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Effect of platinum nanoparticles on morphological parameters of spring wheat seedlings in a substrate-plant system

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When wheat is cultivated in the media contaminated with platinum nanoparticles, the change in the morphological and physiological indexes of wheat seedlings depends on the physico-chemical parameters of the germination substrate. The changes become less pronounced with the decreasing bioaccessability of the nanomaterial in the following order: water suspension – luvisols – phaeozems. Contamination with nanoparticles affects the height parameters and activates the mechanisms protecting the plant from stress. When using wheat seedlings as test organisms for biotesting the environmental safety of NPs, it is advisable to use the following parameters: weight of roots, weight of aerial part, leaf area, and flavonoid content.
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Effect of platinum nanoparticles on morphological parameters of spring wheat seedlings in a
substrate-plant system
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2015 IOP Conf. Ser.: Mater. Sci. Eng. 98 012004
(http://iopscience.iop.org/1757-899X/98/1/012004)
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Effect of platinum nanoparticles on morphological parameters
of spring wheat seedlings in a substrate-plant system
T Astafurova, A Zotikova, Yu Morgalev, G Verkhoturova, V Postovalova,
S Kulizhskiy, S Mikhailova
Tomsk State University, 36, Lenina ave., Tomsk, 634050, Russia, tel./fax: +7(3822)
534519
E-mail: yu.morgalev@gmail.com
Abstract. When wheat is cultivated in the media contaminated with platinum nanoparticles,
the change in the morphological and physiological indexes of wheat seedlings depends on the
physico-chemical parameters of the germination substrate. The changes become less
pronounced with the decreasing bioaccessability of the nanomaterial in the following order:
water suspension luvisols phaeozems. Contamination with nanoparticles affects the height
parameters and activates the mechanisms protecting the plant from stress. When using wheat
seedlings as test organisms for biotesting the environmental safety of NPs, it is advisable to use
the following parameters: weight of roots, weight of aerial part, leaf area, and flavonoid
content.
1. Introduction
With nanomaterial production on the steady increase, nanoparticles (NPs) are being released into the
environment at different stages of their life cycle, which makes it necessary to research possible
consequences of their interaction with elements of the biota and ecosystems. Recent research has
shown that NPs that penetrate into biological tissue cause various bioeffects, both positive and
negative [1-3]. Interacting with various cell structures, NPs can be catalysts in different reactions
producing not only growth promoters but also inhibitors [4,5]. The effect of NPs on plants may differ
from that of the salts of the same metals. Even in very low dosage, they can change physiological and
biochemical processes, while maintaining prolonged action [6]. The discovered bioactivity of
technogenous NPs confirms the necessity to research their migration and accumulation in plants
growing on the territories subject to contamination with finely-dispersed materials.
The aforementioned papers contain little data on the research into platinum NPs phytotoxicity
[7-9]. We know, however, that they show a strong regenerative ability related to their high antioxidant
activity as well as unique catalytic propertie [10].
Phytotoxicity is difficult to assess, because toxicity does not only depend on the NP physical
nature, production method, size and structure, but also on features of the biological models and, quite
possibly, their growing technique.
The purpose of this paper was to compare the effect of platinum NPs 4 nm in size on the morpho-
physiological traits of wheat seedlings, when growing them in water culture as well as on different soil
types.
2. Materials and methods
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The object of the study was water and soil cultures of 10-day plants of soft spring wheat (Triticum
aestivum L.), variety Novosibirskaya - 29, which were grown in a laboratory setting in a temperature
chamber at a constant temperature of 22 °С and light intensity of 150 W/m2 (photoperiod 12/12
hours). One set of experiments compared water and soil cultures. In water cultures, we grew the plants
in a fine medium containing platinum NPs with the initial concentration of 10 mg/l and used distilled
water as a control. In soil cultures, we grew the seedlings in containers with 200 g of Garant soil
containing, per 100 grams of soil, 30-50 mg of nitrogen, 70 mg of phosphorus, 80-100 mg of
potassium, pH 6.5, micronutrients, and humic growth promoters. Before seeding, the substrate was
irrigated by a suspension of NPs until their concentration reached 10 mg/kg of soil. Another set of
experiments used two types of soils, luvisol and phaeozem, through which we had poured a 10 mg/l
suspension of platinum NPs in a filtration column. Luvisol retained 13.4 % (C = 1 mg/kg) of the
platinum NPs introduced and phaeozem, 22.5 % (1.34 mg/kg). Uncontaminated soil served as a
control.
Platinum nanoparticles (nPt) were obtained by laser ablation in distilled water from high-purity
(99.97%) platinum bars [Morgalev et al., 2012]. The characteristics of NPs were verified by TEM
(Phillips CM-12, France), dynamic light scattering (Zetasizer Nano ZS, USA), and BET (TriStar 3000,
USA). Particle size Δ50=5 nm and specific surface S =36 m2/g.
Platinum nanoparticles bioaccumulation in the plants from the substrates was determined by ICP-
MS (ELAN DRC-e, USA) in homogenates from the plant roots and aerial parts (leaves + stem). The
morphometric changes were evaluated by the length of the root system, height of the seedlings and
weight of the organs. The content of chlorophylls and flavonoids in the leaves was measured by a
Dualex-4 sensor (France). The nitrogen index was calculated as a ratio of the sum of chlorophylls to
that of flavonoids.
The agrochemical soil composition was studied according to the following GOSTs: рН of the salt
extract, GOST 26483-85; labile phosphorus (P2 O5) and labile potassium (К2О) fractions, GOST R
54650-11; nitrate nitrogen, GOST 26951-86; exchangeable ammonium, GOST 26489-85; humus,
GOST 26213-91; exchangeable calcium and exchangeable magnesium, GOST 26487-85; hydrolytic
acidity, GOST 26212-91.
Statistica 7 software package was used for statistical data processing. All the indicators were
analyzed for normality of distribution. The significance threshold was set at р<0.05. The tables and
figures show the mean data and SEM.
3. Results and discussion
The nPt introduced into the cultivation medium triggered changes in the height and weight parameters
of the leaf and root system in wheat seedlings when those were cultivated in a water dispersion
medium and Garant substrate. In water cultures, the length and weight of the root increased
significantly, which indicates that platinum NPs actively interfere with the complicated mechanism of
plant growth regulation. Soil cultures were superior to their water counterparts in height and weight
parameters and the effects of NP introduction were less prominent (see Table 1).
One of the reasons for such differences is the NP lifetime in the nanosized state, which depends on
the properties of the dispersion medium [11]. In water solutions with natural stabilizers, it ranges from
several hours to 40 days and sometimes even exceeds a year [12, 13]. As to soil, there are very little
data showing that NP inactivation in soils may be long-term as indicated for ultradispersed metal
powders: they gradually oxidize in soils and serve as micronutrients for plants during their growth and
development [14].
Among other things, NP aggregation may reduce their bioaccessibility, which must affect the
bioaccumulation processes in the plant tissues. Our studies have shown that platinum NPs are
massively accumulated in the root system of wheat seedlings at their early ontogenetic stages, if they
are grown in water culture (see Table 2).
Nanobiotech 2015 IOP Publishing
IOP Conf. Series: Materials Science and Engineering 98 (2015) 012004 doi:10.1088/1757-899X/98/1/012004
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Table 1. Morphometric parameters of wheat seedlings grown in an aqueous dispersion medium or
soil comprising nPt a concentration of 10 mg /l and 10 mg / kg.
Variant
Root
Aboveground part
Length (cm)
Weight (mg)
Height (cm)
Water culture
Control
6.67 ± 2.80
31±3
16.33 ± 0.85
Experiment
9.22 ± 0.72
*
38±1
*
17.93 ± 0,87
Soil culture
Control
13.78 ± 1.98
57±1
24.4 ± 3.11
Experiment
14.12 ± 2.34
59±2
25.01 ± 2.49
Note: the asterisk hereinafter marks significant differences of parameters as compared to the control
with the confidence figure of p<0.05.
Water culture is an effective tool to evaluate not only the adaptative reserves of a growing
organism but also the unique role played by the tillering node in the initial growth and development of
plants. Located at the stem-root junction, it functions as a powerful physiological barrier to substance
transport, which, along with other possible mechanisms, helps restrict the access of NPs into the
vegetative part of plants at the early stage of their development. Therefore, fewer NPs entered the
aerial part, yet even in this case, the differences between test and control samples were tremendous. It
is noteworthy that NPs can not only migrate through xylem vessels from the root to leaves but also
move in the opposite direction with the help of a phloem, which is known to transport photosynthates
from leaves to where they are consumed [13].
In soil cultures, on the contrary, the nPt accumulation is much lower; nonetheless, the difference
between the test and control samples of the root system was still considerable (more than 50 times).
Crystalline nanostructures have much higher surface energy than macroforms, so their dissolution in
the soil moisture and transition to the germination zone must be significantly easier [15]. In our
research, however, the leading role in reducing NP bioaccumulation seems to belong to their
adsorption by soil elements, since both the oxidative modification and dissolution are negligible for
nPt in this time interval.
The other set of experiments studied the influence of the soil type on the display of biological effects
of nanomaterials. We used typical soils of the Siberian region: luvisol and phaeozem.
The phaeozem had somewhat higher fertility level vs. luvisol due to a greater content of humus
(6.4±0.6 vs. 5.4±0.5)%, labile phosphorus (175±35 vs.75±15) mg/kg, labile potassium (155±23
vs.100±15) mg/kg, exchangeable calcium and magnesium (20.4±1.5 vs.15.5±1.2 and 2.7±0.2
vs.4.9±0.59 respectively) mmol/100g. Both the soil types are favorable for grain farming.
Soil contamination with nPt led to a significant (p<0.05) increase in the content of exchangeable
ammonium (from 4.5±0.7 to 9.0±1.4) mg/kg in the luvisol and (from 15.1±3.0 to 4.7±1.4) mg/kg in
the phaeozem and hydrolytic acidity (from 4.9±0.59 to 6.66±0.8) mmol/100g in the luvisol and (from
5.01±0.6 to 6.8±0.8) mmol/100g in the phaeozem. At the same time, the content of nitrate nitrogen
Table 2. nPt content in water and soil cultures of wheat .
Variant
nPt content (mkg/g wet weight)
Water culture
Soil culture
Root
Aboveground part
Root
Aboveground part
Control
0.0012 ± 0.0001
0.00062 ± 0.00010
0.0016 ± 0.0005
≤ 0.0001
Experiment
42.96 ± 8.69
0.44 ± 0.08
0.81 ± 1.16
0.10 ± 0.02
Nanobiotech 2015 IOP Publishing
IOP Conf. Series: Materials Science and Engineering 98 (2015) 012004 doi:10.1088/1757-899X/98/1/012004
3
dropped (from 16.6±3.3 to 10.5±2.1) mg/kg in the luvisol and (from 15.1±3.0 to 4.7±1.4) mg/kg in the
phaeozem. Thus, we can see the effect of nPt on the agrochemical properties of the soils under study
and, therefore, on their fertility level.
When cultivated in the phaeozem, the control sample had a greater dry weight of its roots and aerial
part as well as root length and leaf area than in the luvisol, which corresponds to the agrochemical
evaluation (see Table 3).
However, although the agrochemical composition of both the soil types changed after nPt
contamination, the height parameters and vegetative weight of the plants changed significantly only in
the luvisol, and these are important indicators of cell division and elongation intensity.
Table 3. nPt impact on morphological parameters of 10-day wheat
seedlings grown in different soils.
Parameters
Luvisols
Phaeozems
Control
Experiment
Control
Experiment
Leaf area
(cm
2
)
4.15±0.49
5.14±0.24*
6.57±0.54
5.20±0.65
Dry above-
ground mass
(mg)
34.5 ± 0.2
47.6±0.2*
53.5±0.0
49.1±0.4
Length of
root (cm)
15.9±1.2
16.5±1.8
20.9±2.6
18.7±1.6
Dry weight
of roots (mg)
25.1 ±0.2
26.2±0.0
30.2±0.2
27.2±0.3
Under nPt contamination of the luvisol, both the leaf area and the overall aerial weight of the wheat
seedlings increased significantly, whereas the root system remained unchanged (see Table 3).
According to the literature, the stimulating effect may be due to the increased activity of redox
enzymes and photochemmical activity in chloroplasts as well as activating ATP synthesis and
resynthesis as one of the major factors of metabolisn regulation [16].
The absence of pronounced effects of the phaeozem contamination may be due to NP adsorption by
soil elements. As noted above, this soil retained more nanomaterial than the luvisol did, when we
poured the suspension through it. This may have been caused by different content of exchangeable
divalent cations promoting NP adsorption by pore walls. A more acidic reaction of the medium in the
luvisol could have contributed as well, judging by the pH of the salt extract (5.1±0.1 vs. 5.3±0.1).
Greater content of humus in the phaeozem could also have enhanced the protective function guarding
the plant roots from NP penetration.
This fact requires a cautious attitude to evaluating the factor of NP bioaccumulation by plants from
the soil. Its calculation as a ratio of the marker element concentration in a plant to that in a soil may be
misleading, since the bioaccessability of NPs may be considerably lower due to adsorption and
aggregation processes in the soil.
When exposed to heavy metals, plants usually accumulate secondary phenolic substances, which
form complexes with heavy metals, thus inactivating them. Besides, flavonoids (vegetable
polyphenols) have antioxidant properties and can neutralize free radicals produced by oxidative stress.
NPs of some metals can induce active forms of oxygen, which cause significant damage to cell
structures [17]. On the other hand, increasing content of flavonoids does not only indicate unfavorable
processes going on but also the activation of mechanisms preventing destructive changes.
The experiments have shown that soil contamination with nPt leads to variation of flavonoids in
seedlings grown in both the luvisol and phaeozem soils (see Figure 1). Especially striking is the
flavonoid content increase in wheat in the luvisol: 40% after the introduction of nPt. Most probably,
Nanobiotech 2015 IOP Publishing
IOP Conf. Series: Materials Science and Engineering 98 (2015) 012004 doi:10.1088/1757-899X/98/1/012004
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the growing amount of flavonoids in wheat seedlings is due to the defense mechanisms activated as a
response to nPt impact. The efficiency of this mechanism reveals itself in the stable content of
chlorophylls when exposed to nPt, since their amount is heavily influenced by the changes in the
microelement soil composition.
The nitrogen index calculated as a ratio of chlorophylls to flavonoids was changing downwards,
which indicated that the growth and development processes were intensified in the seedlings and they
required additional nitrogen nutrition.
Figure 1. nPt impact on biochemical parameters of 10-day wheat seedlings grown in luvisol and phaeozem
soils. Control and test samples, luvisol (1, 2); control and test samples, phaeozem (3, 4).
4. Conclusion
The research findings show that nPt penetrate plants better when they are cultivated in water media as
compared to soil substrates. Pt nanoparticles change the agrochemical composition of both the luvisol
and phaeozem soils. The morphological, physiological and biochemical changes in the plants under
study, when introducing nPt into the cultivation medium, become less pronounced depending on the
type of substrate and bioaccessibility of the nPt introduced in the following order: water suspension
luvisol phaeozem. Here, nPt affect the height parameters and leave the chlorophyll content virtually
unchanged, while activating protective mechanisms, which is confirmed by the increase in flavonoids.
When using wheat seedlings as test organisms for biotesting the environmental safety of NPs, it is
advisable to use the following parameters: weight of roots, weight of aerial part, leaf area, and total
flavonoid content.
Acknowledgments
The results obtained in the framework of the state task 37.901.2014/K Ministry of education and
science of Russia.
Work was conducted with the application of the Tomsk regional common use centre technical
equipment acquired thanks to a grant of the Russian Ministry of the Agreement No.14.594.21.0001
(RFMEFI59414X0001).
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... As gold is not a micronutrient required for plant growth, the utilization of gold nanoparticles as fertilizer is limited in agriculture. Platinum nanoparticles are reported as growth enhancers as they increase the length and weight of the plant root system (Astafurova et al. 2015). When Sinapis alba and Lepidium sativum were applied with the platinum nanoparticle, nutrient uptake and translocation were observed in shoot and roots of both the species without any toxicity effect (Astafurova et al. 2015). ...
... Platinum nanoparticles are reported as growth enhancers as they increase the length and weight of the plant root system (Astafurova et al. 2015). When Sinapis alba and Lepidium sativum were applied with the platinum nanoparticle, nutrient uptake and translocation were observed in shoot and roots of both the species without any toxicity effect (Astafurova et al. 2015). Few nanocrystalline metals such as iron, cobalt and copper were applied to soybean seeds, and improved chlorophyll index, nodule number and number of crops were observed (Ngo et al. 2014). ...
... In general, biologically engineered nanomaterials are less toxic than chemically synthesized, and are more biocompatible and safer. The behaviour, properties and decomposition of the nanomaterial should be studied to minimize the toxicity and make it environmentally safe (Astafurova et al. 2015). According to the group of researchers from the School of Agricultural, Food and Biosystems Engineering (ETSIAAB) under Universidad Politécnica de Madrid (UPM), zinc oxide nanoparticles can be used as a source of nano-fertilizer without any toxicity (Chemgroup 2017). ...
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In the generation of frequent climatic conditions, the international agricultural scenario is going through numerous and remarkable demanding situations. To obtain food security, nano-engineering and nanotechnology are a practical biotechnological application on agriculture for increasing the productivity of food crop plants, particularly cereals. Nanotechnology, a recent scientific tool, helps increase agricultural productivity by enhancing the efficiency of agronomic inputs and minimizing the relevant losses due to the drastic climate change. Human health in rural areas is highly affected by consuming nutrient-deficient food crops, and nanotechnology might be the sustainable crop biotechnology approach to accept this challenge. There are divergent and contrasting strategies of fortifying the food crops, especially cereals, with the valuable vitamins and minerals, which constitute the concept of nutritional diversification. However, the sustainability and affordability of these strategies have now no longer been achieved. Biofortification through the application of nanotechnology is a current, impending, hopeful, economical and durable agricultural method of providing the micronutrients which are essential to a diversified population of human beings that has narrow access to healthy diets. This chapter concerns about all the relevant factors of crop biofortification in cereals. It attempts to encapsulate and outline all of the biofortification studies through nanotechnology that has been performed on important cereal crop plants. Besides the challenges in biofortified cereal crops, nanotechnology and nano-engineering strategies have a great prospect to convene the challenges of malnutrition across the globe.
... Conversely, the opposite results were obtained by Feichtmeier et al. [14] for barley seedlings, where fresh biomass per plant decreased with exposure to increasing concentrations of Au-NPs (3 to 10 μg mL − 1 ), but a concentration of 1 μg mL − 1 of Au-NPs in the nutrient medium had a stimulating effect on biomass. Astafurova et al. [29] observed a significant increase in the weight of wheat seedlings treated with Pt-NPs in both water and soil culture; however, dry weight of shoots increased only when the plants grew in one of two soil types tested. An increase in fresh weight and dry weight of lettuce shoot was observed in our experiment due to Pt-NPs applied at higher concentration. ...
... Judging by the data reported in the literature, there is generally a positive correlation between phenolics content and plant exposure to Ag-NPs, in our case such a relationship was revealed at higher Ag-NPs concentrations. In the present experiment we also observed an increase in phenolics content due to 40 ppm Pt-NPs application; Astafurova et al. [29] found that treatment of wheat seedlings with Pt-NPs led to an increase in flavonoids contentdepending on the type of soil in which the plants grew, this increase even reached 40% compared to the control. Mirzajani et al. [25] observed a significant increase in carotenoids content in rice shoots when plants were treated with 60 mg L − 1 Ag-NPs, which is consistent with our data. ...
... In our experiment we did not observe any significant effects of Au-NPs on chlorophyll concentration, but it has been reported that treatment with Au-NPs (10-100 ppm) could produce higher chlorophyll content in B. juncea seedlings, especially in seedlings treated with 10 ppm Au-NPs [13]. No response of wheat seedlings in respect of chlorophyll level after exposure to Pt-NPs was observed by Astafurova et al. [29]. ...
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... The transfer of water under the action of capillary forces plays an essential role in soils, especially when water is pulled into the rhizosphere in the dry season. Plants take up PtNPs (Astafurova et al., 2015;Ahmed et al., 2021), which means that the established capillary transfer will enhance the uptake of PtNPs by the roots. The least active nanoparticles move in the capillary pores of the carbonate horizons. ...
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Chapter
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The increasing manufacture and implementation of engineered nanomaterials (ENMs) will continue to lead to the release of these materials into the environment. Reliably assessing the environmental exposure risk of ENMs will depend highly on the ability to quantify and characterise these materials in environmental samples. However, performing these measurements is obstructed by the complexity of environmental sample matrices, physiochemical processes altering the state of the ENM and the high background of naturally occurring nanoparticles (NNPs), which may be similar in size, shape and composition to their engineered analogues. Current analytical techniques can be implemented to overcome some of these obstacles, but the ubiquity of NNPs presents a unique challenge requiring the exploitation of properties that discriminate engineered and natural nanomaterials. To this end, new techniques are being developed that take advantage of the nature of ENMs to discern them from naturally occurring analogues. This paper reviews the current techniques utilised in the detection and characterisation of ENMs in environmental samples as well as discusses promising new approaches to overcome the high backgrounds of NNPs. Despite their occurrence in the atmosphere and soil, this review will be limited to a discussion of aqueous-based samples containing ENMs, as this environment will serve as a principal medium for the environmental dispersion of ENMs.
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Size characteristics, structure, and spectral and luminescent properties of nanoparticles fabricated by laser ablation of zinc metal targets in water and ethanol are experimentally investigated upon excitation by Nd:YAG-laser radiation (1064 nm, 7 ns, and 15 Hz). It is demonstrated that zinc oxide nanoparticles with average sizes of 10 nm (in water) and 16 nm (in ethanol) are formed in the initial stage as a result of ablation. The kinetics of the absorption and luminescence spectra, transmission electron microscopy, and x-ray structural analysis demonstrate that during long storage of water dispersions and their drying, nanoparticles efficiently interact with carbon dioxide gas of air that leads to the formation of water-soluble Zn(CO3)2(OH)6. In ethanol, Zn oxidation leads to the formation of stable dispersions of ZnO nanoparticles with 99% of the wurtzite phase; in this case, the fluorescence spectra of ZnO nanoparticles change with time, shifting toward longer wavelength region from 550 to 620 nm, which is caused by the changed nature of defects.
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Silica nanowires are one-dimensional nanomaterials that are being developed for use in biological systems. Unfortunately, little is known regarding the cytotoxic potential of this type of nanomaterial. Here, using two different human epithelial cell lines we have examined the cytotoxicity of silica nanowires over a broad concentration range. The results indicate that silica nanowires are nontoxic at concentrations below 190 µg/ml but exhibit considerable cytotoxicity at higher concentrations. Examination of the mechanisms responsible for nanowire-induced cytotoxicity indicates that apoptotic pathways are not activated. Instead, cytotoxicity appears to be primarily due to increased necrosis in cells exposed to high concentrations of nanowires. In contrast to what was seen with silica nanowires, analysis of silica nanoparticles revealed very little cytotoxicity even at the highest concentrations tested. These results indicate that structural differences between silica nanomaterials can have dramatic effects on interaction of these nanomaterials with cells.
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This work reports on the toxicity of CuO nanoparticles (NPs) to maize (Zea mays L.) and their transport and redistribution in the plant. CuO NPs (100 mg L(-1)) had no effect on germination, but inhibited the growth of maize seedlings; in comparison the dissolved Cu(2+) ions and CuO bulk particles had no obvious effect on maize growth. CuO NPs were present in xylem sap as examined by transmission electron microscopy (TEM) and energy dispersive spectroscopy (EDS), showing that CuO NPs were transported from roots to shoots via xylem. Split-root experiments and high-resolution TEM observation further showed that CuO NPs could translocate from shoots back to roots via phloem. During this translocation, CuO NPs could be reduced from Cu (II) to Cu (I). To our knowledge, this is the first report of root-shoot-root redistribution of CuO NPs within maize. The current study provides direct evidence for the bioaccumulation and biotransformation of CuO NPs (20-40 nm) in maize, which has significant implications on the potential risk of NPs and food safety.
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The rapid development and potential release of engineered nanoparticles (ENPs) have raised considerable concerns due to the unique properties of nanomaterials. An important aspect of the risk assessment of ENPs is to understand the interactions of ENPs with plants, an essential base component of all ecosystems. The impact of ENPs on plant varies, depending on the composition, concentration, size and other important physical chemical properties of ENPs and plant species. Both enhancive and inhibitive effects of ENPs on plant growth at different developmental stages have been documented. ENPs could be potentially taken up by plant roots and transported to shoots through vascular systems depending upon the composition, shape, size of ENPs and plant anatomy. Despite the insights gained through many previous studies, many questions remain concerning the fate and behavior of ENPs in plant systems such as the role of surface area or surface activity of ENPs on phytotoxicity, the potential route of entrance to plant vascular tissues and the role of plant cell walls in internalization of ENPs. This article reviewed the current knowledge on the phytotoxicity and interactions of ENPs with plants at seedling and cellular levels and discussed the information gap and some immediate research needs to further our knowledge on this topic.
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Because of the ability to induce cell death in certain conditions, the fullerenes (C(60)) are potential anticancer and toxic agents. The colloidal suspension of crystalline C(60) (nano-C(60), nC(60)) is extremely toxic, but the mechanisms of its cytotoxicity are not completely understood. By combining experimental analysis and mathematical modelling, we investigate the requirements for the reactive oxygen species (ROS)-mediated cytotoxicity of different nC(60) suspensions, prepared by solvent exchange method in tetrahydrofuran (THF/nC(60)) and ethanol (EtOH/nC(60)), or by extended mixing in water (aqu/nC(60)). With regard to their capacity to generate ROS and cause mitochondrial depolarization followed by necrotic cell death, the nC(60) suspensions are ranked in the following order: THF/nC(60)>EtOH/nC(60)>aqu/nC(60). Mathematical modelling of singlet oxygen ((1)O(2)) generation indicates that the (1)O(2)-quenching power (THF/nC(60)<EtOH/nC(60)<aqu/nC(60)) of the solvent intercalated in the fullerene crystals determines their ability to produce ROS and cause cell damage. These data could have important implications for toxicology and biomedical application of colloidal fullerenes.
  • A Adili
  • S Crowe
  • M Beaux
Adili A, Crowe S, Beaux M 2008 Nanotoxicology 2 1-8
  • X Ma
  • J Geiser-Lee
  • Y Deng
  • A Kolmakov
  • Sci
Ma X, Geiser-Lee J, Deng Y and Kolmakov A Sci. Total Environ 2010 408 3053-61