Available via license: CC BY 3.0
Content may be subject to copyright.
This content has been downloaded from IOPscience. Please scroll down to see the full text.
Download details:
IP Address: 45.45.141.58
This content was downloaded on 03/01/2016 at 15:58
Please note that terms and conditions apply.
Effect of platinum nanoparticles on morphological parameters of spring wheat seedlings in a
substrate-plant system
View the table of contents for this issue, or go to the journal homepage for more
2015 IOP Conf. Ser.: Mater. Sci. Eng. 98 012004
(http://iopscience.iop.org/1757-899X/98/1/012004)
Home Search Collections Journals About Contact us My IOPscience
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
Nanobiotech 2015 IOP Publishing
IOP Conf. Series: Materials Science and Engineering 98 (2015) 012004 doi:10.1088/1757-899X/98/1/012004
Content from this work may be used under the terms of the Creative Commons Attribution 3.0 licence. Any further distribution
of this work must maintain attribution to the author(s) and the title of the work, journal citation and DOI.
Published under licence by IOP Publishing Ltd 1
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
2
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)
Weight (mg)
Water culture
Control
6.67 ± 2.80
31±3
16.33 ± 0.85
93±2
Experiment
9.22 ± 0.72
*
38±1
*
17.93 ± 0,87
100±2
*
Soil culture
Control
13.78 ± 1.98
57±1
24.4 ± 3.11
133±3
Experiment
14.12 ± 2.34
59±2
25.01 ± 2.49
145±5
*
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
4
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).
References
[1] Adili A, Crowe S, Beaux M 2008 Nanotoxicology 2 1–8
[2] Ma X, Geiser-Lee J, Deng Y and Kolmakov A Sci. Total Environ 2010 408 3053–61
[3] Salama H. J. Biotechnology 2012 3 190–7
Nanobiotech 2015 IOP Publishing
IOP Conf. Series: Materials Science and Engineering 98 (2015) 012004 doi:10.1088/1757-899X/98/1/012004
5
[4] Prasad M 2003 Plant physiology 50 764–80
[5] Lam C, James J, McClyskey R Crit. Rev. Toxicology 2006 36 189–217
[6] Churilov G and Ampleeva L 2010 (Rjazan: Rjazan State University Press) p 148
[7] Morgalev Yu, Astafurova T, Borovikova G, Zotikova A, Zaytseva T, Postovalova V,
Verkhoturova G and Morgaleva T Nanotechnic 2012 3 81–6
[8] Zotikova A, Astafurova T, Mikhaylova C and Bender O. 2013 Conf. Factors of plant resistance
to extreme natural and man-made environment (Tomsk) 94 –7
[9] Astafurova T, Morgalev Yu, Borovikova G, Zotikova A, Zaytseva T, Postovalova V,
Verkhaturova G and Morgaleva T 2013 Plant Physiology and Genetics 45 544–9
[10] Ershov B Rus.Chen.J. 2001 45 20–30
[11] Morgalev S, Morgaleva T, Morgalev Yu and Gosteva I 2015 Adv. Mat. Res. 1085 424-30
[12] Svetlichnyi Vand Lapin I 2013 Russian Physics Journal 56 581-7
[13] Wang Zhenyu and Xie Xiaoyan, Zhao Jian et al. 2012 Environ. Sci. Technol. 46 4434–41
[14] Panitchkin L and Raikova A 2008 Nanotechnology in agriculture 3 79–81
[15] Montaño M 2014 Environmental Chemistry 4 351–66
[16] Davronov K, Usmanov R and Kutchkarov K 2008 Agricultural biology 1 65–9
[17] Markovic Z, Todorovic-Markovic B, Kleut D, Nikolic N, Vranjes-Djuric S, Misirkic M,
Vucicevic L, Janjetovic K, Isakovic A, Harhaji L, Babic-Stojic B, Dramicanin M and
Trajkovic V 2007 Biomaterials 28 5437–48
Nanobiotech 2015 IOP Publishing
IOP Conf. Series: Materials Science and Engineering 98 (2015) 012004 doi:10.1088/1757-899X/98/1/012004
6