Zhihao Liang1, Xiaoqin Pan1,2, Wei Li2, Erfeng Kou1,2, Yunyan Kang1, Bingfu Lei1,2,3, Shiwei Song1. 1. College of Horticulture, South China Agricultural University, Guangzhou 510642, P. R. China. 2. Key Laboratory for Biobased Materials and Energy of Ministry of Education, College of Materials and Energy, South China Agricultural University, Guangzhou 510642, P. R. China. 3. Maoming Branch, Guangdong Laboratory for Lingnan Modern Agriculture, Guangdong, Maoming 525100, P. R. China.
Abstract
As the cadmium-free semiconductor quantum dots, ZnO quantum dots (ZnO QDs) have wide potential applications in agriculture. However, the effects of ZnO quantum dots on crop growth and nutritional quality have not been fully studied. In this work, the lettuce was sprayed with different concentrations of ZnO QDs from 50 to 500 mg·L-1 to evaluate their influence on lettuce antioxidant, biomass, and nutritional quality. The results showed that ZnO QDs existed in the lettuce in the form of Zn2+. Lettuce treated with 500 mg·L-1 ZnO QDs would produce a large amount of reactive oxygen species (ROS), which adversely affected the absorption of nutrients, soluble protein content, and chlorophyll content, thus reducing plant biomass. When the concentrations range from 50 to 200 mg·L-1, the antioxidant enzyme systems of lettuce were triggered to counteract the damage caused by excessive ROS. Moreover, ZnO QDs at this level promoted Ca, Mg, Fe, Mn, Zn, and B absorption and accumulation; increased soluble sugar content; and improved the lettuce biomass and nutritional quality.
As the cadmium-free semiconductor quantum dots, ZnO quantum dots (ZnO QDs) have wide potential applications in agriculture. However, the effects of ZnO quantum dots on crop growth and nutritional quality have not been fully studied. In this work, the lettuce was sprayed with different concentrations of ZnO QDs from 50 to 500 mg·L-1 to evaluate their influence on lettuce antioxidant, biomass, and nutritional quality. The results showed that ZnO QDs existed in the lettuce in the form of Zn2+. Lettuce treated with 500 mg·L-1ZnO QDs would produce a large amount of reactive oxygen species (ROS), which adversely affected the absorption of nutrients, soluble protein content, and chlorophyll content, thus reducing plant biomass. When the concentrations range from 50 to 200 mg·L-1, the antioxidant enzyme systems of lettuce were triggered to counteract the damage caused by excessive ROS. Moreover, ZnO QDs at this level promoted Ca, Mg, Fe, Mn, Zn, and B absorption and accumulation; increased soluble sugar content; and improved the lettuce biomass and nutritional quality.
With
the rapid development of nanotechnology, nanomaterials have
been widely used in the fields of agriculture and biology.[1,2] In the past few decades, plant cultivation technology has made remarkable
innovation and progress. Nanomaterials were also used as fertilizers,[3] pesticides,[4] or plant
growth regulators[5,6] in agri-biotechnological applications.
The influences of the type, particle size, surface charge, and surface
modification of nanomaterials on plant growth also have been fully
studied.[7−10] With an extensive application of nanomaterials, the toxicity of
nanomaterials has become an important issue. Because crops safety
is the first thing to ensure human food security. The understanding
of the interaction between nanomaterials and plants has become a crucial
topic for studying the impact of nanomaterials on ecosystems.Carbon-based nanomaterials (such as fullerenes, carbon nanotubes,
graphene quantum dots, and carbon quantum dots) and metal or metal
oxide nanomaterials (such as nCuO, nFe3O4, nTiO2, nCeO2, CdS QDs, etc.) have been used to study
their interaction with plants.[11−17] Using CdS:Mn/ZnS quantum dots to treat Snow Pea (Pisum sativum), when the concentration was up to
40 μg·mL–1, the content of total chlorophyll
decreased significantly, resulting in phytotoxicity.[12] Majumdar et al.[13] reported that
kidney been exposed to high concentrations of CeO2 nanoparticles
(NPs) (500 mg·mL–1) significantly decreased
the root antioxidant enzyme activities, but the soluble protein increased
by 204%. Szymańska et al.[14] found
that high concentrations (1000 mg·mL–1) of
TiO2 NPs could cause toxic symptoms of Arabidopsis
thaliana, increase antioxidant levels, and promote
root growth. Azhar et al.[15] observed that
CuO NPs had an adverse effect on Arabidopsis biomass, chlorophyll
content, guard cells, stomata aperture, and other organelles, and
significantly increased the accumulation of reactive oxygen species
(ROS) in leaves; the toxicity of CuO NPs was proved by the reduction
of biomass. Rui et al.[16] reported that
the Fe content in peanut plants treated with Fe2O3 NPs was higher than that in the control; the authors suggested that
Fe2O3 NPs adsorbed on sandy soil to improve
the utilization of Fe; Fe2O3 NPs enhanced the
root length, plant height, and biomass of peanut plant and promoted
the peanut growth by changing phytohormone content and antioxidant
enzyme activity. Ag NPs induced dose-dependent toxicity by affecting
the shoot and root length, biomass, photosynthesis, antioxidant enzyme
activity, and the content of nutrient elements in maize.[17] The relationship between different types of
nanoparticles and plant species is further studied to clarify the
unique effects of various nanoparticles on plant species, so as to
promote the safety and risk assessment of nanomaterials.Conventional
nano-ZnO has been widely studied in agriculture because
of its environmental protection, low cost, low toxicity, and high
electron mobility.[18−21] On this basis, ZnO has been developed into quantum dots material
with rich surface functional groups and excellent water solubility.[22,23] ZnO QDs have been widely used in the biological field.[24,25] Also, the extensive application of ZnO QDs will unavoidably cause
excessive ZnO QDs to enter into crop plants.[26] However, there were few reports on the effect of ZnO QDs in plant
cultivation. In this study, we used lettuce as a model plant to analyze
the effect of ZnO QDs on lettuce physiology. The element content of
lettuce was measured, and the effect of ZnO QDs on the absorption
and distribution of Ca, Fe, Mn, Mg, Zn, and B was analyzed. ROS production;
the lipid peroxidation level; and the activity of antioxidant enzymes
catalase (CAT), superoxide dismutase (SOD), and peroxidase (POD) were
measured. Finally, the effects of ZnO QDs on plant biomass and photosynthetic
pigment contents were measured to assess the oxidative stress response
induced by dose.
Results
Characterization
of ZnO QDs
As shown
in Figure A, the transmission
electron microscopy (TEM) image shows that the ZnO QDs are uniform
and monodispersed. The lattice spacing of ZnO QDs is 0.25 nm, corresponding
to the (001) crystal plane of wurtzite.[22] From the size distribution diagram, it can be seen that the average
size of ZnO QDs is 3.76 nm (Figure B). Such small and uniform nanosize makes it possible
for them to enter the plant body.[26] The
photoluminescence (PL) emission spectrum of the ZnO QD solution with
the excitation from 360 to 420 nm is shown in Figure A. It can be seen that the emission peak
of the ZnO QD solution is located at 570 nm with independent-excitation
effects, which proves that ZnO QDs have stable PL emission.[27]
Figure 1
(A) TEM and high-resolution TEM (HRTEM) images of ZnO
QDs; inset,
enlarged HRTEM image of single ZnO QDs. (B) Size distribution of ZnO
QDs.
Figure 2
(A) PL emission spectra of ZnO QDs (excitation
wavelength from
360 to 420 nm). (B) FTIR spectra of ZnO QDs. (C) XRD patterns of ZnO
QDs. (D) Full XPS spectra of ZnO QDs.
(A) TEM and high-resolution TEM (HRTEM) images of ZnO
QDs; inset,
enlarged HRTEM image of single ZnO QDs. (B) Size distribution of ZnO
QDs.(A) PL emission spectra of ZnO QDs (excitation
wavelength from
360 to 420 nm). (B) FTIR spectra of ZnO QDs. (C) XRD patterns of ZnO
QDs. (D) Full XPS spectra of ZnO QDs.As shown in Table , the ζ-potential of 50–500 mg·L–1 ZnO QDs ranges from 40.3 to 42.7 mV, indicating the good water stability
of the further applied concentration of ZnO QDs.[28] In Fourier transform infrared (FTIR) spectra (Figure B), the stretching
vibration band of Si–O can be clearly observed at 880 cm–1, indicating that silane has been coated onto the
ZnO QDs.[29] The peak at 3413 cm–1 is due to the stretching vibration of the O–H bond, while
the peak at 3243 cm–1 corresponds to stretching
of the N–H bond.[30] Bending vibration
of C–H is observed at 1394 cm–1. Due to the
presence of these hydrophilic functional groups, ZnO QDs can be well
dispersed in the aqueous solution.
Table 1
ζ-Potential
(mV) of ZnO QDs
at Concentrations in the Deionized Water
ZnO QDs
50 mg·L–1
100 mg·L–1
200 mg·L–1
500 mg·L–1
ζ-potential (mV)
40.27 ± 0.65
41.93 ± 1.88
41.36 ± 2.35
42.67 ± 0.83
X-ray diffraction (XRD) is used to
further characterize the crystalline
characteristics of ZnO QDs. As shown in Figure C, the peaks can be indexed to the crystal
planes of (100), (002), (101), (102), (110), (103), (112), and (202)
of ZnO, which can be attributed to the diffraction of wurtzite ZnO.[31] X-ray photoelectron spectroscopy (XPS) is used
to characterize the binding state of ZnO QDs. The peaks for C 1s,
N 1s, O 1s, Zn 2p, and Si 2p have been marked in Figure D. Among them, Zn 2p and O
1s belong to ZnO, while N 1s, C 1s, and Si 1s belong to the surface
modifier APTES. High-resolution XPS further reveals the valence bond
relationship in ZnO QDs (Figure S1). The
peaks at 1021.6 and 1044.6 eV are from Zn 2p3/2 and 2p1/2 in ZnO QDs, respectively. The distance between the two
peaks is 23.0 eV, which is consistent with the 2p1/2 and
2p3/2 peak spacings of Zn(II) in the standard manual. The
binding energy position of Zn 2p3/2 is 1021.6 eV, which
is 0.2 eV lower than the standard peak position of Zn(II) in ZnO (1021.8
eV). This might be due to the influence of surface modification.[32] Because APTES is modified on the surface of
quantum dots. In the high-resolution spectrum of O 1s, there are two
peaks in O 1s, one at 530.2 eV and the other at 531.8 eV. The former
comes from the O–Zn bond and the latter is mainly from the
C–O/Si–O bond. The C 1s spectrum mainly contains C–C,
C–O, C=O, and C–H bonds. Two peaks appear in
spectra of N 1s. The peaks at 399.7 and 398.3 eV correspond to the
N–C and N–H bonds (N 1s). These results for the XPS
spectra are consistent with those for the FTIR spectra. Based on the
above results, ZnO QDs are composed of C, H, O, N, and Zn elements,
all of which are essential for plant growth and development. Therefore,
it is meaningful to study the effect of ZnO QD on plants.
Effect of ZnO QDs on Zn Uptake by Lettuce
After 10
days of incubation in a nutrient solution without Zn2+,
the content of Zn in lettuce was measured to evaluate the
absorption, transport, and accumulation of ZnO QDs by lettuce. As
shown in Figure S2, with the increase of
treatment concentration, the content of Zn element in shoot and root
increased significantly, and the increment of Zn element in the shoot
was larger, indicating more accumulation of ZnO QDs in leaves. The
results primarily indicated the dose-dependent effect of ZnO QDs for
lettuce cultivation.
Effects on Lettuce Biomass
and Chlorophyll
Contents
Compared to the control plants, the total fresh
weights of treated groups increased by 13.95, 24.44, and 8.9% under
50, 100, and 200 mg·L–1 ZnO QD exposure (Figure A), while the total
dry weights of them increased by 10.4, 19.3, and 22.1%, respectively
(Figure B). However,
when exposed to 500 mg·L–1 ZnO QDs, the total
fresh weight and total dry weight of treated lettuce significantly
decreased by 21.47 and 33.5%, compared to those of the control, respectively,
which indicated the negative effect of ZnO QDs at a high concentration
of 500 mg·L–1. In response to this phenomenon,
the chlorophyll contents were measured. The contents of chlorophyll
a, chlorophyll b, and total chlorophyll were increased by 18.23, 42.82,
and 18.22% only under 50 mg·L–1 group. Groups
of 100 and 200 mg·L–1 treatments did not significantly
alter the chlorophyll b and total chlorophyll contents, while 500
mg·L–1 ZnO QDs decreased the chlorophyll a,
chlorophyll b, and total chlorophyll contents by 17.37, 31.25, and
17.38%, compared to those of the control, respectively (Figures C and S3). Wang et al.[33] found that 300
mg·L–1 ZnO nanoparticles could reduce the chlorophyll
content and biomass of A. thaliana.
We speculated that the change of lettuce biomass might be due to the
effect of ZnO on the pigment contents of lettuce leaves.
Figure 3
(A) Fresh weight,
(B) dry weight, and (C) chlorophyll content in
lettuce, exposed to different concentrations of ZnO QDs.
(A) Fresh weight,
(B) dry weight, and (C) chlorophyll content in
lettuce, exposed to different concentrations of ZnO QDs.
Analysis of Oxidative Stress
Confocal
laser scanning microscopy (CLSM) of dichlorofluorescein (DCF) fluorescence
was used to characterize the formation of ROS in the lettuce leaves.
As depicted in Figures and 5, no significantly increased fluorescence
intensity was observed with the treatment of 50 and 100 mg·L–1 ZnO QDs compared to the control. The fluorescence
intensity increased obviously at 200 mg·L–1 and reached the peak at 500 mg·L–1 (Figure D,E). Differently,
the fluorescence intensity of treated root showed that ROS generation
increased significantly only at 500 mg·L–1 (Figure E). which resulted
in less accumulation of ZnO QDs in roots than in leaves (Figure S2).
Figure 4
ROS production in lettuce leaves after
exposure to ZnO QDs. (A)
Control deionized water, (B–E) ZnO QD exposure of 50, 100,
200, and 500 mg·L–1, respectively.
Figure 5
ROS production in lettuce root after exposure to ZnO QDs. (A) Control
Deionized water, (B–E) ZnO QD exposure of 50, 100, 200, and
500 mg·L–1, respectively.
ROS production in lettuce leaves after
exposure to ZnO QDs. (A)
Control deionized water, (B–E) ZnO QD exposure of 50, 100,
200, and 500 mg·L–1, respectively.ROS production in lettuce root after exposure to ZnO QDs. (A) Control
Deionized water, (B–E) ZnO QD exposure of 50, 100, 200, and
500 mg·L–1, respectively.In addition, the measurement of MDA content was used to analyze
the stress induced by ZnO QDs. In Figure A, the shoot MDA content of lettuce exposed
to 50 mg·L–1 ZnO QDs was not significantly
different from that of the control. With an increase of the concentration,
the MDA contents of root and shoot both increased significantly. When
the concentration reached 500 mg·L–1, the MDA
content also reaches the maximum, and the MDA contents of the shoot
and root increased by 26.68 and 41.91% compared with that of the control,
respectively.
Figure 6
Lipid peroxidation. (A) MDA and the activity of antioxidant
enzymes
(B) CAT, (C) SOD, and (D) POD in lettuce shoot and roots exposed to
different concentrations of ZnO QDs. Different letters indicate that
ZnO QDs with different concentrations have significant differences
at the P < 0.05 level. The letters in the figure
that follows have the same meaning.
Lipid peroxidation. (A) MDA and the activity of antioxidant
enzymes
(B) CAT, (C) SOD, and (D) POD in lettuce shoot and roots exposed to
different concentrations of ZnO QDs. Different letters indicate that
ZnO QDs with different concentrations have significant differences
at the P < 0.05 level. The letters in the figure
that follows have the same meaning.The antioxidant enzymes were measured to study the antioxidant
activity of ZnO QD-treated lettuce. From Figure B, compared with the control group, groups
of 50, 100, and 200 mg·L–1 remarkably increased
the CAT activity of the lettuce shoot, while that of the 500 mg·L–1 group significantly decreased. Only groups of 200
and 500 mg·L–1 showed a significant increase
in CAT activity compared to other groups. As can be seen in Figure C, all treated groups
except the group of 500 mg·L–1 significantly
improved the SOD activity of lettuce. When the concentration was up
to 500 mg·L–1, the activity of root SOD obviously
decreased. Peroxidase (POD) can catalyze H2O2 to react with acids and amines to reduce the damage to the cell
membrane and stabilize the selective permeability of the membrane.
It can be seen from Figure D that the effect of ZnO QDs on POD activity increased first
and then decreased with an increase of ZnO QD concentration. When
the exposure concentration reached 500 mg·L–1, the POD activity decreased both in the shoot and root compared
to that in the control (Figure D). Results above demonstrated that an increased concentration
of ZnO QDs would improve the antioxidant activity of lettuce by enhancing
its CAT, SOD, and POD activities. However, when the treated concentration
is up to 500 mg·L–1, the enhanced antioxidant
activity induced by ZnO QDs would be ineffective.
Effect on Shoot Soluble Protein and Soluble
Sugar Contents
As shown in Figure A, the total soluble protein content of lettuce
reached its maximum at 100 mg·L–1 ZnO QD exposure,
which was about 50.86% higher than that of the control. This may due
to the stress response of the plant that promotes protein synthesis.[34] When the ZnO QD concentration was up to 500
mg·L–1, the soluble protein content decreased
by 31.1%. The total soluble sugar contents of treated groups with
concentration less than 500 mg·L–1 all increased
by 11.87, 31.51, and 33.81% compared to the control group, respectively.
However, the total soluble sugar content of the 500 mg·L–1 group significantly decreased by 33.62% (Figure B). Results above
demonstrated the high toxicity of 500 mg·L–1 ZnO QDs for lettuce growth.
Figure 7
(A) Soluble protein content and (B) soluble
sugar content in lettuce
exposed to different concentrations of ZnO QDs.
(A) Soluble protein content and (B) soluble
sugar content in lettuce
exposed to different concentrations of ZnO QDs.
Effects on the Absorption of Nutrient Elements
To explore the effect of ZnO QDs on plant nutrient absorption,
we measured the content of macronutrients (Ca, Mg) and micronutrients
(Zn, Fe, Mn, B). Compared to the control group, 50–200 mg·L–1 ZnO QD exposure significantly increased the accumulation
of Ca, Fe, and Mn from root and shoot. As for the lettuce shoot (Figure A), compared to the
control group, at the exposure of 500 mg·L–1 in the shoot, Ca and Mn contents were decreased by 12.06 and 11.69%,
respectively. Mg contents were increased by 14.32 and 15.24% at 100
and 200 mg·L–1, respectively. The Zn content
in the shoot increased with an increase of ZnO concentration and reached
the maximum at 500 mg·L–1, demonstrating the
absorption of ZnO QDs. In the lettuce root (Figure B), relative to the control group, the content
of Mg, Mn, and B in the root decreased significantly when the concentration
was 500 mg·L–1. Exposure of 200 and 500 mg·L–1 significantly increased the contents of Zn by 34.56
and 47.22%, respectively.
Figure 8
Ca, Mg, Fe, Mn, Zn, and B contents in lettuce
(A) shoot and (B)
root exposed to different concentrations of ZnO QDs.
Ca, Mg, Fe, Mn, Zn, and B contents in lettuce
(A) shoot and (B)
root exposed to different concentrations of ZnO QDs.
Discussion
Oxidative
Stress Response and Lipid Peroxidation
ROS in plants can
play the role of signal,[35] but excessive
ROS will oxidize proteins and lipids, and ultimately
affect plant growth.[36,37] The existence of nanomaterials
will produce oxidative stress on the plant, thus affecting the absorption
of nutrients and water.[38] Investigations
have shown that nanoparticles can produce stress, generating excess
ROS, which directly affects the enzyme activity in plants.[39,40] The accumulation of MDA is the result of ROS on membrane lipid damage
in plants. In this study, high concentrations (500 mg·L–1) of ZnO QDs could significantly increase the content of ROS and
MDA, which indicated that high concentrations of ZnO QDs induced stress
in lettuce, resulting in membrane lipid peroxidation, which caused
serious damage to lettuce. Similar results have been found in previous
studies on nanoparticles.[41−43]SOD, CAT, and POD are important
enzymes involved in antioxidant defense systems. Generally, when plants
are under external stress, a large number of active oxygen in vivo
will be produced. These antioxidant enzymes are very essential for
the removal of excessive O2– and H2O2.[44] Studies have shown that nanomaterials
can induce oxidative stress and change the activity of antioxidant
enzymes.[45−47] In this study, we found that the activity of antioxidant
enzymes in the shoot was more sensitive than that in the root when
lettuce was treated with ZnO QDs. Also, at low concentrations of ZnO
QDs, SOD, POD, and CAT activities increased significantly in a dose-dependent
manner. When the concentration reached up to 500 mg·L–1, the activities of antioxidant enzymes were significantly decreased,
except for the CAT activity of root, demonstrating the stress that
lettuce could not bare at 500 mg·L–1 concentration
of ZnO QDs. Similar results have been reported in other nanomaterials.[48,49]
Analysis of Nutritional Quality
Hayes
et al.[50] reported that nanoparticles could
affect the uptake of essential elements needed for plant growth and
balanced nutrition. The accumulation of nutrient elements is an effective
method to test how nanomaterials affect the nutritional quality of
plants.[51] Essential nutrients elements
such as Ca, Zn, Fe, Mn, B, and Mg play important roles in the growth
of plants.[38] The increased content of nutrient
elements in leaves can improve the nutritional quality of the edible
tissues.[52] In this work, lettuce being
exposed to the lower concentrations from 50 to 200 mg·L–1 increased the accumulation of essential elements, such as Ca, Fe,
Mn, and Zn, but the content of Ca, Fe, Mn, and B decreased when treated
with high concentrations (500 mg·L–1). The
content of nutrients can directly increase the chlorophyll content
in leaves. For example, the enzyme catalyzing chlorophyll synthesis
needs the activation of Fe, while the photolysis of water for photosynthesis
needs Mn participation, thereby increasing the photosynthetic rate
and biomass of leaves.[53]Chlorophyll
is the pigment that plants use to absorb light energy for photosynthesis.
The increase of chlorophyll content of plants is conducive to the
light absorption efficiency of photosynthesis and the formation of
carbohydrates.[54] The impact of nanomaterials
on photosynthesis has also attracted more and more attention.[55−57] The soluble protein content is closely related to photosynthetic
pigments, which can directly affect the photosynthesis capacity.[58,59] In this work, soluble protein content was increased by 6.12 and
50.86% at 50 and 100 mg·L–1, respectively.
Also, the contents of chlorophyll were significantly increased at
50 mg·L–1. Hu et al.[38] also reported a similar effect, they found that the treatment of
lettuce with nTiO2 increased the content of soluble protein
and chlorophyll. However, a significant decrease in chlorophyll content
was observed when exposed to 500 mg·L–1 ZnO
QDs. It might be due to an increase of MDA content, which damaged
the chloroplast membrane, resulting in a decrease in chlorophyll content.
The results are consistent with the previous findings of Sturikova
et al.[60] When lettuce was treated with
low-concentration zinc oxide QDs, the soluble protein and soluble
sugar content increased significantly, indicating that the nutritional
quality of lettuce has been improved, with potential applications
in agriculture. At the same time, the accumulation of soluble protein
and soluble sugar in plants is conducive to inducing antioxidation
and improving plant resistance.[61] Both
soluble protein and carbohydrate content maintain a certain degree
of metabolic balance in the organism, and when the plant is subjected
to external stress, this balance will fluctuate.[62] High-concentration ZnO treatment (500 mg·L–1) can significantly reduce the content of soluble proteins, which
may be due to the damage of cell membrane lipid, thus inhibiting protein
synthesis.[63,64]
Experimental
Section
Synthesis of ZnO Quantum Dots
Zinc
acetate dihydrate (Zn (AC)2·2H2O), ethanol
absolute (CH3CH2OH, 99.7%), 3-aminopropyl triethoxysilane
(APTES), and potassium hydroxide (KOH) were purchased from McLean.
All chemicals were of analytical grade and used without further purification.Water-soluble APTES-coated ZnO QDs were synthesized by a simple
sol–gel method.[32] In brief, 16.7
mmol zinc acetate dihydrate was dissolved in 50 mL of ethanol solution
followed by vigorous stirring and refluxed for 2 h at 78 °C.
When zinc acetate was completely dissolved, the above solution was
placed in a cold bath at room temperature. Meanwhile, 23.4 mmol KOH
was dissolved in 13.5 mL of ethanol with sonication. The KOH solution
was dropped into zinc acetate dihydrate solution under intense stirring
at room temperature until it became colorless and transparent. APTES
(800 μL) was mixed with 2 mL of deionized water and then poured
into the above-mentioned ZnO QD solution; APTES was hydrolyzed in
water and reacted with ZnO QDs to form silane-modified ZnO QDs. After
the mixture was centrifuged, a white precipitate was obtained. The
precipitate was then washed three times with ethanol to remove unreacted
impurities. Finally, the precipitated ZnO QD powder obtained by heating
in an oven at 60 °C for 12 h.
Characterization
of ZnO Quantum Dots
To obtain the structure and morphology
of the samples, high-resolution
transmission electron microscopy (HRTEM, JEOL-2010) images were collected.
The powder X-ray diffraction (XRD) patterns were measured in the range
of 2θ from 10 to 80°. The infrared spectrum was recorded
by a Nicolet 6700. Fourier transform infrared (FTIR) spectra were
collected at a wavenumber of 500–4000 cm–1, and the chemical composition of the sample was analyzed with KBr
as a reference. Photoluminescence (PL) spectra were recorded with
a Hitachi FL 7000 fluorescence spectrophotometer. X-ray photoelectron
spectroscopy (XPS) spectra were obtained using an X-ray photoelectron
spectrometer (AXIS ULTRA DLD, Kratos).
Plant
Growth and Treatment
Lettuce
seeds were seeded in the sponge blocks of hydroponics, and when the
third true leaf of the seedling appeared, they were transferred to
planting cups for the deep solution flow culture. After 2 weeks, different
concentrations of ZnO QDwater solutions were sprayed by foliar spraying.
ZnO QD solutions with different concentrations (0, 50, 100, 200, 500
mg·L–1) were prepared in deionized water and
then sprayed on the leaves once every 3 days until harvesting. Each
lettuce was sprayed with 4 mL of ZnO QDwater solutions on average
5 times during the treatment.
Growth
Parameters and Photosynthetic Pigment
Measurements
After harvesting, plants were thoroughly washed
with tap water and then rinsed three times with deionized water to
remove dust and residual ZnO QDs. Then, the shoot and root tissues
were separated and weighed on a balance. Then, the shoot and root
tissues were dried in an oven at 70 °C for 2 days to determine
their dry weight (DW). Meanwhile, fresh leaf tissues (0.5 g) were
soaked in a 50 mL centrifuge tube containing 25 mL of absolute ethanol
and extracted for about 24 h until the leaves turned white. Then,
the absorbance of the supernatant was measured at 470, 646, and 663
nm by a UV–vis spectrophotometer.
Physiological
Parameters
The physiological
parameters were determined by a UV–vis spectrophotometer. The
activity of superoxide dismutase (SOD) was determined by the photoreduction
method of nitrogen blue tetrazole, and the peroxidase (POD) activity
was measured by the guaiacol method.[65] The
determination of catalase (CAT) activity was estimated using the method
following Aebi.[66] The content of malondialdehyde
(MDA) was evaluated by a thiobarbituric acid (TBA) reaction.[67] The soluble protein content was analyzed using
the dying method with Coomassie brilliant blue G-250.[68] The content of soluble sugar was estimated by anthrone
colorimetry.[69]
Imaging
of ROS after ZnO QD Exposure
2′,7′-Dichloroflourescein
diacetate (DCFH-DA) was used
to qualitatively evaluate ROS in plants. DCFH-DA can be hydrolyzed
by esterase to produce DCFH. However, DCFH does not penetrate the
cell membrane, so the probe is easy to accumulate in the cell. DCFH
can be oxidized with cellular ROS to form fluorescent DCF. The green
fluorescence intensity is directly proportional to the level of ROS.[70] Leaf and root slices were immersed in pH 7.0
phosphate buffered saline (PBS) buffer containing 10 μM DCFH-DA,
incubated for 30 min, and then washed three times continuously to
remove excess DCFH-DA. Finally, the fluorescence image was observed
under a confocal laser scanning microscope (CLSM) with an excitation
wavelength of 488 nm and an emission wavelength of 530 nm.
Elemental Content Analysis
Lettuce
shoot and root were thoroughly washed three times with deionized water
to remove dust and residual ZnO QDs. Then, the shoot and root tissues
were dried in an oven at 70 °C for 2 days. The dry sample was
pulverized into powder and 300 mg were put into centrifugal tubes.
The contents of Ca, Mg, Zn, B, Fe, and Mn were successfully determined
by flame atomic absorption spectrometry.[71]
Statistical Analysis
Statistical
analysis was performed using IBM SPSS (version 22, SPSS, Inc.). The
mean values were compared using analysis of variance (ANOVA), and
the results were reported as mean ± standard deviation (SD).
The P value below 0.05 indicates a statistically
significant difference.
Conclusions
In the
present work, foliar application of ZnO QDs could influence
the antioxidant status of lettuce, thereby affecting the changes of
antioxidant enzyme activity, chlorophyll content, soluble protein,
and biomass. ZnO QD exposure at low levels (50, 100, 200 mg·L–1) significantly improved the lettuce biomass and nutritional
quality because ZnO QDs promote the uptake and translocation of nutrients.
However, when lettuce was exposed at 500 mg·L–1, increased ROS fluorescent intensity and MDA content and decreased
CAT, POD, and SOD activities were observed. In this study, the preliminary
relationship between ZnO QDs and lettuce growth was understood. Nevertheless,
additional work should be done to explore the potential mechanism
of ZnO QD impact on plants for agricultural and biotechnology applications.
Authors: Jing Hu; Xinyi Wu; Fan Wu; Weixiao Chen; Jason C White; Yu Yang; Bin Wang; Baoshan Xing; Shu Tao; Xilong Wang Journal: J Hazard Mater Date: 2019-12-06 Impact factor: 10.588
Authors: G C M Falck; H K Lindberg; S Suhonen; M Vippola; E Vanhala; J Catalán; K Savolainen; H Norppa Journal: Hum Exp Toxicol Date: 2009-06 Impact factor: 2.903