Abstract
Background
Soil acidity (and associated Al toxicity) is a major factor limiting crop production worldwide and threatening global food security. Electrostatic layer-by-layer (LBL) self-assembly provides a convenient and versatile method to form an extracellular silica nanocoat, which possess the ability to protect cell from the damage of physical stress or toxic substances. In this work, we have tested a hypothesis that extracellular silica nanocoat formed by LBL self-assembly will protect root border cells (RBCs) and enhance their resistance to Al toxicity.
Results
Scanning electron microscopy (SEM) and X-ray photoelectron spectroscopy (XPS) were used to compare the properties of RBCs surface coated with nanoshells with those that were exposed to Al without coating. The accumulation of Al, reactive oxygen species (ROS) levels, and the activity of mitochondria were detected by a laser-scanning confocal microscopy. We found that a crystal-like layer of silica nanoparticles on the surface of RBCs functions as an extracellular Al-proof coat by immobilizing Al in the apoplast and preventing its accumulation in the cytosol. The silica nanoshells on the RBCs had a positive impact on maintaining the integrity of the plasma and mitochondrial membranes, preventing ROS burst and ensuring higher mitochondria activity and cell viability under Al toxicity.
Conclusions
The study provides evidence that silica nanoshells confers RBCs Al resistance by restraining of Al in the silica-coat, suggesting that this method can be used an efficient tool to prevent multibillion-dollar losses caused by Al toxicity to agricultural crop production.
Electronic supplementary material
The online version of this article (10.1186/s12951-019-0486-y) contains supplementary material, which is available to authorized users.
Keywords: Silica nanoparticle, Layer by layer self-assembly technique (LBL), Root border cells (RBCs), Mitochondrial activity, Aluminum toxicity
Introduction
During the biological evolution, some marine organisms have developed various special structures to achieve optimal function. One of the obvious examples is a use of biominerals as their exterior coats/shells to fulfill many roles, including protection against physical stress and toxic substances [1–4]. Various (bio-) chemical modification methods have been developed to create (coat) artificial nanoshells on microbial or mammalian cells [5, 6]. It has also been shown that the nanoshells can confer cells new or unique properties [7–10]. Therefore, a material-based chemical strategy for the cell modification could meet various needs for more efficient applications of the cell biotechnology.
The electrostatic layer-by-layer (LBL) self-assembly provides a convenient and versatile method to synthesize nanoparticles with different surface compositions for strengthening the surface functionalization [2, 11–13]. The formation of a nanoparticle structure on the surface of solid is due to the alternating deposition of the polyelectrolyte by electrostatic interactions of anions and cations [3]. A uniformly thin and continuous layer of biocompatible silica is loaded on the surface of the yeast cell taking advantages of the LBL self-assembly technique [2]. Feifel et al. [14] demonstrates the potentiality of LBL to construct fully electro-active cyt c multilayer assemblies following natural examples of protein arrangements.
Silicon (Si) is taken up by roots mainly as monosilicic acid (H4SiO4) from the soil and translocated via xylem to the shoot. Although Si has not been considered as an essential element for higher plants, Si has been showed to play an astonishingly large number of diverse roles in various organisms [1]. Majority of Si is deposited in the specialized Si cells or extracellular space [15]. Intra- or extracellular solidification can significantly alleviate a range of abiotic stresses in rice plants, including heavy metal toxicity and lodging [16–18]. The presence of silicified structures improved plant cadmium tolerance of both rice seedlings and their single cells [16–18]. Silica nanostructures also enhance the capacity of plants or individual cell in coping with environmental stresses such as heat, drought stress and Cd toxicity [2, 10, 19].
Around 40% of the world’s arable land is acidic and thus contains high concentrations of free aluminum. Al hydrolyses in solution such that the trivalent Al species, Al3+, dominates in acid conditions (pH < 5) [20]. Thus, Al toxicity is a major limiting factor for plant growth and development in acid soils. While the breeding for Al tolerance has been on agenda for long time, most crops still display major yield losses when grown in acidic soils [21–23]. Can silica nanocoating ameliorate the impact of toxic Al species on root metabolism? To the best of our knowledge, no answers are available in the literature.
In this work, we have addressed this question by using LBL self-assembled nanoparticles for coating root border cells (RBCs), in an attempt to enhance their resistance to Al. Originated from the root cap meristematic cells, RBCs are programmed to produce and finally encapsulate the root apex. They are a population of the alive single cells that play a variety of biological functions in protecting the root tip from biotic and abiotic stress [24, 25]. Previous study shows RBCs function as a protection barrier of Al toxicity to root tips [25, 26], relying on the properties of cell wall in Al immobilization, predominantly in alkali-soluble pectin, which impairs Al access to the intracellular space [24, 27]. Our working hypothesis was that the LBL self-assembly of silica nanoparticles was supposed to enhance the roles of cell wall in Al immobilization as well as an “additional wall” of Al access to the symplast of RBCs. The findings of this work fully support this hypothesis and show that nanoshells formed on the surface of RBCs enhance its Al resistance by restraining the intrusion of Al into the cell, thus alleviating cellular injury.
Materials and methods
Plant materials
Seeds of pea (Pisum sativum L. cv Zhongwan no. 5) were germinated in a mist culture and RBCs were harvested as described previously [25, 28]. Pea seeds were immersed in 7.5% sodium hypochlorite for 30 min, and thereafter rinsed six times with deionized water. Seeds that were soaked, deformed and floating, were discarded, only unaltered seeds were kept and immersed in deionized water for 8 h, and then were spread on the mesh screen of the mist-culture device. Seeds were germinated at 24 °C in 20 L plastic tanks for 36 h with 80 s mist sprayed with 2 mM CaCl2 every 5 min. RBCs were harvested by snipping root tips into a plastic beaker containing 0.5 mM CaCl2 solution and stirring gently for 5 min. RBCs were pelleted at 4500×g for 10 min after removing the root tips. Pellets were re-suspended in an ultrapure water and centrifuged again. The rinsing procedure was repeated twice to yield purified RBCs.
Silica mineralization on the surface of RBCs
The silica mineralization was modified following an established method [11]. RBCs were incubated in 2 μg/L PDADMAC (Poly dimethyl diallyl ammonium chloride, Sigma) solution (prepared in 1 mM/L CaCl2) for 10 min. Excessive PDADMAC was removed by centrifugation at 1000×g for 5 min, and the pelleted cells were rinsed three times in 1 mM/L CaCl2 solution. Pelleted cells were then reacted with PSS (Poly (sodium-p-styrenesulfonate), Sigma) for 10 min, and centrifuged and rinsed as described in PDADMAC loading. (PDADMAC/PSS)2 coated RBCs were obtained after repeating the process of PDADMAC/PSS loading for once. Then (PDADMAC/PSS)2 coated RBCs were incubated in 1% (w/v) silica particles (in 0.15 M NaCl) for 10 min, centrifuged and rinsed as described for PDADMAC loading.
Cell viability of RBCs exposed to Al toxicity
Silicon coated or none-coated cells were exposed to 100 μM AlCl3 (2 mM CaCl2, pH 4.5) for 1 h. The cell viability was then detected microscopically by trypan blue (0.5%) exclusion test as described elsewhere [25].
Al adsorption and Morin stain
After being treated with 100 μM AlCl3 solution (containing 2 mM CaCl2, pH 4.5) for 1 h, RBCs were pelleted at 4500×g for 10 min and surplus Al3+ in the supernatant was determined by pyrocatechol violet (PCV) following the methods described previously by Li et al. [27]. Cells were washed three times with deionized water, and then incubated in 0.01% Morin solution for 30 min and rinsed three times with de-ionized water. The green fluorescence signal was observed respectively using a laser-scanning confocal microscope (LSCM, FV1000, Olympus). The image analysis was performed using the ImageJ (https://rsb.info.nih.gov/ij).
Scanning electron microscopy (SEM) and EDS analysis
After being treated with 100 μM AlCl3 solution (containing 2 mM CaCl2, pH 4.5) for 1 h, cells were pelleted at 4500×g and washed three times with 0.1 M PBS buffer solution. The pellet was then fixed in the glutaraldehyde (2.5%) solution for 24 h. Specimens were rinsed three times with 0.1 M PBS buffer and dehydrated through an ethanol dehydration series (30%, 50%, 70%, 90%, 95%) and 100% twice at 15-min intervals. The specimens were then processed with 1:1 (v/v) ethanol/isoamyl acetate mixed solution and isoamyl acetate solution for 10 min. Finally, specimens were desiccated in a critical-point dryer. SEM measurements (S-3700N, Hitachi, Japan) were performed for cell surface images, and the distribution of Ca and Al in cells was further analyzed by energy dispersive spectroscopy (EDS; Oxford, Inca 300, UK).
X-ray photoelectron spectroscopy (XPS) studies
After being treated with 100 μM AlCl3 solution (containing 2 mM CaCl2, pH 4.5) for 1 h, RBCs were pelleted at 4500×g for 10 min and rinsed three times with deionized water, and finally the pelleted RBCs were freeze-dried and kept for analysis of surface element content by X-ray photoelectron spectroscopy [27]. RBCs samples were pressed onto plastic adhesive tape using a spatula to obtain a smooth surface for XPS measurement (VG multilab 2000 equipment Thermo VG scientific, East Grinstead, West Sussex, UK) using the Al Ka X-ray line of 1486.6 eV excitation energy at 300 W. RBCs were vacuum-dried for at least 8 h before the measurement. To correct sample charges, high-resolution spectra were used as a reference by setting the C1s hydrocarbon peak to 284.6 eV. The background was subtracted. Data analysis was performed using Thermal Advantage software (http://www.tainstruments.com) and draw by Originpro 9. The ratios of atomic concentrations were calculated using the peak areas normalized on a basis of acquisition parameters and sensitivity factors supplied by the manufacturer.
Detection of reactive oxygen species (ROS)
Reactive oxygen species production was detected according to Hasanain et al. [29] with modifications. After Al3+ treatment for 1 h, the RBCs with or without nanoshells were incubated with 10 μM 5-(and 6)-chloromethyl-2′,7′-difluorodihydrofluorescein diacetate (CM-H2DCFDA, Thermo Fisher Scientific, Massachusetts, USA), dissolved in dimethyl sulfoxide and supplemented with 0.5 mM CaCl2, pH 4.5, in the dark at 25 °C for 30 min. Thereafter, the RBCs were rinsed with distilled water for 10 min in the dark. Fluorescence was imaged on a CLSM (FV1000, Olympus) at 488 nm excitation and 510–530 nm emission.
Detection of mitochondrial activity and mitochondrial membrane potential
The mitochondrial activity of RBCs was assessed by MTT [3-(4, 5-dimethylthiazol-2)-2, 5-diphenyl-2H-tetrazolium bromide] reduction according to a previously published procedure [28]. Cells were pelleted at 4500×g for 10 min, rinsed three times with deionized water, and suspended in 0.5 mM CaCl2, containing 250 µg mL−1 MTT, (Thermo Fisher Scientific, Massachusetts, USA) before and after Al3+ treatment. The suspension was gently shaken at 25 °C for 2 h in the dark. The cells were then harvested, re-suspended in 5 mL of isopropanol containing 0.04 mM HCl, and vigorously mixed to dissolve the formazan produced from the cleavage of MTT. The cell pellets were removed via centrifugation, and the absorbance of formazan in the supernatant was determined spectrophotometrically at 590 nm. The MTT reduction of RBCs was expressed as formazan formation (A590/5 × 105 cells).
The mitochondrial membrane potential was determined by JC-1 (5,5′,6,6′-tetrachloro-1,1′,3,3′-tetraethyl-benzimidazolyl-carbo-cyanine iodide, Thermo Fisher Scientific, Massachusetts, USA) staining. The purified cells were mixed with 20 μM JC-1 dye solution (1:1 [v/v]), and then incubated for 10 min at 37 °C. JC-1-loaded RBCs were excited at 488 nm using an Ar ion laser source, and the fluorescence was recorded simultaneously in two channels through a 515–545-nm band-pass filter (Green, Monomer) and a 580–600 nm long-pass filter (Red, J-aggregate) with two simultaneous independent detectors using a CLSM (FV1000, Olympus). Consequently, the mitochondrial depolarization is indicated by a decrease in the red/green fluorescence intensity ratio.
Statistical analysis
All experiment was repeated independently for three times. Statistical analyses were performed using the statistical program SAS 9.4 and EXCEL 2013.
Results
The application of LBL self-assembly technique modifies surface properties of RBCs
Root tips of pea and the attached RBCs grew vigorously in the mist culture (Fig. 1A); The trypan blue test was applied to observe the morphology and viability of silica-coated cells or bare cells exposed to 100 μM AlCl3 (pH 4.5) for 1 h (Fig. 1B–E). The harvested RBCs had width of 10 to 30 μm and were 100–200 μm in length. The exposure of Al induced cell death indicated in Fig. 1C. The images of SEM showed the differences in morphological features of RBCs with or without silica-coat under Al toxicity (Fig. 1F, G). The surface of the bare cells was relatively smooth, whereas the surface of cells treated by LBL technique became uneven, indicating the form of silica-coat. The analysis of EDS revealed that the cells with silica-coat accumulated more Al and less Ca compared with the bare cells (Fig. 1H). The ratios of C and O in cells treated by LBL self-assembly technique were also different from that of the bare cell. The results indicate the outermost layer of RBCs is covered with a unique new layer of silica nanoparticles which may enhance Al accumulation.
Silica-coat promotes Al deposition in cell surface
The adsorption assay showed that the silica-coated cells accumulated tenfold more Al than the bare cells (Fig. 2A), indicating an extraordinarily enhanced Al adsorption capacity of silica-coated cells. The stain of Morin also showed the surface of silica-coated cells accumulated more Al than the bare cells (Fig. 2B). Morin stain also disclosed the obvious Al accumulation in the nucleolus of bare cells (Fig. 2C, D), suggesting the intrusion of Al into the cells through the cell wall of RBCs without silica-coat.
The X-ray photoelectron spectroscopy (XPS) analysis was performed on the silica-coated cells for the information on the chemical composition of the cell surface. The Si2p peak appeared near 102.65 and 104.0 eV (Fig. 2E) corresponding to aluminum silicate hydroxide [30] and typical of silica [31], respectively. The magnitude of the peak at ~ 102.65 eV (70.5 at %) was much higher than the components at 104.0 (29.5 at %). Al2p peak appeared near ~ 73.10 eV (7.60 at %, Al2O3/Al [32]) and ~ 74.50 eV (92.4 at %, aluminum silicate hydroxide [30]) (Fig. 2F). These results indicated that Al on the surface of silica-coated cells mainly is mainly in the form of aluminum silicate hydroxide.
Silica-coat inhibits ROS production in RBCs induced by Al
The fluorescent probe CM-H2DCFDA was applied to detect ROS in silica-coated cells or bare cells exposed to 100 μM AlCl3 (pH 4.5) for 1 h. In this method, the intensity of the green fluorescence signal is proportional to the amount of accumulated ROS. The results showed that Al toxicity induced significant ROS burst in bare cells (Fig. 3a, b). The coating of silica on the surface of RBCs induced a slightly increased ROS production in the silica-coated cells (Fig. 3c). However, Al induced less ROS production in silica-coated cells than in the bare cells under Al toxicity (Fig. 3c, d). Therefore, the results show that the nanoshells can reduce the intracellular ROS production caused by Al toxicity.
Silica-coat enhances Al resistance of RBCs
Cell viability, determined by both trypan blue exclusion test and FDA-PI staining, decreased significantly after Al exposure in bare cells; however, this decrease was not observed in the silica-coated cells (Fig. 4A and Additional file 1: Figure S1). The results from the reduction of MTT also showed that the cells with nanoshells had a higher mitochondrial activity than the bare cells under Al toxicity (Fig. 4B), indicating less injuries occurred in mitochondria of cells with nanoshells.
The fluorescent probe JC-1 exhibit potential-dependent accumulation in mitochondria, indicated by a fluorescence emission shift from green (monomer, Em ~ 525 nm) to red (J-aggregate, Em ~ 590 nm), and mitochondrial depolarization is indicated by a decrease in the red/green fluorescence intensity ratio. The fluorescent probe JC-1 was used to specifically detect mitochondrial membrane potential of RBCs in here (Fig. 4D). The mitochondrial membrane potential decreased after bare cells were exposed to Al toxicity, as indicated by an increase in green fluorescence and radio of red/green (Fig. 4D, E). However, there was little differences in cells with nanoshells after Al exposure, although nano-coating process decreased the membrane potential (Fig. 4E, F). Therefore, membrane potential was significantly higher in the nanocoated cells than the bare cell under Al stress (Fig. 4C), which indicated that the nanocoated cell has stronger mitochondrial activity.
Discussion
Layer-by-layer self-assembly technique can alternately deposit the anionic and cationic polyelectrolyte onto the solid surface by electrostatic interaction [33]. Meanwhile, LBL is a simple, abundant film-forming material, free from the base material of the body structure, and can protect the biologically active molecules, such as proteins and enzymes [11, 34, 35]. Through LBL self-assembly technique, the surface of RBCs became uneven (Fig. 1g), similar to the results on individual mammalian cells or yeast [2, 11]. That indicate LBL self-assembly technique can also form nanoshells on the surface of RBCs. Previous studies highlight the LBL self-assembly technique is a safe and non-toxic method [2, 36], which also been confirmed in this article. LBL self-assembly technique has little negative effect on the viability of RBCs (Fig. 4A, C), except inducing a slight increase in the ROS production (Fig. 3), which does not have to be a negative response [37–39].
Silica-coat confers the RBCs a peculiar capacity of Al adsorption from both EDS analysis of Al content in spots of single RBC and determination of Al absorption in millions of RBCs population. Cells covered by the silica nanoshells accumulated much more Al than the bare cells (Figs. 1G, 2A). Morin staining is generally used to study the Al distribution and semi-quantitative analysis of Al content [40]. Previous study proved that morin can detect Al in the cytosol but not cell wall-bound Al or vacuole-compartmentalized Al [41, 42]. After exposure to 100 μM Al for 1 h, surface of cells with silica nanoshells showed brighter green fluorescence compared with the bare cells (Fig. 2C, D), while nucleolus was brighter in the bare cells. Thus, it appears that the formation of nanoshells confers the RBCs an Al3+-proof “coat” that attracts Al in cell surface and blocks the entrance of Al3+ into the cell.
The images of SEM showed the surface of silica-coated cells became uneven and accompanied with small crystals (Fig. 1G). The thickness of the silica shell was 100 nm in yeast [2] or 200–300 nm in rice suspension cells [19]. XPS analysis can detect the surface elements down to a depth of 5–30 nm [43], which was used to analysis the surface chemical composition of the silica-coated RBCs. The Al2p core-level X-ray photoelectron spectroscopy (XPS) spectra show an obvious peak at 74.5 eV (aluminum silicate hydroxide), Si2p peak at 102.65 eV (aluminum silicate hydroxide), which indicated aluminum and silicon may form aluminum silicate hydroxides. The formation of Al–Si complexes, presumably hydroxyaluminosilicate species, leads to reduction of bioavailability of aluminum. Wang et al. [44] further showed the formation of hydroxyaluminumsilicates in the apoplast can reduces the toxicity of aluminum by reducing the mobility of apoplastic Al. Thus, the extra layer of silica provides sufficient protection as an Al-proof coat for RBCs, and inhibit the Al entering symplasts, preventing cell from ROS burst and a consequent injury.
The extra layer of the silica reduces the entry of Al3+ and accumulation of Al in symplast, preventing a burst of ROS [45, 46]. The accumulation of intracellular ROS will impact the integrity of the cellular membranes and organelles, e.g. mitochondria [47–49]. Adopting the trypan exclusion test as a proxy for membrane integrity, we found that nanocoated cells kept the integrity of membrane under Al exposure while the bare cells lost the membrane integrity (Fig. 4A). Morin stain detected little Al in the cytoplast of RBCs with nanoshells while obvious accumulation of Al in nucleolus of bare cells was observed. Since less Al enters the RBCs with silica-coat (Fig. 2), relatively less ROS production was induced by Al toxicity as indicated by ROS probe (Fig. 3). The accumulation of ROS leads to the imbalance of intracellular redox homeostasis [50, 51]. Our work showed that silica nano-coat on the surface of RBCs reduces the production of ROS induced by Al toxicity, which allows cells to maintain higher activity under Al toxicity.
Al-triggered ROS production is considered to be a cause of ATP depletion [48, 52]. The accumulation of ROS in cells and the imbalance of intracellular redox homeostasis will lead to depolarization of the mitochondrial membrane potential and diminished mitochondrial activity [48, 53]. This may be a result of direct damage caused by ROS to the membrane system [54, 55], or be a result of ROS activation of ion transporters in mitochondrial membranes [56, 57]. The resultant mitochondrial dysfunction will then lead to the programed cell death (PCD) [58–60]. The membrane potential was significantly higher in nanocoated cells than the bare cells under Al stress (Fig. 4D, F). The mitochondrial membrane potential decreased after bare cells were exposed to Al toxicity (Fig. 4B). RBCs coated with silica had a higher mitochondrial activity than the bare cells after exposing to Al toxicity (Fig. 4A and Additional file 1: Figure S1). Therefore, silica-coated cells maintained higher membranes potential, enabling normal activity of mitochondria under Al toxicity, and preventing their PCD.
Root border cells act as a phalanx of biological ‘goalies’, which neutralize dangers to newly generated root from the soil. As summarized in the model (Fig. 5), silica nanoparticles layer, formed by LBL self-assembly, confers RBCs Al resistance by binding Al and forming aluminum silicate hydroxides, thus inhibits the entry of Al3+ into the symplast, therefore preventing ROS burst and injury to the mitochondria. These findings have major translational implications, by offering an approach for improvement of plant tolerance to Al toxicity caused by acid soils that occupies 40% of the land, thus ensuring the sustainability of agriculture and contributing to the global food security in the twenty first century.
Additional file
Authors’ contributions
MY designed and reviewed the experiments, YMF, SXG and XWL performed the most experiments. XWL analyzed the data and wrote the paper; XYC and TXC performed the experiments of mitochondrial activity of RBCs; SS and YMH reviewed the manuscript. All authors read and approved the final manuscript.
Acknowledgements
Not applicable.
Competing interests
The authors declare that they have no competing interests.
Availability of data and materials
All data generated or analyzed during this study are included in this published article.
Ethics approval and consent to participate
Not applicable.
Funding
This work was financially supported by the National Natural Science Foundation of China (31672228, 31172038), the Key Project of Department of Education of Guangdong Province (2014KZDXM061), the Provincial National Science Foundation of Guangdong Province (2015A030313637, 2016A030313379), the Science and Technology Project of Guangdong Province (2015A040404048), and Foundation for Distinguished Young Talents in Higher Education of Guangdong (LYM11125, 2015KQNCX174).
Publisher’s Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
References
- 1.Hamm CE, Merkel R, Springer O, Jurkojc P, Maier C, Prechtel K, Smetacek V. Architecture and material properties of diatom shells provide effective mechanical protection. Nature. 2003;421(6925):841–843. doi: 10.1038/nature01416. [DOI] [PubMed] [Google Scholar]
- 2.Wang G, Wang L, Liu P, Yan Y, Xu X, Tang R, Addadi L. Extracellular silica nanocoat confers thermotolerance on individual cells: a case study of material-based functionalization of living cells. ChemBioChem. 2010;11(17):2368–2373. doi: 10.1002/cbic.201000494. [DOI] [PubMed] [Google Scholar]
- 3.Yao H, Dao M, Imholt T, Huang J, Wheeler K, Bonilla A, Suresh S, Ortiz C. Protection mechanisms of the iron-plated armor of a deep-sea hydrothermal vent gastropod. Proc Natl Acad Sci. 2010;107(3):987–992. doi: 10.1073/pnas.0912988107. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Romano P, Fabritius H, Raabe D. The exoskeleton of the lobster Homarus americanus as an example of a smart anisotropic biological material. Acta Biomater. 2007;3(3):301–309. doi: 10.1016/j.actbio.2006.10.003. [DOI] [PubMed] [Google Scholar]
- 5.Liu Z, Xu X, Tang R. Improvement of biological organisms using functional material shells. Adv Funct Mater. 2016;26(12):1862–1880. doi: 10.1002/adfm.201504480. [DOI] [Google Scholar]
- 6.Park JH, Yang SH, Lee J, Ko EH, Hong D, Choi IS. Nanocoating of single cells: from maintenance of cell viability to manipulation of cellular activities. Adv Mater. 2014;26(13):2001–2010. doi: 10.1002/adma.201304568. [DOI] [PubMed] [Google Scholar]
- 7.Park JH, Hong D, Lee J, Choi IS. Cell-in-shell hybrids: chemical nanoencapsulation of individual cells. Acc Chem Res. 2016;49(5):792–800. doi: 10.1021/acs.accounts.6b00087. [DOI] [PubMed] [Google Scholar]
- 8.Carnes EC, Harper JC, Ashley CE, Lopez DM, Brinker LM, Liu J, Singh S, Brozik SM, Brinker CJ. Cell-directed localization and orientation of a functional foreign transmembrane protein within a silica nanostructure. J Am Chem Soc. 2009;131(40):14255–14257. doi: 10.1021/ja906055m. [DOI] [PubMed] [Google Scholar]
- 9.Wang B, Liu P, Jiang W, Pan H, Xu X, Tang R. Yeast cells with an artificial mineral shell: protection and modification of living cells by biomimetic mineralization. Angew Chem Int Ed. 2008;47(19):3560–3564. doi: 10.1002/anie.200704718. [DOI] [PubMed] [Google Scholar]
- 10.Baca HK, Carnes E, Singh S, Ashley C, Lopez D, Brinker CJ. Cell-directed assembly of bio/nano interfaces-a new scheme for cell immobilization. Acc Chem Res. 2007;40(9):836–845. doi: 10.1021/ar600027u. [DOI] [PubMed] [Google Scholar]
- 11.Lee J, Choi J, Park JH, Kim M, Hong D, Cho H, Yang SH, Choi IS. Cytoprotective silica coating of individual mammalian cells through bioinspired silicification. Angew Chem. 2014;53(31):8056–8059. doi: 10.1002/anie.201402280. [DOI] [PubMed] [Google Scholar]
- 12.Wang L, Nie Q, Li M, Zhang F, Zhuang J, Yang W, Li T, Wang Y. Biosilicified structures for cooling plant leaves: a mechanism of highly efficient midinfrared thermal emission. Appl Phys Lett. 2005;87(19):194105. doi: 10.1063/1.2126115. [DOI] [Google Scholar]
- 13.Caruso F, Caruso RA, Mohwald H. Nanoengineering of inorganic and hybrid hollow spheres by colloidal templating. Science. 1998;282(5391):1111–1114. doi: 10.1126/science.282.5391.1111. [DOI] [PubMed] [Google Scholar]
- 14.Feifel SC, Lisdat F. Silica nanoparticles for the layer-by-layer assembly of fully electro-active cytochrome c multilayers. J Nanobiotechnol. 2011;9(1):59. doi: 10.1186/1477-3155-9-59. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Ma JF, Yamaji N. Silicon uptake and accumulation in higher plants. Trends Plant Sci. 2006;11(8):392–397. doi: 10.1016/j.tplants.2006.06.007. [DOI] [PubMed] [Google Scholar]
- 16.He C, Ma J, Wang L. A hemicellulose-bound form of silicon with potential to improve the mechanical properties and regeneration of the cell wall of rice. New Phytol. 2015;206(3):1051–1062. doi: 10.1111/nph.13282. [DOI] [PubMed] [Google Scholar]
- 17.Ma J, Cai H, He C, Zhang W, Wang L. A hemicellulose-bound form of silicon inhibits cadmium ion uptake in rice (Oryza sativa) cells. New Phytol. 2015;206(3):1063–1074. doi: 10.1111/nph.13276. [DOI] [PubMed] [Google Scholar]
- 18.Wang L, Wang Y, Chen Q, Cao W, Li M, Zhang F. Silicon induced cadmium tolerance of rice seedlings. J Plant Nutr. 2000;23(10):1397–1406. doi: 10.1080/01904160009382110. [DOI] [Google Scholar]
- 19.Ma J, Zhang X, Zhang W, Wang L. Multifunctionality of silicified nanoshells at cell interfaces of Oryza sativa. ACS Sustain Chem Eng. 2016;4(12):6792–6799. doi: 10.1021/acssuschemeng.6b01736. [DOI] [Google Scholar]
- 20.Delhaize E, Ryan PR. Aluminum toxicity and tolerance in plants. Plant Physiol. 1995;107(2):315–321. doi: 10.1104/pp.107.2.315. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Von Uexküll HR, Mutert E. Global extent, development and economic impact of acid soils. Plant Soil. 1995;171(1):1–15. doi: 10.1007/BF00009558. [DOI] [Google Scholar]
- 22.Zheng SJ. Crop production on acidic soils: overcoming aluminium toxicity and phosphorus deficiency. Ann Bot. 2010;106(1):183–184. doi: 10.1093/aob/mcq134. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Kochian LV, Piñeros MA, Liu J, Magalhaes JV. Plant adaptation to acid soils: the molecular basis for crop aluminum resistance. Annu Rev Plant Biol. 2015;66:571–598. doi: 10.1146/annurev-arplant-043014-114822. [DOI] [PubMed] [Google Scholar]
- 24.Yang J, Qu M, Fang J, Shen RF, Feng YM, Liu JY, Bian JF, Wu LS, He YM, Yu M. Alkali-soluble pectin is the primary target of aluminum immobilization in root border cells of pea (Pisum sativum) Front Plant Sci. 2016;7:1297. doi: 10.3389/fpls.2016.01297. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Yu M, Shen R, Liu J, Chen R, Xu M, Yang Y, Xiao H, Wang H, Wang H, Wang C. The role of root border cells in aluminum resistance of pea (Pisum sativum) grown in mist culture. J Plant Nutr Soil Sci. 2009;172(4):528–534. doi: 10.1002/jpln.200800039. [DOI] [Google Scholar]
- 26.Cai M, Zhang S, Xing C, Wang F, Ning W, Lei Z. Developmental characteristics and aluminum resistance of root border cells in rice seedlings. Plant Sci. 2011;180(5):702–708. doi: 10.1016/j.plantsci.2011.01.017. [DOI] [PubMed] [Google Scholar]
- 27.Li XW, Liu JY, Fang J, Tao L, Shen RF, Li YL, Xiao HD, Feng YM, Wen HX, Guan JH, Wu LS, He YM, Goldbach HE, Yu M. Boron supply enhances aluminum tolerance in root border cells of pea (Pisum sativum) by interacting with cell wall pectins. Front Plant Sci. 2017;8:742. doi: 10.3389/fpls.2017.00742. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Yu M, Feng MY, Goldbach HE. Mist culture for mass harvesting of root border cells: aluminum effects. J Plant Nutr Soil Sci. 2006;169(5):670–674. doi: 10.1002/jpln.200620604. [DOI] [Google Scholar]
- 29.Hasanain M, Bhattacharjee A, Pandey P, Ashraf R, Singh N, Sharma S, Vishwakarma AL, Datta D, Mitra K, Sarkar J. α-Solanine induces ROS-mediated autophagy through activation of endoplasmic reticulum stress and inhibition of Akt/mTOR pathway. Cell Death Dis. 2015;6(8):e1860. doi: 10.1038/cddis.2015.219. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.He H, Barr TL, Klinowski J. ESCA studies of framework silicates with the sodalite structure. 2. Ultramarine. J Phys Chem. 1994;98(33):8124–8127. doi: 10.1021/j100084a033. [DOI] [Google Scholar]
- 31.Edgell MJ, Baer DR, Castle JE. Biased referencing experiments for the XPS analysis of non-conducting materials. Appl Surf Sci. 1986;26(2):129–149. doi: 10.1016/0169-4332(86)90001-2. [DOI] [Google Scholar]
- 32.Olefjord I, Mathieu HJ, Marcus P. Intercomparison of surface analysis of thin aluminium oxide films. Surf Interface Anal. 1990;15(11):681–692. doi: 10.1002/sia.740151108. [DOI] [Google Scholar]
- 33.Addadi L, Joester D, Nudelman F, Weiner S. Mollusk shell formation: a source of new concepts for understanding biomineralization processes. Chem Eur J. 2006;12(4):980–987. doi: 10.1002/chem.200500980. [DOI] [PubMed] [Google Scholar]
- 34.Epstein E. Silicon: its manifold roles in plants. Ann Appl Biol. 2009;155(2):155–160. doi: 10.1111/j.1744-7348.2009.00343.x. [DOI] [Google Scholar]
- 35.Walker JJ, Spear JR, Pace NR. Geobiology of a microbial endolithic community in the Yellowstone geothermal environment. Nature. 2005;434(7036):1011–1014. doi: 10.1038/nature03447. [DOI] [PubMed] [Google Scholar]
- 36.Konnova SA, Lvov YM, Fakhrullin RF. Nanoshell assembly for magnet-responsive oil-degrading bacteria. Langmuir. 2016;32(47):12552–12558. doi: 10.1021/acs.langmuir.6b01743. [DOI] [PubMed] [Google Scholar]
- 37.Choudhury FK, Rivero RM, Blumwald E, Mittler R. Reactive oxygen species, abiotic stress and stress combination. Plant J. 2017;90(5):856–867. doi: 10.1111/tpj.13299. [DOI] [PubMed] [Google Scholar]
- 38.Gechev TS, Van Breusegem F, Stone JM, Denev I, Laloi C. Reactive oxygen species as signals that modulate plant stress responses and programmed cell death. BioEssays. 2006;28(11):1091–1101. doi: 10.1002/bies.20493. [DOI] [PubMed] [Google Scholar]
- 39.Kawano T. Roles of the reactive oxygen species-generating peroxidase reactions in plant defense and growth induction. Plant Cell Rep. 2003;21(9):829–837. doi: 10.1007/s00299-003-0591-z. [DOI] [PubMed] [Google Scholar]
- 40.Klug B, Specht A, Horst WJ. Aluminium localization in root tips of the aluminium-accumulating plant species buckwheat (Fagopyrum esculentum Moench) J Exp Bot. 2011;62(15):5453–5462. doi: 10.1093/jxb/err222. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Eticha D, Staß A, Horst WJ. Localization of aluminium in the maize root apex: can morin detect cell wall-bound aluminium? J Exp Bot. 2005;56(415):1351–1357. doi: 10.1093/jxb/eri136. [DOI] [PubMed] [Google Scholar]
- 42.Huang CF, Yamaji N, Chen ZC, Ma JF. A tonoplast-localized half-size ABC transporter is required for internal detoxification of aluminum in rice. Plant J. 2012;69(5):857–867. doi: 10.1111/j.1365-313X.2011.04837.x. [DOI] [PubMed] [Google Scholar]
- 43.Mann AK, Varandani D, Mehta BR, Malhotra LK, Shivaprasad SM. Size-induced changes in optical and X-ray photoelectron spectra of GaN nanoparticles deposited at lower substrate temperature. J Nanosci Nanotechnol. 2005;5(11):1858–1863. doi: 10.1166/jnn.2005.424. [DOI] [PubMed] [Google Scholar]
- 44.Wang Y, Stass A, Horst WJ. Apoplastic binding of aluminum is involved in silicon-induced amelioration of aluminum toxicity in maize. Plant Physiol. 2004;136(3):3762–3770. doi: 10.1104/pp.104.045005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.Yin L, Mano J, Wang S, Tsuji W, Tanaka K. The involvement of lipid peroxide-derived aldehydes in aluminum toxicity of tobacco roots. Plant Physiol. 2010;152(3):1406–1417. doi: 10.1104/pp.109.151449. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46.Sharma SS, Dietz K. The relationship between metal toxicity and cellular redox imbalance. Trends Plant Sci. 2009;14(1):43–50. doi: 10.1016/j.tplants.2008.10.007. [DOI] [PubMed] [Google Scholar]
- 47.Su H, Chou C, Hung D, Lin S, Pao I, Lin J, Huang F, Dong R, Lin J. The disruption of bacterial membrane integrity through ROS generation induced by nanohybrids of silver and clay. Biomaterials. 2009;30(30):5979–5987. doi: 10.1016/j.biomaterials.2009.07.030. [DOI] [PubMed] [Google Scholar]
- 48.Yamamoto Y, Kobayashi Y, Devi SR, Rikiishi S, Matsumoto H. Aluminum toxicity is associated with mitochondrial dysfunction and the production of reactive oxygen species in plant cells. Plant Physiol. 2002;128(1):63–72. doi: 10.1104/pp.010417. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49.Baumber J, Ball BA, Gravance CG, Medina V, Davies Morel MC. The effect of reactive oxygen species on equine sperm motility, viability, acrosomal integrity, mitochondrial membrane potential, and membrane lipid peroxidation. J Androl. 2000;21(6):895–902. [PubMed] [Google Scholar]
- 50.Das P, Nutan KK, Singla-Pareek SL, Pareek A. Oxidative environment and redox homeostasis in plants: dissecting out significant contribution of major cellular organelles. Front Environ Sci. 2015;2:70. doi: 10.3389/fenvs.2014.00070. [DOI] [Google Scholar]
- 51.Kapoor D, Sharma R, Handa N, Kaur H, Rattan A, Yadav P, Gautam V, Kaur R, Bhardwaj R. Redox homeostasis in plants under abiotic stress: role of electron carriers, energy metabolism mediators and proteinaceous thiols. Front Environ Sci. 2015;3:13. doi: 10.3389/fenvs.2015.00013. [DOI] [Google Scholar]
- 52.Li Z, Xing D. Mechanistic study of mitochondria-dependent programmed cell death induced by aluminium phytotoxicity using fluorescence techniques. J Exp Bot. 2010;62(1):331–343. doi: 10.1093/jxb/erq279. [DOI] [PubMed] [Google Scholar]
- 53.Dunn JD, Alvarez LA, Zhang X, Soldati T. Reactive oxygen species and mitochondria: a nexus of cellular homeostasis. Redox Biol. 2015;6:472–485. doi: 10.1016/j.redox.2015.09.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54.Koh E, Carmieli R, Mor A, Fluhr R. Singlet oxygen induced membrane disruption and serpin-protease balance in vacuolar driven cell death in Arabidopsis thaliana. Plant Physiol. 2016;171:1616–1625. doi: 10.1104/pp.15.02026. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Mittler R. ROS are good. Trends Plant Sci. 2017;22(1):11–19. doi: 10.1016/j.tplants.2016.08.002. [DOI] [PubMed] [Google Scholar]
- 56.Demidchik V, Sokolik A, Yurin V. The effect of Cu2+ on ion transport systems of the plant cell plasmalemma. Plant Physiol. 1997;114(4):1313–1325. doi: 10.1104/pp.114.4.1313. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Demidchik V. ROS-activated ion channels in plants: biophysical characteristics, physiological functions and molecular nature. Int J Mol Sci. 2018;19(4):1263. doi: 10.3390/ijms19041263. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.Nunes-Nesi A, Brito DS, Inostroza-Blancheteau C, Fernie AR, Araújo WL. The complex role of mitochondrial metabolism in plant aluminum resistance. Trends Plant Sci. 2014;19(6):399–407. doi: 10.1016/j.tplants.2013.12.006. [DOI] [PubMed] [Google Scholar]
- 59.Petrov V, Hille J, Mueller-Roeber B, Gechev TS. ROS-mediated abiotic stress-induced programmed cell death in plants. Front Plant Sci. 2015;6:69. doi: 10.3389/fpls.2015.00069. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Huang S, Van Aken O, Schwarzländer M, Belt K, Millar AH. The roles of mitochondrial reactive oxygen species in cellular signaling and stress response in plants. Plant Physiol. 2016;171(3):1551–1559. doi: 10.1104/pp.16.00166. [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
All data generated or analyzed during this study are included in this published article.