 40, SI-1000 Ljubljana, Slovenia; sanja.krusic@nutris.org (S.K.);
masa.hribar@nutris.org (M.H.); anita.kusar@nutris.org (A.K.); katja.zmitek@vist.si (K.Ž.)
3 VIST—Higher School of Applied Sciences, Gerbičeva Cesta 51A, SI-1000 Ljubljana, Slovenia
4 Biotechnical Faculty, University of Ljubljana, Jamnikarjeva 101, SI-1000 Ljubljana, Slovenia
* Correspondence: igor.pravst@nutris.org; Tel.: +38-659-068-871
Abstract: Food-grade titanium dioxide (TiO2; E171) is a coloring food additive. In May 2021, a sci-
entific opinion was published by the European Food Safety Authority concluding that TiO2 can no
longer be considered as a safe food additive. Our aim was to investigate the trends in the use of TiO2
in the food supply. A case study was conducted in Slovenia using two nationally representative
cross-sectional datasets of branded foods. Analysis was performed on N = 12,644 foods (6012 and
6632 in 2017 and 2020, respectively) from 15 food subcategories where TiO2 was found as a food
additive. A significant decrease was observed in the use of TiO2 (3.6% vs. 1.8%; p < 0.01). TiO2 was
most often used in the chewing gum category (36.3%) in 2017, and chocolate and sweets category
(45.9%) in 2020. Meanwhile, in 2017, the largest share of TiO2-containing foods was observed in the
chewing gum category, namely, 70.3%, and these products presented over 85% of the market share.
In 2020, only 24.6% of chewing gums contained TiO2, which accounted for only 3% of the market
share. In conclusion, we showed an overall decrease in TiO2 use, even though it has not yet been
officially removed from the list of authorized food additives.
Keywords: titanium dioxide; E171; food supply; nanoparticles; safety; Europe; Slovenia
1. Introduction
Titanium dioxide (TiO2) is a transition metal oxide with application as a pigment or
photocatalyst [1]. As a white pigment it has been added to a variety of food products,
including bakery products, sauces, cheeses, edible ices and sweets. In addition to food,
titanium dioxide is also used in medicinal products as an excipient, and in personal care
products as a pigment and thickener [2,3], and can also be used as an UV filter in mineral
sunscreen products [4,5].
TiO2 was first approved for use in food in 1966 by the US Food and Drug Admin-
istration (FDA), with the stipulation that its content must not exceed 1% of the food weight
[6]. On the basis of the Codex Alimentarius of the Food and Agriculture Organiza-
tion/World Health Organization (FAO/WHO) [1] safety evaluation, TiO2 has been author-
ized as a food additive by the European Union (EU) with code E171 since 1969 [7]. Due to
the presence of a fraction of nanoparticles, it falls under the scope of the EFSA Guidance
on nanotechnology as “a material that is not engineered as nanomaterial but contains a
fraction of particles, less than 50% in the number–size distribution, with one or more ex-
ternal dimensions in the size range 1–100 nm” [8]. E171 as a food additive consist of ap-
proximately 40% of TiO2 nanosized particles (<100 nm) and 60% of TiO2 microsized par-
ticles (>100 nm) [2,9,10]. As it was permitted for use in the EU before 20 January 2009, it
Citation: Blaznik, U.; Krušič, S.;
Hribar, M.; Kušar, A.; Žmitek, K.;
Pravst, I. Use of Food Additive
Titanium Dioxide (E171) before the
Introduction of Regulatory
Restrictions Due to Concern for
Genotoxicity. Foods 2021, 10, 1910.
https://doi.org/10.3390/
foods10081910
Academic Editors: Isabel María
Moreno Navarro and Juan D.
Bautista Palomas
Received: 14 June 2021
Accepted: 13 August 2021
Published: 17 August 2021
Publisher’s Note: MDPI stays neu-
tral with regard to jurisdictional
claims in published maps and institu-
tional affiliations.
Copyright: © 2021 by the authors. Li-
censee MDPI, Basel, Switzerland.
This article is an open access article
distributed under the terms and con-
ditions of the Creative Commons At-
tribution (CC BY) license (http://crea-
tivecommons.org/licenses/by/4.0/).
Foods 2021, 10, 1910 2 of 11
belongs to the group of food additives that are subject to a safety re-evaluation by the
European Food Safety Authority (EFSA), according to Commission Regulation (EU) No.
257/2010, and in line with the provision of Regulation (EC) No. 1333/2008 [11]. Therefore,
the safety of TiO2 as a food additive was re-evaluated by the EFSA Panel on Food Addi-
tives and Nutrient Sources added to Food (ANS) [12] in 2016, on the basis of which the
EFSA concluded that TiO2 did not raise concerns with respect to genotoxicity and carcino-
genicity. Genotoxicity refers to the ability of a chemical substance to damage the genetic
material of cells, which may lead to carcinogenic effects [13]. EFSA also recommended
that additional studies be conducted to fill the gaps in possible effects on the reproductive
system, which could lead to an established Acceptable Daily Intake (ADI) for TiO2. There-
fore, in January 2017, the European Commission (EC) issued an open call for additional
data for TiO2, including reproductive toxicity data. Several studies investigated the tox-
icity of dietary TiO2 [10,14–25], raising some concerns regarding its potential tumor-pro-
moting activity. In 2018, the outcome of four specific studies [10,14,20,23] was included in
a scientific evaluation to determine the need to re-open the conclusion of the EFSA’s opin-
ion from 2016. However, the decision was taken in 2018 that the re-opening of this issue
was not needed [26]. In April 2019, the French Agency for Food, Environmental and Oc-
cupational Health and Safety (ANSES) delivered a scientific opinion, based on 25 studies
published between 2017 and 2019 [27], on the exposure to nanoparticles of TiO2, and high-
lighted that the previous EFSA assessment did not consider all available data. In response
to this opinion [28], the EFSA noted that ANSES reiterated previously identified concerns
and data gaps, and did not present findings that changed the Authority’s previous con-
clusions on the safety of TiO2. Furthermore, the Office for Risk Assessment and Research
of the Netherlands Food and Consumer Product Safety Authority (NVWA) delivered an
opinion on possible health effects of TiO2 in 2019 [29], highlighting the possible immune
and reproductive toxicological effects of TiO2. While further activities were underway to
obtain new data, the French Government followed the precautionary principle, based on
the opinion of the ANSES in 2019 [27], and decided to ban TiO2 in food products starting
on 1 January 2020. Just a few days after this decision was announced, a joint letter to the
EC [30] was published to EC, with civil society organizations requesting to remove TiO2
from the EU list of permitted food additives. Following the request of the EC in March
2020, the EFSA started an additional safety evaluation of this additive. An in-depth safety
assessment report for the TiO2 was published on 6 May 2021 [31]. The EFSA panel con-
cluded that with consideration of the available evidence, a concern for genotoxicity could
not be excluded and, therefore, TiO2 could no longer be considered as a safe food additive.
As mentioned, several studies have addressed the question of toxicity of E171. Stud-
ies on rats and mice have shown that nanoparticles can pass through the intestinal barrier,
accumulate in the intestine and cause preneoplastic lesions [14,32], promote anxiety, in-
crease the number of adenomas in the colon, induce hypertrophy and hyperplasia in gob-
let cells [33] and disrupt gut microbiota composition and function [34–38]. Accumulation
and toxic effects have also been found in plants [39,40]. However, health aspects of E171
oral intake by consumers in a real exposure environment still need to be confirmed by
further research.
Food additives are an important part of processed foods. Consumers have expressed
concern for some time about their possible adverse health effects [41] and would like to
be better informed about their potential health implications [42,43]. EU Member States,
and the EC as risk managers, request the EFSA to provide independent scientific advice,
which informs European food policy makers. In the next step, the EFSA’s scientific advice
on TiO2 will be used to support further regulatory procedures and decisions. The most
realistic outcome is that the use of TiO2 as a food additive will not be approved in the EU
in the near future.
The objective of this study was to evaluate the prevalence and changes in the use of
TiO2 as a food additive in the food supply since 2017, when the EC issued an open call for
additional toxicity data for TiO2. The Slovenian food supply was selected for a case study,
Foods 2021, 10, 1910 3 of 11
using nationally representative cross-sectional data on the composition of prepacked
foods in 2017 and 2020 collected within the national “Nutrition and Public Health” re-
search program and the “Food Nutrition Security Cloud” project (FNS-Cloud; www.fns-
cloud.eu, accessed: 15 August 2021).
2. Materials and Methods
2.1. Data Collection and Categorization
The study was conducted on a sample of prepacked foods available in Slovenia, EU.
The food supply sample was collected in 2017 and 2020 in major retail shops representing
the majority of the food market, and was part of the Composition and Labelling Information
System (CLAS, Nutrition Institute, Ljubljana, Slovenia) [44]. In both years, data collection
was done in retail shops of Mercator, Spar, Tuš, Lidl, Hofer, while in 2020 we also included
retailer Eurospin. The dataset was prepared by the extraction of food labelling information
from photographs of all branded foods available in selected food stores at the time of collec-
tion. Data were collected with the aim of monitoring the nutritional composition of pro-
cessed foods in the food supply [45], with the adaptation that we also collected ingredient
lists. The detailed methodology of the data collection is described elsewhere [46,47].
Foods were classified into food categories according to Global Food Monitoring
Group (GFMG) recommendations [45], with minor modifications [46,47]. Without food
supplements, food additives sold to consumers in food stores and food that did not fit into
any of the GFMG food groups, our dataset contained 49,919 prepacked food items; 23,690
and 26,229 from 2017 and 2020 monitoring, respectively. For 10,034 products (42%) in the
2017 dataset, there was a matching product with same International/European Article Num-
ber (EAN) barcode in the 2020 dataset. We identified all foods in this dataset, where the
ingredient list text contained the terms “TiO2”, “E171” and/or “titanium (di)oxide”.
Food (sub)categories that contained foods with TiO2 as a food additive at least in one
sampled year and were further investigated in this study are as follows: biscuits; cakes,
muffins and pastry; canned fish with vegetables; chewing gum; chocolate and sweets; cor-
dials; desserts; flavored yogurt; ice cream and edible ices; jelly; processed fish products;
side dishes; soup; spreads and processed cheese; and sugar. Our total study sample, there-
fore, included between 12.664 and 6.012 foods for 2017, of which 215 contained TiO2
(3.6%), and 6.632 foods for 2020, of which 122 (1.8%) contained TiO2.
2.2. Data Processing and Statistical Analyses
Food composition data were processed using Microsoft SQL Server Management
Studio 13.0, Microsoft Analysis Services Client Tools 13.0, Microsoft Data Access Compo-
nents (MDAC) 10.0, Microsoft Excel 2019 (Microsoft, Redmond, Washington, DC, USA)
and the Composition and Labelling Information System (CLAS) (Nutrition Institute,
Ljubljana, Slovenia). Statistical analyses were performed using Microsoft Excel 2019 (Mi-
crosoft, Redmond, Washington, DC, USA).
For statistical evaluation, we calculated proportions of TiO2-containing foods in dif-
ferent food (sub)categories. Additionally, we calculated the within-category proportion of
foods containing TiO2, which was corrected with product market shares using the previ-
ously described sale-weighting approach [47]. In the investigated food categories, market
share data were available for 59.8% (N = 3597) and 54.2% of foods (N = 3597) for 2017 and
2020, respectively. Sale-weighted proportions of TiO2-containing foods were calculated
for each (sub)category separately, using the EAN barcode as a unique product identifier,
with consideration of product packaging quantity and number of sold products in a 12-
month period (based on nationwide sales data provided by food retailers). Food subcate-
gories with less than four TiO2-containing foods were excluded from this analysis.
Descriptive analysis was used for proportions of food that contained TiO2, and the
95% confidence interval (95% CI) was calculated employing the Wilson score interval [48].
A two-tailed z-test was used to identify differences in the use of TiO2 between 2017 and
Foods 2021, 10, 1910 4 of 11
2020. The level of significance was set at p < 0.05. The following subcategories were ex-
cluded from this part of the analysis due to their low sample size of foods containing TiO2:
processed fish products; canned fish with vegetable; sugar; ice cream and edible ices; des-
serts; flavored yogurt; cordials; soup; biscuits; side dishes and spreads and processed
cheese.
3. Results and Discussion
The study was conducted on a sample of 6012 foods and beverages in 2017, and 6632
foods and beverages in 2020. Within the 15 selected food subcategories, 13 categories con-
tained TiO2 in 2017 (215 products), and 10 categories in 2020 (122 products). In 2017, foods
containing the highest amount of TiO2 were distributed in the chewing gum category,
accounting for more than a third (36.3%) of the total amount of TiO2-containing foods
(Figure 1). The second third was represented by chocolates and sweets (32.6%), followed
by cakes, muffins and pastry (11.6%), jelly (8.4%) and processed fish products (2.3%). In
2020, almost half of TiO2 was distributed in the chocolate and sweets category (45.9%) and
one third in the chewing gum category (27.9%), followed by cakes, muffins and pastry
(9.0%), jelly (5.7%) and processed fish products (4.9%) (Figure 1). The remaining categories
(each with less than a 3% share) represented 9% and 7% of TiO2-containing foods in 2017
and 2020, respectively (Figure 1, “Other”).
Figure 1. Distribution of foods containing TiO2 per food (sub)category in 2017 versus 2020.
To provide insights into food reformulation practices, we also compared the compo-
sition of foods, which were found in both 2017 and 2020 dataset. Food matching using
EAN barcodes resulted in 10,034 foods available in both datasets. Altogether, 88 of these
products contained TiO2 in the 2017 sample, while in 2020 the use of TiO2 was retained in
49 products (55.7%). This indicates that food reformulation (removal of TiO2) was ob-
served in 44.3% (N = 39) products.
Furthermore, we calculated per-category proportions of TiO2-containing foods in the
food supply for both 2017 and 2020 (Table 1). For each year, we calculated the (non-
weighted) proportion as a percentage of TiO2-containing foods of all available foods in the
category. To gain an insight into the availability of such foods with a consideration of
market share, we further employed the sale-weighting approach using nationwide 12-
month sales data, provided by the largest food retailers in Slovenia. Such an approach
provided information on whether TiO2 was used in market-leading brands or mostly in
niche products. It should be noted that sales data were available for most, but not all foods
2017 2020
Foods 2021, 10, 1910 5 of 11
in our study sample (see Section 2.1 for details). Missing data mostly reflect availability in
discounter retailers.
Per-category, nonweighted proportions of TiO2-containing foods represented up to
70.3% in 2017 (Table 1). In 2017, the largest share of TiO2-containing foods was represented
by chewing gum, comprising more than two third of the sample (70.3%), followed by jelly
(9.7%) and processed fish products (7.0%) (Table 1). Chewing gum was also the highest
ranked category (24.6%) in 2020, followed by processed fish products (6.9%) and jelly
(4.4%).
In 2017, the sale-weighted proportion of TiO2-containing chewing gums was higher
than the nonweighted proportion (85.5% vs. 70.3%), showing that this food additive was
present in major brands. The situation changed considerably in 2020, when the sale-
weighted proportion was much lower (3.1% vs. 24.6%). This indicates that a decrease in
the use of TiO2 was even more pronounced in the best-selling products. We also compared
the composition of the chewing gums, which contained TiO2 in 2017, and were still mar-
keted in 2020. Out of 44 such products, 25 (56.8%) no longer contained TiO2 in 2020. This
indicates that TiO2 dropped not only because of the arrival of new (TiO2-free) products
and removal of older (TiO2-containing) products from the market, but also because of the
reformulation of the existing products. However, the differences between sale-weighted
and nonweighted proportions in other food categories were expressed to a much lower
extent. Beside chewing gums, food subcategories with the highest sale-weighted propor-
tions of foods with TiO2 were jelly (14.8%) and processed fish products (19.3%) in 2017.
Considerably high sale-weighted proportions were also observed in these two categories
in 2020 (20.2% and 19.0%, respectively).
The overall comparison of the 2017 and 2020 data showed a significant (p < 0.01) de-
crease in the use of TiO2 as a food additive from 2017 to 2020. Across the 15 observed food
subcategories, 3.6% foods contained TiO2 in 2017, and 1.8% in 2020. This change could be
attributed to the availability of new evidence on the potential health risks of TiO2, and by
concerns raised by national health authority agencies [27,29]. As health concerns were also
raised by EFSA [31], it is expected that responsible food producers will remove it from
their products, despite the fact that it has not yet been officially restricted from the EU
food supply. A statistically significant decrease in the use of TiO2 was also observed in
specific food categories where TiO2 was a relevant additive in 2017. Sale-weighted pro-
portions showed a similar trend, with the exception of the abovementioned processed fish
products and jelly.
Foods 2021, 10, 1910 6 of 11
Table 1. (Sub)category proportions of foods containing TiO2 (E171) as food additive in the food supply for 2017 and 2020 (Slovenia).
Food Category
2017 2020 z-Test Statistic for
Proportions
Total N
Added
TiO2
N
% (95% CI) Sale-Weighted
Proportion (%) Total N
Added
TiO2
N
% (95% CI) Sale-Weighted
Proportion (%)
Proportion
Change
(95% CI)
p-Value
Chewing gum 111 78 70.3 (61.8–78.8)
85.5 138 34 24.6 (17.4–31.8) 3.1 45.6 (34.5–56.8) <0.01
Jelly 185 18 9.7 (5.5–14.0) 14.8 159 7 4.4 (1.2–7.6) 20.2 5.3 (0.0–10.6) 0.03
Processed fish products 71 5 7.0 (1.1–13.0) 19.3 87 6 6.9 (1.6–12.2) 19.0 0.1 (−7.8–8.1) ns
Cakes, muffins and pastry 569 25 4.4 (2.7–6.1) 3.0 639 11 1.7 (0.7–2.7) 1.1 2.7 (0.7–4.6) <0.01
Chocolate and sweets 1917 70 3.7 (2.9–4.5) 2.8 2173 56 2.6 (1.9–3.2) 1.1 1.1 (0.0–2.1) 0.02
Canned fish with vegetable 60 1 1.7 (0.3–8.9) * 60 0 ns
Sugar 127 2 1.6 (0.4–5.6) * 108 0 ns
Ice cream and edible ices 431 6 1.4 (0.3–2.5) 1.6 586 3 0.5 (0.0–1.1) * 0.9 (−0.4–2.1) ns
Desserts 207 2 1.0 (0.4–2.3) * 298 0 ns
Flavored yogurt 419 3 0.7 (0.2–2.1) * 386 0 ns
Cordials 179 1 0.6 (0.1–3.1) * 190 0 ns
Soup 264 1 0.4 (0.1–2.1) * 257 1 0.4 (0.1–2.2) * 0.0 (−1.1–1.1) ns
Biscuits 1035 3 0.3 (0.1–0.9) * 1122 2 0.2 (0.1–0.6) * 0.1 (−0.2–0.5) ns
Side dishes 199 0 224 1 0.5 (0.1–2.5) * ns
Spreads and processed cheese 238 0 205 1 0.5 (0.1–2.7) * ns
Total 6012 215 3.6 (3.1–4.0) na 6632 122 1.8 (1.5–2.2) na 1.8 (1.1–2.3) <0.01
Notes: Data presented for food categories with at least one product with TiO2 in either the 2017 or 2020 dataset. 95% CI: 95% confidence interval; N—number of all products; ns—not
significant; na—not applicable; *—low sample size (sale-weighted proportions not calculated for subsamples with N < 4).
Foods 2021, 10, 1910 7 of 11
To our knowledge, this is the first repeated cross-sectional study on the use of TiO2
in the food supply in which trends in the use of TiO2 in prepacked foods were investigated
with consideration of market share data. Such methodology makes the study results par-
ticularly relevant for the assessment of public health risks. While this makes comparisons
with other studies difficult, relevant comparisons can be performed without consideration
of sale-weighting. Mintel’s Global New Products Database (GNPD) [49], which contains
data of newly launched foods in different countries (but not Slovenia), was used in the
recent safety assessment of TiO2 by EFSA [31]. For a more relevant comparison, we com-
bined several of Mintel’s food subcategories [50]. The highest proportion of TiO2-contain-
ing foods was observed in chewing gums (39%), followed by pastilles, gums, jellies and
chews (10%), cakes, pastries and desserts (4%); and chocolate and sweets (3%) [31]. The
Mintel database cannot be considered as cross-sectional, as it only contains data on newly
launched products on the market (and not the overall situation in the food supply, where
some market-leading brands have a long history of availability). Nevertheless, it should
be mentioned that a decreasing trend in the use of TiO2 in newly launched foods was also
observed. Data are also available for the US, where TiO2 was most commonly used in
nonchocolate candy (32%), followed by cupcakes and snack cakes (14%), cookies (8%),
coated pretzels and trail mix (7%), baking decorations (6%), gum and mints (4%) and ice
cream (2%). However, it was assumed that many other foods contain TiO2, because in the
US market TiO2 can be considered as an exempt color that does not require explicit decla-
ration on the ingredient statement [51].
Exposure to TiO2 largely depends on an individual’s dietary habits. Since TiO2 is
mainly present in processed foods such as chewing gum, cakes, pastry and other sweets,
children and young people are more likely to be more exposed to higher TiO2 intake. For
the United Stated and United Kingdom population it has been calculated that children
potentially consumed two to four times as much TiO2 per kg body weight as an adult [2].
Similar studies revealing that children consume higher amount of TiO2 were observed
across Europe [52] in the German and [53] Dutch population [21,54], and among Chinese
young people [55].
Given scrutiny from regulatory bodies, the food industry has been working on TiO2
alternatives for some years. Reformulation initiatives were also stimulated by various
nongovernmental active groups. In the US, for example, the As You Sow group put pres-
sure on the Dunkin’ brand, which then withdrew the use of TiO2 from their sugar pow-
dered donuts [56]. However, replacing TiO2 across all applications is technologically very
challenging, as TiO2 is not only an excellent whitening pigment but also very cost effective
[51]. However, rice starches now offer clean label solutions that can help with reducing
the chipping and cracking of coatings [51]. Avalanche, starch and mineral based white
opacifier are the most common replacements for TiO2 in food applications [57].
The strength of the present study is in the use of two large nationally representative
cross-sectional food composition datasets in combination with market shares. While such
an approach was used in the past for the assessment of public health risks related to spe-
cific nutrients, such as salt [58] and sugar [47], we showed that it can also be employed for
food additives. The limitation of the study is that the used dataset did not contain all avail-
able foods, and that sales data were not available for the whole dataset. However, we
should mention that data collection included all major retailers with a nationwide net-
work of food stores, and that sales data were available from retailers who are responsible
for over 50% of the food market. Another limitation is that the data on the use of TiO2
were extracted from food labels, and not determined in a laboratory. However, regula-
tions require the labeling of functional additives, and the laboratory analysis of thousands
of foods is not a feasible option in food supply studies. We should also note that our study
did not investigate certain groups of foods in which a higher use of coloring agents could
be expected, such as food supplements and food additive products (i.e., foods sold directly
to consumers which are intended for coloring), which are also available to consumers in
food stores.
Foods 2021, 10, 1910 8 of 11
4. Conclusions
According to the results of our study, the availability of prepackaged food products
in Slovenia has undergone several improvements regarding the use of TiO2 in certain food
categories. This is particularly notable in the category of chewing gum, where a reformu-
lation trend was also observed. In recent years, we have witnessed an increased regulatory
scrutiny of TiO2 as a food additive. In other studies, this was reflected in a decline in new
launches of foods containing TiO2, while this cross-sectional study also confirmed such an
observation in a whole supply of processed foods in Slovenia. We observed that in the
past, the category with the most common use of TiO2 was chewing gum. In 2017, approx-
imately 70% of chewing gums contained TiO2, and these products presented over 85% of
the market share (by weight). However, the situation changed drastically; in 2020, approx-
imately 25% of chewing gums contained TiO2, accounting for only 3% of the market share.
The other two food categories with a high use of TiO2 were jelly and processed fish prod-
ucts, while in other food categories, less than 3% of products contained TiO2. Considering
the EFSA’s 2021 announcement of TiO2 no longer being safe to use, a further decrease in
the use of this additive is expected despite the fact that it has not yet been officially re-
moved from the list of authorized food additives in the EU. Specific food categories were
identified (i.e., chocolate and sweets), in which product reformulation is needed, and of-
ficial controls by authorities will be most relevant.
Author Contributions: Conceptualization, I.P.; data collection, M.H., S.K. and U.B.; methodology,
I.P. and U.B.; formal analysis, S.K.; writing—original draft preparation, I.P., S.K. and U.B.; manu-
script writing—review and editing, all authors; manuscript review, A.K. and K.Ž. All authors have
read and agreed to the published version of the manuscript.
Funding: Data collection for this study was supported by the national research program “Nutrition
and Public Health” (P3-0395, funded by the Slovenian Research Agency), and the Food Nutrition
Security Cloud project (FNS-Cloud), which received funding from the European Union’s Horizon
2020 Research and Innovation program (H2020-EU.3.2.2.3.—a sustainable and competitive agri-
food industry) under grant agreement No. 863059. Information and views in this report do not nec-
essarily reflect the official opinion or position of the European Union. Neither the European Union
institutions and bodies nor any person acting on their behalf may be held responsible for the use of
the information contained herein.
Institutional Review Board Statement: Not applicable.
Informed Consent Statement: Not applicable.
Data Availability Statement: The data presented in this study are available on request from the
corresponding author.
Acknowledgments: The authors would like to thank the retailers for granting access to their stores
to collect data for the study. We also acknowledge collaborating researchers at the Nutrition Insti-
tute and students from the Biotechnical Faculty (University of Ljubljana) and BIC (Ljubljana) for
their help in the data collection.
Conflicts of Interest: The authors declare no conflict of interest. The funders had no role in the
design of the study; in the collection, analyses or interpretation of data; in the writing of the manu-
script; or in the decision to publish the results. Igor Pravst has led and participated in various other
research projects in the fields of nutrition, public health and food technology, which were
(co)funded by the Slovenian Research Agency; the Ministry of Health of the Republic of Slovenia;
the Ministry of Agriculture, Forestry and Food of the Republic of Slovenia; and in the case of specific
applied research projects, also by food businesses.
Foods 2021, 10, 1910 9 of 11
References
1. Ropers, M.-H.; Terrisse, H.; Mercier-Bonin, M.; Humbert, B. Titanium Dioxide as Food Additive; IntechOpen: Rijeka, Croatia, 2017.
2. Weir, A.; Westerhoff, P.; Fabricius, L.; Hristovski, K.; Von Goetz, N. Titanium dioxide nanoparticles in food and personal care
products. Environ. Sci. Technol. 2012, 46, 2242–2250.
3. Peters, R.J.; van Bemmel, G.; Herrera-Rivera, Z.; Helsper, H.P.; Marvin, H.J.; Weigel, S.; Tromp, P.C.; Oomen, A.G.; Rietveld,
A.G.; Bouwmeester, H. Characterization of titanium dioxide nanoparticles in food products: Analytical methods to define
nanoparticles. J. Agric. Food Chem. 2014, 62, 6285–6293.
4. Kullavanijaya, P.; Lim, H.W. Photoprotection. J. Am. Acad. Dermatol. 2005, 52, 937–958, quiz 959–962,
doi:10.1016/j.jaad.2004.07.063.
5. Lautenschlager, S.; Wulf, H.C.; Pittelkow, M.R. Photoprotection. Lancet Lond. Engl. 2007, 370, 528–537, doi:10.1016/s0140-
673660638-2.
6. United States Food and Drug Administration. Summary of Color Additives for Use in the United States in Foods, Drugs,
Cosmetics, and Medical Devices, 2017. Available online: https://www.fda.gov/industry/color-additive-inventories/summary-
color-additives-use-united-states-foods-drugs-cosmetics-and-medical-devices (accessed on 17 August 2021).
7. European Commission. Commission (EC) No 1333/2008 of the European Parliament and of the Council of 16 December 2008 on
Food Additives. Off. J. Eur. Union 2011, L354/16, 1–18.
8. EFSA Scientific Committee; Hardy, A.; Benford, D.; Halldorsson, T.; Jeger, M.J.; Knutsen, H.K.; More, S.; Naegeli, H.; Noteborn,
H.; Ockleford, C.; et al. Guidance on risk assessment of the application of nanoscience and nanotechnologies in the food and
feed chain: Part 1, human and animal health. EFSA J. 2018, 16, e05327, doi:10.2903/j.efsa.2018.5327.
9. Dorier, M.; Béal, D.; Marie-Desvergne, C.; Dubosson, M.; Barreau, F.; Houdeau, E.; Herlin-Boime, N.; Carriere, M. Continuous
in vitro exposure of intestinal epithelial cells to E171 food additive causes oxidative stress, inducing oxidation of DNA bases
but no endoplasmic reticulum stress. Nanotoxicology 2017, 11, 751–761, doi:10.1080/17435390.2017.1349203.
10. Proquin, H.; Rodríguez-Ibarra, C.; Moonen, C.G.; Urrutia Ortega, I.M.; Briedé, J.J.; de Kok, T.M.; van Loveren, H.; Chirino, Y.I.
Titanium dioxide food additive (E171) induces ROS formation and genotoxicity: Contribution of micro and nano-sized fractions.
Mutagenesis 2017, 32, 139–149, doi:10.1093/mutage/gew051.
11. European Comission. Commission Regulation (EU) No 257/2010 of 25 March 2010 setting up a programme for the re-evaluation
of approved food additives in accordance with Regulation (EC) No 1333/2008 of the European Parliament and of the Council
on food additives. Off. J. Eur. Union 2010, L80/19, 1–9.
12. EFSA Panel on Food Additives Nutrient Sources added to Food. Re-evaluation of titanium dioxide (E 171) as a food additive.
EFSA J. 2016, 14, 83, doi:10.2903/j.efsa.2016.4545.
13. Maurici, D.; Aardema, M.; Corvi, R.; Kleber, M.; Krul, C.; Laurent, C.; Loprieno, N.; Pasanen, M.; Pfuhler, S.; Phillips, B.; et al.
Genotoxicty and mutagenicity. Altern. Lab. Anim. ATLA 2005, 33 (Suppl. 1), 117–130, doi:10.1177/026119290503301s13.
14. Bettini, S.; Boutet-Robinet, E.; Cartier, C.; Coméra, C.; Gaultier, E.; Dupuy, J.; Naud, N.; Taché, S.; Grysan, P.; Reguer, S.; et al.
Food-grade TiO(2) impairs intestinal and systemic immune homeostasis, initiates preneoplastic lesions and promotes aberrant
crypt development in the rat colon. Sci. Rep. 2017, 7, 40373, doi:10.1038/srep40373.
15. Chen, X.X.; Cheng, B.; Yang, Y.X.; Cao, A.; Liu, J.H.; Du, L.J.; Liu, Y.; Zhao, Y.; Wang, H. Characterization and preliminary
toxicity assay of nano-titanium dioxide additive in sugar-coated chewing gum. Small Weinh. Bergstr. Ger. 2013, 9, 1765–1774,
doi:10.1002/smll.201201506.
16. Athinarayanan, J.; Alshatwi, A.A.; Periasamy, V.S.; Al-Warthan, A.A. Identification of nanoscale ingredients in commercial food
products and their induction of mitochondrially mediated cytotoxic effects on human mesenchymal stem cells. J. Food Sci. 2015,
80, N459–N464, doi:10.1111/1750-3841.12760.
17. Tassinari, R.; Cubadda, F.; Moracci, G.; Aureli, F.; D’Amato, M.; Valeri, M.; De Berardis, B.; Raggi, A.; Mantovani, A.; Passeri,
D.; et al. Oral, short-term exposure to titanium dioxide nanoparticles in Sprague-Dawley rat: Focus on reproductive and
endocrine systems and spleen. Nanotoxicology 2014, 8, 654–662, doi:10.3109/17435390.2013.822114.
18. Jovanović, B. Critical review of public health regulations of titanium dioxide, a human food additive. Integr. Environ. Assess.
Manag. 2015, 11, 10–20, doi:10.1002/ieam.1571.
19. Periasamy, V.S.; Athinarayanan, J.; Al-Hadi, A.M.; Juhaimi, F.A.; Mahmoud, M.H.; Alshatwi, A.A. Identification of titanium
dioxide nanoparticles in food products: Induce intracellular oxidative stress mediated by TNF and CYP1A genes in human lung
fibroblast cells. Environ. Toxicol. Pharmacol. 2015, 39, 176–186, doi:10.1016/j.etap.2014.11.021.
20. Heringa, M.B.; Geraets, L.; van Eijkeren, J.C.; Vandebriel, R.J.; de Jong, W.H.; Oomen, A.G. Risk assessment of titanium dioxide
nanoparticles via oral exposure, including toxicokinetic considerations. Nanotoxicology 2016, 10, 1515–1525,
doi:10.1080/17435390.2016.1238113.
21. Rompelberg, C.; Heringa, M.B.; van Donkersgoed, G.; Drijvers, J.; Roos, A.; Westenbrink, S.; Peters, R.; van Bemmel, G.; Brand,
W.; Oomen, A.G. Oral intake of added titanium dioxide and its nanofraction from food products, food supplements and
toothpaste by the Dutch population. Nanotoxicology 2016, 10, 1404–1414, doi:10.1080/17435390.2016.1222457.
22. Farrell, T.P.; Magnuson, B. Absorption, Distribution and Excretion of Four Forms of Titanium Dioxide Pigment in the Rat. J.
Food Sci. 2017, 82, 1985–1993, doi:10.1111/1750-3841.13791.
23. Guo, Z.; Martucci, N.J.; Moreno-Olivas, F.; Tako, E.; Mahler, G.J. Titanium Dioxide Nanoparticle Ingestion Alters Nutrient
Absorption in an In Vitro Model of the Small Intestine. NanoImpact 2017, 5, 70–82, doi:10.1016/j.impact.2017.01.002.
Foods 2021, 10, 1910 10 of 11
24. Jia, X.; Wang, S.; Zhou, L.; Sun, L. The Potential Liver, Brain, and Embryo Toxicity of Titanium Dioxide Nanoparticles on Mice.
Nanoscale Res. Lett. 2017, 12, 478, doi:10.1186/s11671-017-2242-2.
25. Pinget, G.; Tan, J.; Janac, B.; Kaakoush, N.O.; Angelatos, A.S.; O’Sullivan, J.; Koay, Y.C.; Sierro, F.; Davis, J.; Divakarla, S.K.; et
al. Impact of the Food Additive Titanium Dioxide (E171) on Gut Microbiota-Host Interaction. Front. Nutr. 2019, 6, 57,
doi:10.3389/fnut.2019.00057.
26. EFSA Panel on Food Additives and Nutrient Sources added to Food; Younes, M.; Aggett, P.; Aguilar, F.; Crebelli, R.; Dusemund,
B.; Filipič, M.; Frutos, M.J.; Galtier, P.; Gott, D.; et al. Evaluation of four new studies on the potential toxicity of titanium dioxide
used as a food additive (E 171). EFSA J. 2018, 16, e05366, doi:10.2903/j.efsa.2018.5366.
27. French Agency for Food Environmental and Occupational Health & Safety. AVIS de l’Agence Nationale de Sécurité Sanitaire de
L’alimentation, de L’environnement et du Travail Relatif aux Risques Liés à L’ingestion de L’additif Alimentaire E171; Saisine n 2019-
SA-0036; Anses: Buenos Aires, Argentina, 2019; pp. 1–44.
28. EFSA. EFSA statement on the review of the risks related to the exposure to the food additive titanium dioxide (E 171) performed
by the French Agency for Food, Environmental and Occupational Health and Safety (ANSES). EFSA J. 2019, 17, e05714,
doi:10.2903/j.efsa.2019.5714.
29. Netherlands Food and Consumer Product Safety Authority (NVWA). Opinion of BuRO on Possible Health Effects of the Food
Additive Titanium Dioxide (E171). Available online:
https://english.nvwa.nl/documents/consumers/food/safety/documents/opinion-of-buro-on-possible-health-effects-of-the-food-
additive-titanium-dioxide-e171 (accessed on 17 August 2021).
30. Civil society organisations, Civil Society Organisations Demand the Removal of E171 from the EU List of Permitted Food
Additives. Available online: https://www.beuc.eu/publications/beuc-x-2019-
031_removal_of_e171_from_the_eu_list_of_permitted_food_additives.pdf (accessed on 17 August 2021).
31. EFSA Panel on Food Additives and Flavourings; Younes, M.; Aquilina, G.; Castle, L.; Engel, K.-H.; Fowler, P.; Frutos Fernandez,
M.J.; Fürst, P.; Gundert-Remy, U.; Gürtler, R.; et al. Safety assessment of titanium dioxide (E171) as a food additive. EFSA J.
2021, 19, e06585, doi:10.2903/j.efsa.2021.6585.
32. Dudefoi, W.; Moniz, K.; Allen-Vercoe, E.; Ropers, M.-H.; Walker, V.K. Impact of food grade and nano-TiO2 particles on a human
intestinal community. Food Chem. Toxicol. 2017, 106, 242–249, doi:10.1016/j.fct.2017.05.050.
33. Medina-Reyes, E.I.; Delgado-Buenrostro, N.L.; az-Urbina, D.; Rodríguez-Ibarra, C.; Déciga-Alcaraz, A.; González, M.I.; Reyes,
J.L.; Villamar-Duque, T.E.; Flores-Sánchez, M.L.O.; Hernández-Pando, R.; et al. Food-grade titanium dioxide (E171) induces
anxiety, adenomas in colon and goblet cells hyperplasia in a regular diet model and microvesicular steatosis in a high fat diet
model. Food Chem. Toxicol. 2020, 146, 111786, doi:10.1016/j.fct.2020.111786.
34. Perez, L.; Scarcello, E.; Ibouraadaten, S.; Yakoub, Y.; Leinardi, R.; Ambroise, J.; Bearzatto, B.; Gala, J.-L.; Paquot, A.; Muccioli,
G.G.; et al. Dietary nanoparticles alter the composition and function of the gut microbiota in mice at dose levels relevant for
human exposure. Food Chem. Toxicol. 2021, 154, 112352, doi:10.1016/j.fct.2021.112352.
35. Agans, R.T.; Gordon, A.; Hussain, S.; Paliy, O. Titanium Dioxide Nanoparticles Elicit Lower Direct Inhibitory Effect on Human
Gut Microbiota Than Silver Nanoparticles. Toxicol. Sci. 2019, 172, 411–416, doi:10.1093/toxsci/kfz183.
36. Chen, Z.; Han, S.; Zhou, D.; Zhou, S.; Jia, G. Effects of oral exposure to titanium dioxide nanoparticles on gut microbiota and
gut-associated metabolism in vivo. Nanoscale 2019, 11, 22398–22412, doi:10.1039/C9NR07580A.
37. Li, M.; Li, F.; Lu, Z.; Fang, Y.; Qu, J.; Mao, T.; Wang, H.; Chen, J.; Li, B. Effects of TiO2 nanoparticles on intestinal microbial
composition of silkworm, Bombyx mori. Sci. Total Environ. 2020, 704, 135273, doi:10.1016/j.scitotenv.2019.135273.
38. Zhang, S.; Jiang, X.; Cheng, S.; Fan, J.; Qin, X.; Wang, T.; Zhang, Y.; Zhang, J.; Qiu, Y.; Qiu, J.; et al. Titanium dioxide nanoparticles
via oral exposure leads to adverse disturbance of gut microecology and locomotor activity in adult mice. Arch. Toxicol. 2020, 94,
1173–1190, doi:10.1007/s00204-020-02698-2.
39. Giorgetti, L.; Spanò, C.; Muccifora, S.; Bellani, L.; Tassi, E.; Bottega, S.; Di Gregorio, S.; Siracusa, G.; Sanità di Toppi, L.; Ruffini
Castiglione, M. An integrated approach to highlight biological responses of Pisum sativum root to nano-TiO2 exposure in a
biosolid-amended agricultural soil. Sci. Total Environ. 2019, 650, 2705–2716, doi:10.1016/j.scitotenv.2018.10.032.
40. Bellani, L.; Muccifora, S.; Barbieri, F.; Tassi, E.; Ruffini Castiglione, M.; Giorgetti, L. Genotoxicity of the food additive E171,
titanium dioxide, in the plants Lens culinaris L. and Allium cepa L. Mutat. Res. Genet. Toxicol. Environ. Mutagenesis 2020, 849,
503142, doi:10.1016/j.mrgentox.2020.503142.
41. Tarnavölgyi, G. Analysis of Consumers’ Attitudes Towards Food Additives Using Focus Group Survey. Gábor TARNAVöLGYI
2003, 68, 193–196.
42. Hansen, J.; Holm, L.; Frewer, L.; Robinson, P.; Sandøe, P. Beyond the knowledge deficit: Recent research into lay and expert
attitudes to food risks. Appetite 2003, 41, 111–121, doi:10.1016/S0195-666300079-5.
43. Bearth, A.; Cousin, M.-E.; Siegrist, M. The consumer’s perception of artificial food additives: Influences on acceptance, risk and
benefit perceptions. Food Qual. Prefer. 2014, 38, 14–23, doi:10.1016/j.foodqual.2014.05.008.
44. Nutrition Institute. Composition and Labelling Information System as a Tool for Monitoring of the Food Supply. Available
online: https://www.nutris.org/en/composition-and-labelling-information-system (accessed on 12 December 2020).
45. Dunford, E.; Webster, J.; Metzler, A.B.; Czernichow, S.; Ni Mhurchu, C.; Wolmarans, P.; Snowdon, W.; L’Abbe, M.; Li, N.;
Maulik, P.K.; et al. International collaborative project to compare and monitor the nutritional composition of processed foods.
Eur. J. Prev. Cardiol. 2012, 19, 1326–1332, doi:10.1177/1741826711425777.
Foods 2021, 10, 1910 11 of 11
46. Pivk Kupirovič, U.; Miklavec, K.; Hribar, M.; Kušar, A.; Žmitek, K.; Pravst, I. Nutrient Profiling Is Needed to Improve the
Nutritional Quality of the Foods Labelled with Health-Related Claims. Nutrients 2019, 11, 287.
47. Zupanic, N.; Hribar, M.; Fidler Mis, N.; Pravst, I. Free Sugar Content in Pre-Packaged Products: Does Voluntary Product
Reformulation Work in Practice? Nutrients 2019, 11, 2577, doi:10.3390/nu11112577.
48. Agresti, A.; Brent, A.C. Approximate is better than “Exact” for interval estimation of binomial proportions. Am. Stat. 1998, 52,
119–126, doi:10.1080/00031305.1998.10480550.
49. Mintel Group Ltd. Mintel Global New Products Database. Availabe online: https://www.mintel.com/global-new-products-
database/features (accessed on 20 May 2021).
50. Mintel. Glossary 2016. Available online: https://www.gnpd.com (accessed on 20 May 2021).
51. Watson, E. Food Colors: How Will EFSA’s Decision on Titanium Dioxide Safety Impact the US Market? Available online:
foodnavigator.com (accessed on 17 August 2021).
52. Huybrechts, I.; Sioen, I.; Boonb, P.E.; De Neve, M.; Amiano, P.; Arganini, C.; Bower, E.; Busk, L.; Christensen, T.; Hilbig, A.; et
al. Long-term dietary exposure to different food colours in young children living in different European countries. EFSA
Supporting Publ. 2010, 7, 53E, doi:10.2903/sp.efsa.2010.EN-53.
53. Bachler, G.; von Goetz, N.; Hungerbuhler, K. Using physiologically based pharmacokinetic (PBPK) modeling for dietary risk
assessment of titanium dioxide (TiO2) nanoparticles. Nanotoxicology 2015, 9, 373–380, doi:10.3109/17435390.2014.940404.
54. Sprong, C.; Bakker, M.; Niekerk, M.; Vennemann, M. Exposure Assessment of the Food Additive Titanium Dioxide (E 171)
Based on Use Levels Provided by the Industry. Available online: https://rivm.openrepository.com/handle/10029/600597
(accessed on 17 August 2021).
55. Yin, C.; Zhao, W.; Liu, R.; Liu, R.; Wang, Z.; Zhu, L.; Chen, W.; Liu, S. TiO2 particles in seafood and surimi products: Attention
should be paid to their exposure and uptake through foods. Chemosphere 2017, 188, 541–547,
doi:10.1016/j.chemosphere.2017.08.168.
56. Morris, S. Dunkin’ Donuts Drops Titanium Dioxide. Available online: https://sensientfoodcolors.com/en-us/industry-
trends/dunkin-donuts-drops-titanium-dioxide/ (accessed on 30 May 2021).
57. Sensient Food Colors. Avalanche, Purely Brilliant Titanium Dioxide Alternatives. Available online:
https://sensientfoodcolors.com/en-us/color-solutions/avalanche/ (accessed on 30 May 2021).
58. Pravst, I.; Lavriša, Ž.; Kušar, A.; Miklavec, K.; Žmitek, K. Changes in Average Sodium Content of Prepacked Foods in Slovenia
during 2011–2015. Nutrients 2017, 9, 952, doi:10.3390/nu9090952.
... For the study, the former diameter was chosen. The application of this chemical compound can be found in fields such as paper making or textiles where it functions as an optically brightening agent [15], paints [16], plastics [17,18], food industry [19], depollution of water [20], and others. ...
Article
Full-text available
This study employs electrospinning to fabricate and characterize composite nanofibrous layers composed of polyamide 6 and titanium dioxide (TiO₂) particles. Polyamide 6 solutions were prepared with varying TiO₂ concentrations (5, 10, 15, 20, 30, 40, 50, 60, 70, and 80 wt%) to investigate the impact of filler content on the spinning process and the resulting nanofiber morphology. The conductivity and viscosity of these solutions were measured to assess their spinnability. The fabricated nanofibrous layers were characterized to determine the distribution of TiO₂ particles and their influence on the overall morphology. Additionally, the wetting behavior and ultraviolet radiation (UV) absorption properties of the layers were evaluated. The results indicate that nanofibrous layers containing 50% TiO₂ exhibit the highest UV absorption potential, making them promising candidates for further applications.
... Background incl. aims Titanium dioxide (TiO2) nanoparticles (NPs) are extensively studied due to their versatile applications ranging from photocatalysis [1] and photovoltaics [2] to incorporation into food items as additives [3] . The reduction of these NPs to sub-stoichiometric TiO2-x, e.g., by solar light irradiation, exposure to inert or reducing atmospheres, or doping is garnering significant interest due to the reaction products superior physical properties compared to the unprocessed NPs. ...
... Nevertheless, the European Food Safety Authority (EFSA, 2021c) has stated that TiO 2 can no longer be considered safe as a food additive. A Commission Regulation (2022/63), released in January, amended EC 1333/2008 regarding TiO 2 withdrawn authorization (Blaznik et al., 2022;Boutillier et al., 2022). ...
Chapter
Nanotechnology has led to a new era of innovation in the food sector, facilitating enhanced functionality and improved quality of food products. However, incorporating nanoparticles into food items raises significant safety and regulatory concerns. This chapter critically evaluates the safety concerns and regulatory complications related to nanomaterial exploitation in food, focusing on legislative structures in Europe and the USA, widespread nanoparticle applications, toxicity consequences, allergenicity considerations, and emerging nanotechnological methodologies for advancing food safety. Within Europe, the European Food Safety Authority (EFSA) predominantly shapes the regulatory model, while the United States Food and Drug Administration (FDA) assumes regulatory administration in the USA. These entities play a fundamental role in evaluating the safety of nanomaterial-infused foodstuffs. However, the regulatory framework exhibits inevitable failures, such as lacking comprehensive directives designed specifically for nanomaterials. This chapter emphasizes the authoritative for standardized evaluation protocols and challenging risk assessment methods. Nanoparticles experience wide-ranging utilization in food packaging, additives, and supplements, potentially creating possibilities for consumer exposure. Toxicological outcomes stemming from nanoparticle exposure are sophisticated and focus on multiple variables, including particle dimensions, surface characteristics, and chemical composition. Recent toxicity in animal trials highlights the necessity of understanding these variables to measure nanoparticle-incorporated products’ safety accurately. The nanoparticles, micro(nano)plastics, present unique challenges due to environmental concerns. Their tendency to accumulate within food matrices creates considerations about prolonged exposure and associated health issues. Moreover, to provide safer food, nanotechnological methodologies are broadly incorporated. A distinctive example includes nanoparticle incorporation for mitigating food allergens and the application of viral nanoparticles in food allergy research, manifesting innovative approaches to improve allergenicity risks. In addition, this analysis exhibits wide dimensions of safety warnings and regulatory complications related to nanomaterials in food, providing insights that will track upcoming research and regulatory endeavors within this promising area.
Article
Full-text available
Metal oxides (MOs) are the key materials in applications of biomedicine industrial technologies due to their versatile features. Knowing their possible toxicity level is crucial given some specific environments, particularly in water. We have learned that their reactivity almost depends on the electronic structure on the surface of the MOs. Thus, a detailed understanding of the electronic structure on the surface and its reactivity processes is useful for determining the toxicity in MOs and defining good descriptive parameters. We simulated the interaction of ZnO and TiO2 slab models with water and checked their geometric and electronic structure changes from the bulk of the material to the water interface. To this end, we used the density functional tight binding theory coupled with finite temperature molecular dynamics. We have observed the interaction of water with the MO surface in terms of electronic and geometric parameters for several conditions, such as temperature, hydrogenated or clean, and exposed surface. In doing so, we provide molecular-level insights into topographical and electronic processes on MO surfaces besides finding critical points on the surface that can explain the initialization of dissolution processes. Thus, we reveal information about potential toxicity descriptors in a systematic analysis approach.
Article
To achieve global sustainability goals, it is necessary to ensure food safety and security by adopting sustainable agricultural practices. However, the current agri‐food sector is not only in its most vulnerable state, but it is also becoming a threat to the environment due to the combination of industrial and human activities that are detrimental. These activities, including the use of highly toxic agrochemicals, have deteriorated the quality of arable soil, thereby impacting food security. One area of research emerging in recent years as a promising avenue to combat concerns around agricultural soil quality and productivity is that of the application of metal and metal oxide nanoparticles (MONPs). In this review, we comprehensively examine the synthesis processes, application, environmental impact, and regulations associated with MONPs in the agri‐food sector. In agriculture, these nanoparticles have been demonstrated to enhance crop yields by acting as delivery systems for nutrients, preventing soil degradation, and reducing the need for pesticides and fertilizers. In relation to ensuring food quality and security, these nanoparticles are used as additives to enhance nutritional content, improve texture, and extend shelf life. Alternatively, the antimicrobial properties of metal and metal oxide nanoparticles can be used to modify packaging materials and make them more effective at preserving food, reducing food waste by inhibiting the growth of harmful bacteria, and reducing the risk of foodborne illnesses. Overall, using nanoparticles in the agriculture and food industry offers exciting opportunities to promote sustainability, reduce environmental pollution, and improve food quality and safety.
Article
Full-text available
Metal oxides (MOs) are key materials in many fields, including technological, industrial, and biomedical applications. In most of these implementations, surface reactivity and reducibility properties are critical considerations. In their nanosized form, MOs exhibit enhanced reactivity that is connected to toxicity. Besides the fact that the biological molecule and the surface of the corresponding material interact chemically, little is known about the toxicological mechanisms involved on the atomic scale. The goal of this study is to investigate the role of TiO2 surfaces in interaction with one genetic base, namely guanine. Using a combination of the quasi-electronic density functional-tight binding molecular dynamics simulations and density functional theory calculations, we explored the adsorption modes of guanine with a stoichiometric and oxygen-deficient anatase TiO2 (101) surface. With such an approach, we have characterized new adsorption modes not previously found, and we have highlighted the relevance of defective surfaces in the adsorption of genetic basis, as a model for explaining possible toxicology mechanisms induced by the adsorption process.
Article
Full-text available
The present opinion deals with an updated safety assessment of the food additive titanium dioxide (E 171) based on new relevant scientific evidence considered by the Panel to be reliable, including data obtained with TiO2 nanoparticles (NPs) and data from an extended one-generation reproductive toxicity (EOGRT) study. Less than 50% of constituent particles by number in E 171 have a minimum external dimension < 100 nm. In addition, the Panel noted that constituent particles < 30 nm amounted to less than 1% of particles by number. The Panel therefore considered that studies with TiO2 NPs < 30 nm were of limited relevance to the safety assessment of E 171. The Panel concluded that although gastrointestinal absorption of TiO2 particles is low, they may accumulate in the body. Studies on general and organ toxicity did not indicate adverse effects with either E 171 up to a dose of 1,000 mg/kg body weight (bw) per day or with TiO2 NPs (> 30 nm) up to the highest dose tested of 100 mg/kg bw per day. No effects on reproductive and developmental toxicity were observed up to a dose of 1,000 mg E 171/kg bw per day, the highest dose tested in the EOGRT study. However, observations of potential immunotoxicity and inflammation with E 171 and potential neurotoxicity with TiO2 NPs, together with the potential induction of aberrant crypt foci with E 171, may indicate adverse effects. With respect to genotoxicity, the Panel concluded that TiO2 particles have the potential to induce DNA strand breaks and chromosomal damage, but not gene mutations. No clear correlation was observed between the physico-chemical properties of TiO2 particles and the outcome of either in vitro or in vivo genotoxicity assays. A concern for genotoxicity of TiO2 particles that may be present in E 171 could therefore not be ruled out. Several modes of action for the genotoxicity may operate in parallel and the relative contributions of different molecular mechanisms elicited by TiO2 particles are not known. There was uncertainty as to whether a threshold mode of action could be assumed. In addition, a cut-off value for TiO2 particle size with respect to genotoxicity could not be identified. No appropriately designed study was available to investigate the potential carcinogenic effects of TiO2 NPs. Based on all the evidence available, a concern for genotoxicity could not be ruled out, and given the many uncertainties, the Panel concluded that E 171 can no longer be considered as safe when used as a food additive.
Article
Full-text available
Titanium dioxide nanoparticles (TiO2NPs) have been widely used as food additives in daily life. However, the impact of oral intake of TiO2NPs on the nervous system is largely unknown. In this study, 7-week-old mice were treated with either vehicle or TiO2NPs suspension solution at 150 mg/kg by intragastric administration for 30 days. Our results demonstrated that oral exposure to TiO2NPs resulted in aberrant excitement of enteric neurons, although unapparent pathological changes were observed in gut. We also found the richness and evenness of gut microbiota were remarkably decreased and the gut microbial community compositions were significantly changed in the TiO2NP-treated group as compared with vehicle controls. Interestingly, oral exposure to TiO2NPs was capable to induce the inhibitory effects on locomotor activity, but it did not lead to significant change on the spatial learning and memory ability. We further revealed the mechanism that TiO2NPs could specifically cause locomotor dysfunction by elevating the excitement of enteric neuron, which might spread to brain via gut-brain communication by vagal pathway. However, inflammation response, enteric neurotransmitter 5-HT and major gut peptides might not be involved in this pathological process. Together, these findings provide valuable insights into the novel mechanism of TiO2NP-induced neurotoxicity. Understanding the microbiota–gut–brain axis will provide the foundation for potential therapeutic or prevention approaches against TiO2NP-induced gut and brain-related disorders.
Article
Full-text available
Ultra-processed, pre-packaged foods are becoming a growing part of our diet, while displacing whole and minimally processed foods. This results in an increased intake of free sugar, salt, and saturated fats, that have a profoundly negative effect on health. We aimed to assess the trend in free sugar content in pre-packaged foods in Slovenia and evaluate the efficacy of industry self-regulations designed to combat the excess consumption of free sugar. A nation-wide data collection of the Slovenian food supply was performed in 2015 and repeated in 2017. In 2017, 54.5% of all products (n = 21,115) contained free sugars (median: 0.26 g free sugar/100 g). Soft drinks became the main free sugar source among pre-packaged goods (28% of all free sugar sold on the market) in place of chocolates and sweets, of which relative share decreased by 4.4%. In the categories with the highest free sugar share, market-leading brands were often sweeter than the average free sugar value of the category. This indicates that changes in on-shelf availability towards a greater number of healthier, less sweet products are not necessarily reflected in healthier consumers’ choices. Relying solely on voluntary industrial commitments to reduce free sugar consumption will likely not be sufficient to considerably improve public health. While some further improvements might be expected over the longer term, voluntarily commitments are more successful in increasing the availability of healthier alternatives, rather than improving the nutritional composition of the market-leading products. Additional activities are, therefore, needed to stimulate reformulation of the existing market-leading foods and drinks, and to stimulate the consumption of healthier alternatives.
Article
Full-text available
Due to continued technological development people increasingly come in contact with engineered nanomaterials (ENMs) that are now used in foods and many industrial applications. Many ENMs have historically been shown to possess antimicrobial properties, which has sparked concern for how dietary nanomaterials impact gastrointestinal health via microbial dysbiosis. We employed an in vitro Human Gut Simulator system to examine interactions of dietary nano titanium dioxide (TiO2) with human gut microbiota. Electron microscopy indicated a close association of TiO2 particles with bacterial cells. Addition of TiO2 to microbial communities led to a modest reduction in community density but had no impact on community diversity and evenness. In contrast, administration of known antimicrobial silver nanoparticles in a control experiment resulted in a drastic reduction of population density. In both cases, communities recovered once the addition of nanomaterials was ceased. Constrained ordination analysis of community profiles revealed that simulated colonic region was the primary determinant of microbiota composition. Accordingly, predicted community functional capacity and measured production of short chain fatty acids were not changed significantly upon microbiota exposure to TiO2. We conclude that tested TiO2 nanoparticles have limited direct effect on human gut microbiota.
Article
Full-text available
The interaction between gut microbiota and host plays a central role in health. Dysbiosis, detrimental changes in gut microbiota and inflammation have been reported in non-communicable diseases. While diet has a profound impact on gut microbiota composition and function, the role of food additives such as titanium dioxide (TiO2), prevalent in processed food, is less established. In this project, we investigated the impact of food grade TiO2 on gut microbiota of mice when orally administered via drinking water. While TiO2 had minimal impact on the composition of the microbiota in the small intestine and colon, we found that TiO2 treatment could alter the release of bacterial metabolites in vivo and affect the spatial distribution of commensal bacteria in vitro by promoting biofilm formation. We also found reduced expression of the colonic mucin 2 gene, a key component of the intestinal mucus layer, and increased expression of the beta defensin gene, indicating that TiO2 significantly impacts gut homeostasis. These changes were associated with colonic inflammation, as shown by decreased crypt length, infiltration of CD8+ T cells, increased macrophages as well as increased expression of inflammatory cytokines. These findings collectively show that TiO2 is not inert, but rather impairs gut homeostasis which may in turn prime the host for disease development.
Article
Background Nanotechnologies provide new opportunities for improving the safety, quality, shelf life, flavor and appearance of foods. The most common nanoparticles (NPs) in human diet are silver metal, mainly present in food packaging and appliances, and silicon and titanium dioxides used as additives. The rapid development and commercialization of consumer products containing these engineered NPs is, however, not well supported by appropriate toxicological studies and risk assessment. Local and systemic toxicity and/or disruption of the gut microbiota (GM) have already been observed after oral administration of NPs in experimental animals, but results are not consistent and doses used were often much higher than the estimated human intakes. In view of the strong evidence linking alterations of the GM to cardiometabolic (CM) diseases, we hypothesized that dietary NPs might disturb this GM-CM axis. Materials and methods We exposed male C57BL/6JRj mice (n = 13 per dose group) to dietary NPs mixed in food pellets at doses relevant for human exposure: Ag (0, 4, 40 or 400 μg/kg pellet), SiO2 (0, 0.8, 8 and 80 mg/kg pellet) or TiO2 (0, 0.4, 4 or 40 mg/kg pellet). After 24 weeks of exposure, we assessed effects on the GM and CM health (n = 8 per dose group). The reversibility of the effects was examined after 8 additional weeks without NPs exposure (recovery period, n ≤ -5 per dose group). Results No overt toxicity was recorded. The GM β-diversity was dose-dependently disrupted by the three NPs, and the bacterial short chain fatty acids (SCFAs) were dose-dependently reduced after the administration of SiO2 and TiO2 NPs. These effects disappeared completely or partly after the recovery period, strengthening the association with dietary NPs. We did not observe atheromatous disease or glucose intolerance after NP exposure. Instead, dose-dependent decreases in the expression of IL-6 in the liver, circulating triglycerides (TG) and urea nitrogen (BUN) were recorded after administration of the NPs. Conclusion We found that long-term oral exposure to dietary NPs at doses relevant for estimated human intakes disrupts the GM composition and function. These modifications did not appear associated with atheromatous or deleterious metabolic outcomes.
Article
Food-grade titanium dioxide (E171) is a white additive widely used in solid and liquid food products. There is still debate about E171 toxic effects after oral consumption since this additive is deposited in colon, liver, spleen, testis and brain. The consumption of E171 commonly occurs with Western diets that are characterized by a high fat content. Thus, E171 could worsen adverse effects associated with a high fat diet (HFD) such as anxiety, colon diseases and testicular damage. We aimed to evaluate the effects of E171 on anxiety-like behavior, colon, liver and testis and to analyze if the administration of a HFD could exacerbate adverse effects. E171 was administered at ~5 mg/kgbw by drinking water for 16 weeks and mice were fed with a Regular Diet or a HFD. E171 promoted anxiety, induced adenomas in colon, goblet cells hypertrophy and hyperplasia and mucins overexpression, but had no toxic effects on testicular tissue or spermatozoa in regular diet fed-mice. Additionally, E171 promoted microvesicular steatosis in liver in HFD fed-mice and the only HFD administration decreased the spermatozoa concentration and motility. In conclusion, E171 administration increases the number of adenomas in colon, induces hypertrophy and hyperplasia in goblet cells and microvesicular steatosis.
Article
E171 (titanium dioxide, TiO2), an authorized foods and beverage additive, is also used in food packaging and in pharmaceutical and cosmetic preparations. E171 is considered to be an inert and non-digestible material, not storable in animal tissues, but the possible presence of TiO2 nanoparticles (NP) may present a risk to human health and the environment. We determined the presence of 15% TiO2 NP in a commercial E171 food additive product, by electron microscopy. The biological effects of E171 were assessed in Lens culinaris and Allium cepa for the following endpoints: percentage of germination, root elongation, mitotic index, presence of chromosomal abnormalities, and micronuclei. The results indicated low phytotoxicity but dose-dependent genotoxicity. We also observed internalization of TiO2 NP and ultrastructural alterations in the root systems.
Article
The widespread use of nanomaterials has raised concerns about the potential impact of nanoparticles on human health and the natural environment. Although high doses of TiO2 nanoparticles (NPs) are toxic to animals, low doses of TiO2 NPs have been shown to benefit their growth and immune functions. Intestinal microorganisms are critical in maintaining the normal life activities and ensuring the health of their host. The intestinal microorganisms of lepidopteran insects can promote growth and development, foster insecticide resistance, and improve resilience against diseases. However, to date, there is no report on the effects of TiO2 NPs on the intestinal microbiota of lepidopteran insects. In this work, we examined the effects of a low dose of TiO2 NPs (5 mg/L) on the intestinal microbiota of silkworm (Bombyx mori). The results showed that the exposure to TiO2 NPs did not alter the dominant species of intestinal microbiota significantly, but changed the abundance of individual species of intestinal microorganisms. Specifically, exposure to TiO2 NPs increased the uniformity of intestinal microorganisms. The abundance of Lachnospiraceae_NK4A136_group, involved in the metabolism of nutrients, as well as the abundance of Pseudomonas and Sphingomonas, both involved in detoxification and disease resistance, was increased. Meanwhile, among the non-dominant species, the conditional pathogenic bacteria Serratia exhibited decreased abundance. In addition, exposure to TiO2 NPs also increased the abundance of norank_f_Bacteroidales_S24-7_group, which could help relieve inflammation and regulate immune functions. The current study is the first to report the effects of TiO2 NPs on the intestinal microbiota of lepidopteran insects. The results demonstrated that TiO2 NPs could alter the composition of the intestinal microbiota of B. mori, and thus promote its growth and development, regulate its immune functions, and enhance its resistance to insecticide.
Article
The antibacterial activity of titanium dioxide nanoparticles (TiO2 NPs) has been extensively documented and applied to food packaging or environmental protection. Ingestion of TiO2 NPs via dietary and environmental exposure...