Soubantika Palchoudhury*a,
Katherine L. Jungjohannb,
Lakmali Weerasenac,
Abdollah Arabshahid,
Uday Ghargea,
Abdulaziz Albattaha,
Justin Millera,
Ketan Patela and
Robert A. Hollere
aDepartment of Civil and Chemical Engineering, University of Tennessee at Chattanooga, Chattanooga, Tennessee 37403, USA. E-mail: soubantika-palchoudhury@utc.edu; Fax: +1-423-425-5229; Tel: +1-423-425-5455
bCenter for Integrated Nanotechnologies, Sandia National Laboratories, Albuquerque, New Mexico 87185, USA
cDepartment of Mathematics, University of Tennessee at Chattanooga, Chattanooga, Tennessee 37403, USA
dSimCenter and Department of Mechanical Engineering, University of Tennessee at Chattanooga, Chattanooga, Tennessee 37403, USA
eCentral Analytical Facility, The University of Alabama, Tuscaloosa, Alabama 35487, USA
First published on 2nd July 2018
The rising demand for food and energy crops has triggered interest in the use of nanoparticles for agronomy. Specifically, iron oxide-based engineered nanoparticles are promising candidates for next-generation iron-deficiency fertilizers. We used iron oxide and hybrid Pt-decorated iron oxide nanoparticles, at low and high concentrations, and at varied pHs, to model seed pre-soaking solutions for investigation of their effect on embryonic root growth in legumes. This is an environmentally friendly approach, as it uses less fertilizer, therefore less nanoparticles in contact with the soil. Analysis from varied material characterization techniques combined with a statistical analysis method found that iron oxide nanoparticles could enhance root growth by 88–366% at low concentrations (5.54 × 10−3 mg L−1 Fe). Hybrid Pt-decorated iron oxide nanoparticles and a higher concentration of iron oxide nanoparticles (27.7 mg L−1 Fe) showed reduced root growth. The combined materials characterization and statistical analysis used here can be applied to address many environmental factors to finely tune the development of vital nanofertilizers for high efficiency food production.
Due to these improved transport mechanisms of NPs, researchers have begun investigating engineered nanostructures/nanoparticles (ENPs) for their potential use in next generation fertilizers.4–6 Raju et al., reported a significant increase in water uptake and enhanced germination of green gram seeds with 1 mM Fe NPs.7 Srivastava et al., used iron pyrite NPs to induce marked increase in growth rate of spinach plants.8 In terms of transport, ENPs have been observed to penetrate tomato plant roots and seed tissues,9 and more specifically, iron oxide NPs have demonstrated absorption into watermelon plants.10 Iron oxide NPs are of particular interest for nanofertilizers, as they are more benign compared to Fe NPs and iron is required by the plants to generate chlorophyll for photosynthesis.11 Recently, iron oxide NPs were used in replacement for commercial Fe-fertilizers to successfully replenish Fe deficiency in peanut plants.5 As nanostructures can now be made in reproducible shapes, sizes, alloyed structures, core–shell structures, and surface functionalization; the most active NP structure for improved plant growth and root absorption is still an active area of research.12–14
The complexity in the NP concentration within the fertilizer is based on providing enough of the dense nutrient within the soil to benefit the plant growth, without over-loading the soil to cause decreased plant biomass, decreased root length, and possibly plant toxicity.15–17 Limited reports are available on the interaction of plants with iron oxide based NPs,18,19 though Zhu et al. demonstrated that 500 mg L−1 of iron oxide NPs did not exert any toxicological effect in pumpkin plants over a prolonged exposure period.20 In addition, a study on green gram seeds showed that the 10 mg L−1 iron oxide NPs facilitated an increased physiological activity.14 In a study on soybean plants, magnetite NPs of concentration 60 mg L−1 were seen to translocate within the plant and increase chlorophyll levels.21 More recently, Jeyasubramanian et al., reported higher growth rate of spinach plants with hematite NPs (100–200 mg Fe) in hydroponic conditions.22 In this study, the slightly acidic pH of the hydroponics facilitated conversion of Fe3+ to water soluble Fe2+ ions, which were then absorbed by the plants. Therefore, iron oxide NPs present an optimal source for iron delivery to plants within fertilizers. However, the NP structure, concentration, and NP absorption have not been optimized.23
Soil pH is also a significant parameter in integrating ENPs as it largely influences the plant root's absorption of the nutrient.24 The absorption of the NPs is dependent on the surface functionality, transformations in morphology, surface structure, and agglomeration state of the NPs after interaction with natural organic matter or nutrients in the environment, irrespective of the type of NP.25,26 Typically, these mineral nutrients and biomolecules displace weaker binding surface ligands on the NP surface to form hybrid NPs, distinct from the original synthesized state of the ENP. Aggregation state of NPs also significantly affected nutrient absorption by plant roots.27 However, most studies on plants have reported the interactions of as-synthesized iron oxide NPs without taking into account the effect of particle transformation or pH. We have developed hybrid Pt-decorated iron oxide NPs and growth solutions at different pHs to address this issue. No information is currently available in the literature of a comparative study between iron oxide and hybrid Pt–Fe2O3 nanostructures.
In this study, we have investigated an experimental matrix of beaker-type NP-containing aqueous growth solutions on edible legumes of different sizes (e.g., green gram (mung bean), black bean, chickpea, green pea, and red bean) that represent a significant fraction of crops consumed world-wide (Fig. 1). Fifteen different growth solutions were tested over a period of six days for each of the five legume seeds with variances in NP type (functionalized iron oxide vs. Pt-decorated iron oxide), NP concentration (0.00554 mg L−1 and 27.7 mg L−1), and solution pH (5.5, 7, and 8) as compared to growth solutions without NPs. This is the first report comparing the interaction of seeds with iron oxide NPs and a newly formulated Pt-decorated hybrid counterpart. Each experiment was repeated six times to obtain reliable growth rates. Root samples were characterized after the growth period using electron microscopy and Fourier-transform infrared spectroscopy (FTIR). We found that the low concentration (0.00554 mg L−1) of iron oxide NPs enhanced root growth of all of the edible legumes by 88–366%, with the most significant growth rate observed for green gram seeds. These studies will be useful in developing a new class of Fe-enhanced fertilizers, and methods for pre-soaking seeds in nutrient dense solutions at the initial stages of germination for seamless nutrient absorption and decreased fertilizer quantity for enhanced environmental safety.
The NPs were cleaned via centrifugation (high-speed minicentrifuge, Fisher Scientific) for 15 min at 14000 rpm to remove any organics as the supernatant. The iron oxide NPs were dissolved in DI water and sonicated for 15 min (Branson 1800, room temperature) to obtain well-mixed final product at the desired concentration (e.g., 5.54 × 10−3 and 27.7 mg L−1 Fe). The concentrations were confirmed using two methods; calculations based on sample weight and calibration plots obtained from ultraviolet-visible spectroscopy (UV-vis). These iron oxide NPs served as seeds for the synthesis of the Pt-decorated iron oxide NPs. In addition, the NPs were used in subsequent NP-seed interaction experiments.
The root growth experiment described above was conducted in different pH solutions (e.g., pH 5.5, 7, and 8) for each seed type to investigate any pH-dependent changes in NP-embryonic root interaction.
A multi-method material characterization technique was used to understand the effect of the nanofertilizers on the embryonic legume roots. Both the morphology and chemical composition of the roots were characterized using a FEI Titan ChemiSTEM (Thermo Scientific) with high-collection-angle X-ray energy dispersive spectroscopy (XEDS). A JEOL 7000 FE scanning electron microscope (SEM) equipped with XEDS was used to identify the overall surface and chemical composition of the roots. To characterize the surface functional groups on the roots, a Bruker Alpha Fourier transform infrared spectrometer (FT-IR) was used over 400–4000 cm−1 range on well-dried root samples. The FT-IR data was used to investigate the differences between the various NP growth solutions on embryonic root growth by detecting the surface ligands on the roots.
Results from our root growth study over a six-day period are represented in detailed statistical plots for both iron oxide and hybrid Pt-decorated iron oxide NPs for each of the five seed types. The statistical results conveyed two findings; iron oxide NPs facilitated better root growth as compared to the hybrid Pt-decorated iron oxide NPs and the low concentration iron oxide growth solution proved to be the best soak solution for increased root growth. Specifically, Fig. 4A and B showed time-dependent plots of the average root length of chickpea seeds in iron oxide and hybrid NPs, respectively. The control, low, and high NP concentrations were marked as water, low NP, and high NP, respectively in the plots for both iron oxide and hybrid NPs (Fig. 4). At low concentrations ∼5.54 × 10−3 mg L−1 Fe, iron oxide NPs significantly enhanced root growth, as suggested from the time-dependent root length plot in Fig. 4A. Though an inhibitory effect was observed at high NP concentrations (∼27.7 mg L−1 Fe), roots were seen in all tested samples for iron oxide NPs (Fig. S3, ESI†). The hybrid Pt-decorated iron oxide NPs exhibited a reduced growth rate of the roots as compared to the iron oxide NPs, but did not completely inhibit development of embryonic roots (Fig. 4B and S4, ESI†). The fact that the different legume seeds showed higher root growth in iron oxide NP growth solution in comparison to the hybrid Pt-decorated iron oxide NPs or the control DI water growth solutions was also supported through comprehensive statistical analysis using two-factors repeated measures analysis of variance (ANOVA) computed in MATLAB (Table S2, ESI†). Since iron oxide NP growth solutions performed better than Pt-decorated iron oxide NPs, we investigated the comparative influence of iron oxide NPs at both low and high concentrations on the five different legumes in one representative statistical plot. Fig. 4C shows the box plots for average root length after six days for each seed type under different concentrations of iron oxide NP growth solutions at pH 7. When we compared these parameters for chickpeas, we observed that there was a significant increase in growth rate of the roots when using low NP concentrations in comparison to water (88% increase) and high NP (184% increase). Further, we observed that low iron oxide NP treatment enhanced the growth of green pea and green gram by 160% and 366%, respectively (Fig. 4C) in comparison to the control growth solution.
The effect of NPs depended on the size and type of seeds, in addition to the concentration and morphology of the NPs, based on these plots in Fig. 4. In comparison to chick pea, green pea, and green gram, the growth of black and red bean seedlings was not affected by ENPs (Fig. 4C, S3 and S4, ESI†). Embryonic roots were observed in all treated black and red bean seeds, but the growth rate of these roots was not enhanced by iron oxide NP fertilizer, unlike the other legume seeds tested. This was likely because these bean types are richer in iron content as compared to the other legume seeds. Therefore, they were less affected by Fe-deficiency fertilizers like iron oxide NPs as the average inherent iron concentration in beans (55 μg g−1) is high in comparison to the other crops.30
In comparison of NP solutions at different pH conditions (pH 5.5, 7, and 8), the representative data from chick peas under the three growth solutions of control, low, and high iron oxide NP concentrations is shown (Fig. 5A and B). The embryonic roots showed the same dose response trend at all pHs, but a slower growth rate of embryonic roots was observed at pH 5.5 or 8 as compared to the neutral pH (Fig. 5A and B). Alternately, the NP concentration-growth trend of seedlings in hybrid Pt-decorated NPs were more sensitive to pH (Fig. 5C and D), but embryonic roots were seen in all samples, suggesting absence of severe toxic effect of these NPs at concentrations < 27.7 mg L−1 Fe. Fig. S5 and S6 (ESI†) show successful growth of first generation legume plants in potted soil, grown from seeds pre-soaked in both low and high concentration of iron oxide NP solution (pH 7). We also demonstrated the healthy growth of one whole generation of chick pea plant from seeds soaked in low concentration iron oxide NPs of pH 7 (Fig. S5, ESI†). These plant growth experiments in potted soil rule out the possibility of adverse effect of iron oxide NP fertilizer, particularly at the low concentration.
The root surfaces were characterized via SEM and XEDS after a six-day growth period to investigate the changes in physiology and chemical composition after interaction with the NPs (Fig. 6). Fig. 6A shows the SEM image of embryonic green gram roots grown in DI water after Au sputtering. Intact epidermis was observed in the control sample grown in DI water. The epidermis was undamaged in roots grown in low concentration of iron oxide NPs, as suggested by the SEM image (Fig. 6B). In addition, these roots had prominent root hairs to facilitate increased absorption of nutrients, as shown by Fig. 6C. In contrast, discernable change in morphology of the epidermis was seen in embryonic roots grown in higher concentration of iron oxide NPs, suggesting possible adverse impact at these high NP concentrations (Fig. 6C and D).31 Roots grown in Pt-iron oxide hybrid NPs showed NP aggregates on the surface, which likely caused the reduced growth of roots in these growth solutions (Fig. 6E). XEDS imaging confirmed the presence of Fe and O in roots grown in high concentration iron oxide NPs (Fig. S7, ESI†).
However, in roots grown in low concentration iron oxide NPs, the Fe was likely taken up or assimilated by the roots, as suggested by the absence of Fe in the XEDS image (Fig. S8, ESI†).9 Interestingly, Fe and O were detected in roots grown in high concentration hybrid Pt-decorated NPs, but Pt was not seen on the root surface. One explanation for the absence of Pt in the XEDS plot would be not high enough sensitivity from the detector at this scale, or the possible selective absorption of the 2 nm Pt NPs through pores in the plant walls, which could consequently induce the slower root growth (Fig. S9, ESI†).31
On the other hand, iron oxide NP soak solutions, particularly at the low concentration induced fertilizer-like impact on legume seeds, based on our observations of different seedlings. Therefore, green gram roots grown in low and high concentration of iron oxide NPs for six days were characterized via TEM as representative samples to understand the role and the uptake of these NPs (Fig. 7). Sections of the roots were viewed directly without staining to clearly locate the NPs within the roots, without hindrance in contrast from the stain. The red arrows indicate probable aggregates of iron oxide NPs and individual NPs within the root sections. Roots grown in low concentration of iron oxide NPs did not show distinct particles in the images (Fig. 7A) as compared to the roots grown in high NP concentrations (Fig. 7B and insert). Regions of many NPs indicate the large number of NPs within the root structure for the high NP concentration sample. The root samples were further characterized via XEDS and FT-IR spectroscopy to investigate the composition of particles absorbed and accumulated within the roots and a plausible mechanism to account for the increased root growth with iron oxide NP growth solution. A representative XEDS plot showing chemical composition of a section of green gram root grown in high concentration iron oxide NP pre-soak solution indicated presence of Fe and O, in addition to the C, P, S, Ca, and K from the organic components within the plant cells. This suggested absorption and accumulation of iron oxide NPs within the plant roots, based on the morphological information from TEM and SEM and the chemical composition from XEDS. Increased length in root hairs was also observed in legume seeds pre-soaked with low concentration iron oxide NP solution, which could account for increased nutrient uptake and the faster growth.32
To further understand why the iron oxide NPs caused increased growth of roots at low concentrations, we investigated the changes in chemical composition of embryonic roots interacted with NPs. In specific, the surface functional groups of well-dried root samples after six-day growth were analyzed using FT-IR spectroscopy. A plausible chemical basis for interaction of the iron oxide nanofertilizer is suggested based on the FT-IR analyses. Fig. 8 shows the comparative FT-IR analysis of iron oxide NPs and green gram roots from seeds pre-soaked in different growth solutions. The FT-IR spectrum of hematite NPs used as the growth solution showed peaks in the fingerprint region at 520 cm−1 characteristic to the Fe–O stretching vibrations and 438 cm−1 corresponding to hydrogen bonds formed by OH groups adsorbed on the iron oxide surface.22,33 The remaining peaks for hematite NPs characterize the PVP and PEI ligand coating on the NP surface. The peak at 1730 cm−1 was due to the CO stretch from PVP ligand coating while the two adjacent peaks between 2380 cm−1 and 2300 cm−1 could be attributed to C–N triple bonds likely from the interaction of the two ligands, PVP and PEI.34 The FT-IR spectrum of roots grown in low concentration iron oxide NPs exhibited the characteristic peaks at 2357 cm−1 and 2338 cm−1, similar to that of PVP/PEI-coated iron oxide NPs (Fig. 8), indicating absorption of NPs by the roots. The other peaks of the spectrum were characteristic of root samples. Broadly, these included peaks at 3272 cm−1 due to O–H and N–H groups, 2927 cm−1 and 2855 cm−1 attributed to CH3 and CH2 stretching vibrations, 1635 cm−1 owing to amide I, 1542 cm−1 from lignin, 1396 cm−1 due to cellulose, 1238 cm−1 owing to carbonyl stretch in ester and amide III, and 1038 cm−1 characteristic to polysaccharides.35,36 The FT-IR spectrum of green gram roots soaked in high concentration iron oxide NPs was similar to low concentration roots, indicating NP absorption by these root as well. However, the lignin content relative to that of polysaccharides and cellulose in these roots as indicated by the 1542/1038 cm−1 and 1542/1396 cm−1 peak ratios was different from the roots grown in low concentration iron oxide NPs.37 This difference in lignin content and increased root hair account for the enhanced growth of legumes in low iron oxide NP pre-soak solutions as compared to the high concentration NPs. The peaks at 2357 cm−1 and 2338 cm−1 were absent in FT-IR spectrum of green gram roots grown in DI water, confirming our suggested mechanism of internalization of iron oxide NPs by the roots. Similar trends in FT-IR spectrum was also observed with black bean root samples grown in different pre-soak solutions (Fig. S10, ESI†). Detailed characterization of NP transport is currently being investigated through computational modeling.
Fig. 8 FT-IR plots of iron oxide NPs and embryonic roots of green gram seeds grown in different concentrations of iron oxide NPs at neutral pH. |
In this study, increased plant growth was achieved through pre-soaking the seeds in growth solutions. This was a more environment-friendly approach as it decreased the quantity of fertilizer used and eliminated the need for adding fertilizer to the soil. This study is impactful in two ways; first it reports a new iron oxide NP fertilizer and pre-soak method effective in increasing plant growth, and secondly, the combined material characterization and statistical method provides a novel approach to assess the efficiency of ENPs as nanofertilizers. Since the increase in plant growth with iron oxide NPs was observed for many seed types, it reliably predicts the great potential of iron oxide NPs as nanofertilizers.
This integrated statistical and material characterization approach could serve as a new multi-method assessment metric for the application of iron oxide NPs in agriculture. The method will also be attractive in developing new nanofertilizer materials to enhance agricultural production, while minimizing the NP contamination impact on the soil environment.38 A plausible mechanism was suggested for absorption of iron oxide NP fertilizer and enhanced root growth, based on the FT-IR data. However, further investigation of plant growth in soil will be required to understand growth trends and interaction with NP fertilizers on a wider species of plants. In addition, detailed mechanism of NP absorption and distribution within the plant will be essential in developing new iron oxide NP based fertilizers and is currently under investigation. Currently, studies are being conducted on chemical analysis, hyperspectral imaging, and TEM analysis of the root, shoot, and leaf samples from plants grown with NP soaked seeds to achieve this goal. Computational modeling on the transport of NPs within the roots is also being conducted.
Footnote |
† Electronic supplementary information (ESI) available: Experimental details: XEDS image of Pt-iron oxide NPs; XRD and FT-IR plots of iron oxide NPs; Table showing size of different seeds; Plots showing the growth rate of green pea, green gram, black bean, and red bean seedlings in iron oxide and hybrid NPs; images showing first and second generation legume plants in potted soil; SEM-XEDS image of green gram roots grown in low concentration of iron oxide NPs and high concentration of Pt-decorated iron oxide NPs; FT-IR plots of black bean roots grown in low and high concentration of iron oxide NP growth solution. See DOI: 10.1039/c8ra04680h |
This journal is © The Royal Society of Chemistry 2018 |