16 research outputs found
Effects of TiO<sub>2</sub> nanoparticles on wheat (<i>Triticum aestivum L</i>.) seedlings cultivated under super-elevated and normal CO<sub>2</sub> conditions
<div><p>Concerns over the potential risks of nanomaterials to ecosystem have been raised, as it is highly possible that nanomaterials could be released to the environment and result in adverse effects on living organisms. Carbon dioxide (CO<sub>2</sub>) is one of the main greenhouse gases. The level of CO<sub>2</sub> keeps increasing and subsequently causes a series of environmental problems, especially for agricultural crops. In the present study, we investigated the effects of TiO<sub>2</sub> NPs on wheat seedlings cultivated under super-elevated CO<sub>2</sub> conditions (5000 mg/L CO<sub>2</sub>) and under normal CO<sub>2</sub> conditions (400 mg/L CO<sub>2</sub>). Compared to the normal CO<sub>2</sub> condition, wheat grown under the elevated CO<sub>2</sub> condition showed increases of root biomass and large numbers of lateral roots. Under both CO<sub>2</sub> cultivation conditions, the abscisic acid (ABA) content in wheat seedlings increased with increasing concentrations of TiO<sub>2</sub> NPs. The indolepropioponic acid (IPA) and jasmonic acid (JA) content notably decreased in plants grown under super-elevated CO<sub>2</sub> conditions, while the JA content increased with increasing concentrations of TiO<sub>2</sub> NPs. Ti accumulation showed a dose-response manner in both wheat shoots and roots as TiO<sub>2</sub> NPs concentrations increased. Additionally, the presence of elevated CO<sub>2</sub> significantly promoted Ti accumulation and translocation in wheat treated with certain concentrations of TiO<sub>2</sub> NPs. This study will be of benefit to the understanding of the joint effects and physiological mechanism of high-CO<sub>2</sub> and nanoparticle to terrestrial plants.</p></div
Physiological responses of wheat seedlings upon exposure to different levels of CO<sub>2</sub>.
<p>Values are presented as mean±SD, error bars represent standard deviation (sample size, n = 64 under super-elevated CO<sub>2</sub> condition and n = 48 under normal CO<sub>2</sub> condition). Lower letters represent significant difference at p<0.05 between super-elevated and normal CO<sub>2</sub> treatments.</p
Phenotypic images of wheat seedlings in different concentrations of TiO2 NPs treatments with or without super elevated CO<sub>2</sub>.
<p>(I) Seedlings grown in different concentrations of TiO<sub>2</sub> NPs under normal CO<sub>2</sub> conditions in a plant growth chamber. (II) Seedlings grown in different concentrations of TiO<sub>2</sub> NPs under super-elevated CO<sub>2</sub> conditions.</p
Effects of TiO<sub>2</sub> NPs on phytohormone contents in wheat seedlings grown under elevated-and normal CO<sub>2</sub> conditions.
<p>Data are mean±SD, error bars represent standard deviation (sample size, n = 16 for treatments under super-elevated CO<sub>2</sub> condition and n = 12 for treatments under normal CO<sub>2</sub> condition). Lower letters represent significant difference at p<0.05 among TiO<sub>2</sub> NPs treatments under the same CO<sub>2</sub> conditions; Upper letters represent significant difference at p<0.05 between elevated CO<sub>2</sub> and normal CO<sub>2</sub> conditions at the same TiO<sub>2</sub> NPs concentration.</p
TEM image and particle size distribution of TiO<sub>2</sub> NPs.
<p>TEM image and particle size distribution of TiO<sub>2</sub> NPs.</p
Effects of TiO<sub>2</sub> NPs on seedling biomass and number of lateral roots.
<p>Values are mean±SD, error bars represent standard deviation (sample size, n = 12 for I and II, n = 16 for III, IV and V). Lower letters represent significant difference at p<0.05 among TiO<sub>2</sub> NPs treatments under the same CO<sub>2</sub> conditions; Upper letters represent significant difference at p<0.05 between super-elevated CO<sub>2</sub> and normal CO<sub>2</sub> conditions at the same TiO<sub>2</sub> NPs concentration.</p
Carbon Nanotubes Filled with Different Ferromagnetic Alloys Affect the Growth and Development of Rice Seedlings by Changing the C:N Ratio and Plant Hormones Concentrations - Fig 5
<p>Transmission electron micrographs of untreated rice roots (A), rice roots treated with MWCNTs (B), Fe-CNTs (C), FeCo-CNTs (D), EDS spectra of FeCo-CNTs in rice roots (E). CNTs are circled in images, cw: cell wall.</p
C: N ratio in rice roots and shoots after treatments with three different carbon nanotubes.
<p>C: N ratio in rice roots and shoots after treatments with three different carbon nanotubes.</p
Phytotoxicity of Silver Nanoparticles to Peanut (<i>Arachis hypogaea</i> L.): Physiological Responses and Food Safety
In the present study,
we investigated the effects of silver nanoparticles
(Ag NPs) on peanut (<i>Arachis hypogaea</i> L.) at physiological
and biochemical levels as well as the impacts on peanut yield and
quality. Peanuts were cultivated in sandy soil amended with different
doses of Ag NPs (50, 500, and 2000 mgĀ·kg<sup>ā1</sup>)
for 98 days. Physiological parameters including plant biomass, height,
grain weight, and yield suggested that Ag NPs could result in severe
damages in plant growth. At the biochemical level, Ag NPs did not
change the predominant isozymes of each antioxidant enzyme but significantly
elevated the amounts of antioxidant isozymes as compared to those
of the control, and the antioxidant enzyme activities were consistent
with the elevation of isozymes. Ag concentrations exhibited a doseāresponse
fashion in peanut tissues with increasing exposure doses of Ag NPs.
The evidence of Ag NPs in the edible portion of peanuts was confirmed
by transmission electron microscopy (TEM) with energy-dispersive X-ray
spectroscopy (EDS). Additionally, alteration of the contents of fatty
acids in peanut grains upon exposure to different doses of Ag NPs
indicated that metal-based NPs could impact crop yield and quality.
Taken together, our results suggested that the concerns over how to
efficiently and safely apply nanoparticle incorporated products in
agriculture and how to control their potential impact on the food
safety and food quality should draw more attention as NPs themselves
could be taken up by crops and humans exposed to them through food
consumption