- Open Access
Characterization of physicochemical properties of ivy nanoparticles for cosmetic application
© Huang et al.; licensee BioMed Central Ltd. 2013
- Received: 21 September 2012
- Accepted: 18 January 2013
- Published: 1 February 2013
Naturally occurring nanoparticles isolated from English ivy (Hedera helix) have previously been proposed as an alternative to metallic nanoparticles as sunscreen fillers due to their effective UV extinction property, low toxicity and potential biodegradability.
This study focused on analyzing the physicochemical properties of the ivy nanoparticles, specifically, those parameters which are crucial for use as sunscreen fillers, such as pH, temperature, and UV irradiation. The visual transparency and cytotoxicity of ivy nanoparticles were also investigated comparing them with other metal oxide nanoparticles.
Results from this study demonstrated that, after treatment at 100°C, there was a clear increase in the UV extinction spectra of the ivy nanoparticles caused by the partial decomposition. In addition, the UVA extinction spectra of the ivy nanoparticles gradually reduced slightly with the decrease of pH values in solvents. Prolonged UV irradiation indicated that the influence of UV light on the stability of the ivy nanoparticle was limited and time-independent. Compared to TiO2 and ZnO nanoparticles, ivy nanoparticles showed better visual transparency. Methylthiazol tetrazolium assay demonstrated that ivy nanoparticles exhibited lower cytotoxicity than the other two types of nanoparticles. Results also suggested that protein played an important role in modulating the three-dimensional structure of the ivy nanoparticles.
Based on the results from this study it can be concluded that the ivy nanoparticles are able to maintain their UV protective capability at wide range of temperature and pH values, further demonstrating their potential as an alternative to replace currently available metal oxide nanoparticles in sunscreen applications.
- Ivy nanoparticle
- UV extinction
- Physicochemical property
Titanium dioxide (TiO2) and zinc oxide (ZnO) nanoparticles have been widely used as commercial sunscreen fillers due to their ability to absorb and scatter UV light [1–3]. TiO2 crystals absorb UVB radiation from 280 to 315 nm, while ZnO crystals absorb UVA radiation from 315 to 400 nm; therefore the combined use of both particles provides the UV protection in a broad spectra . Later, silicon (Si) nanoparticles were also proposed to achieve the same purpose . The advantage of using nanoparticles, as opposed to micro-sized particles, is the transparency of nanoparticles to visible light, which is more desirable than the white opaque appearance of micron sized metal oxide particles [1, 6]. Besides, after reducing size to the nano-scale, the performance (UV attenuation) of these particles can be enhanced, which has been verified by both theoretical and experimental studies [7–9]. However, in spite of their ability to efficiently block UV radiation, concerns have been raised about the environmental impact and potential toxicity of these metal oxide nanoparticles [9, 10].
It is well-known that the photocatalytic activity of metal oxide nanoparticles can result in free radical generation, which has been proven to damage DNA or tissues [1, 9, 11]. Although some metal oxide nanoparticles can be modified with non-semiconductor materials to reduce the generation of reactive oxygen species [1, 12], other biosafety concerns, such as uptake and the interaction of nanoparticles with biological tissues still exist . Though significant penetration of nanoparticles contained in sunscreens through the intact epidermal layer of skin has not been observed till now [1, 13], human skin is not an impenetrable barrier. Hair follicles and abrasions provide opportunities for penetration into the vasculature [9, 14]. A previous study indicated that 40 nm nanoparticles could penetrate through follicular openings and enter epidermal cells . The increased use of synthetic nanoparticles has also been reported as a source of environmental contamination that may affect the ecosystem. Studies showed that TiO2 nanoparticles released into the aquatic environment may have long-term toxic effects due to their prolonged stability [16, 17]. Besides, the toxic bioaccumulation caused by the transfer of nanomaterials among species raised more concerns [6, 18]. Although many studies have been carried out to understand the scope and breadth of these potential hazards, a consensus about nanoparticle toxicity has not been reached [19, 20].
Due to the potential hazards associated with the utilizing of metal oxide nanoparticles in sunscreen products, new green nanomaterials which are harmless to both human health and environment while providing similar UV protective effects are highly desirable. Naturally occurring ivy nanoparticles, which are secreted from the adventitious roots of English ivy (Hedera helix) , have been proposed for sunscreen applications [6, 22]. Inherent properties of the natural organic nanoparticles usually endow them with less biosafety or environmental compatibility concerns compared to inorganic counterparts. As one special case of naturally occurring nanostructures , ivy nanoparticles are secreted from the root hairs accompanying with the secretion process of the ivy adhesive , forming a matrix with other components to support the surface climbing [21, 25]. Both experimental and theoretical studies have shown that ivy nanoparticles have excellent transparency to visible light, and a strong ultraviolet extinction potential compared to TiO2 or ZnO nanoparticles . Moreover, previous studies have indicated that ivy nanoparticles could be degraded by proteolytic enzymes, showed low cytotoxicity to mammalian cells, and had a limited possibility of penetrating human skin, all of which make ivy nanoparticles a promising candidate for sunscreen fillers .
However, before practical application of ivy nanoparticles to cosmetic fields, the physicochemical properties of these nanoparticles should be investigated. Nanoparticles behave differently from other micro- or macro-scale materials, due to the larger surface-to-volume ratio, which allows more atoms or molecules to be displayed on the surfaces . The impact of particle size on the properties of materials can be illustrated by the case of TiO2 nanoparticles. TiO2 nanoparticles demonstrate rutile phase while particle size is above ~20 nm, whereas they exist in the form of anatase phase while particle size is below ~20 nm. [10, 26]. Rutile TiO2 nanoparticles are usually used for sunscreen fillers, while anatase nanoparticles have been applied to self-cleaning glasses. The anatase-to-rutile phase transition is not only dependent on the particle size, but also related to other parameters, such as temperature , reaction atmosphere , and synthesis conditions [26, 29]. Besides, the final nanomorphology of TiO2 depends upon the pH value, and hence its properties are sensitive to the resultant chemistry at the surface [26, 30]. Therefore, a detailed understanding of the relationship between the function of nanoparticles and their physicochemical properties must be carried out before related products could be produced and commercialized . Moreover, nanoparticles are also sensitive to the ambient environment. Environmental changes, such as temperature, pressure, or humidity, may alter the performance of nanomaterials . For example, electromagnetic irradiation can permanently alter the shape of colloidal silver nanoparticles, thus affecting the surface plasmon resonances [31, 32]. Due to the high surface-to-volume ratio of nanoparticles, it is challenging to maintain the stable surfaces of these nanomaterials both in device and in storage media. Changes of temperature or pH often influence the surface reactivity or desorb stabilizing surfactants on the surfaces, and hence cause the agglomeration of nanoparticles . As naturally occurring nanoparticles, ivy nanoparticles may offer more complicated composition than synthetic inorganic nanoparticles. Thus, in-depth investigation on their physicochemical properties is necessary before practical applications. This study is not only necessary for the efficient use of ivy nanoparticles in the sunscreen industry but also for eliminating potential biosafety concerns about utilizing ivy nanoparticles.
In this study, the UV extinction properties of ivy nanoparticles were measured and analyzed under various temperatures and pH values. In addition, the influence of prolonged UV radiation on ivy nanoparticles was also investigated. Methylthiazol tetrazolium (MTT) assay was employed to study the cytocompatibility of this naturally occurring nanomaterial. Different from our early study, this research focused on the physicochemical properties analysis of ivy nanoparticles and data from this study provided a comprehensive understanding about the relationship between the UV extinction ability and the properties. Information gained through this study will advance potential applications of the ivy nanoparticles in sunscreen products.
Juvenile shoots of English ivy were generously donated from Swan Valley Farms, Seattle. TiO2 and ZnO nanoparticles (diameter of 50 nm, 99% purity) were purchased from Nanostructured & Amorphous Materials Inc., Houston, TX. Murine melanoma B16BL6 cells, human non-small-cell lung cancer A549 cell lines were preserved by our own lab. Fetal bovine serum (FBS) and Dulbecco's modified Eagle's medium (DMEM) were purchased from Mediatech, Manassas, VA. Bovine serum albumin (BSA) was purchased from Sigma-Aldrich, St. Louis, MO. All other chemicals were purchased from Fisher Scientific, Pittsburgh, PA. All the water used for sample preparation and test was purified by a NANO pure Infinity-unit (Barnstead, Boston, MA).
Ivy adventitious roots (rootlets) cultivation and nanoparticle isolation
Collected juvenile Hedera helix shoots were trimmed to 12 cm in length leaving only one piece of foliage on the head of each shoot fragment. The bottom of the resulting shoots were immersed into water for 24 hours, then incubated in 4.95 mM Indole-3-butyric acid Potassium (K-IBA) solution, and shaken at 100 rpm for 3 hours. After rinsing with water twice, shoots were then placed upright into Magenta GA7 boxes containing 50 ml water and were grown at 24°C at a 16:8 photoperiod under 82 μmol·m-2·s-1 irradiance. Ivy rootlets appeared at 8~10 days and grew to approximately 3 cm in length after one more week cultivation. Adventitious roots were then excised from each ivy shoot carefully to avoid potential physical damage to root hairs. Collected adventitious roots were then used immediately for isolation of ivy nanoparticles. After rinsing with distilled water twice, the wet ivy rootlets (10 g wet weight, from 200 ivy shoots) were extracted twice with 25 ml distilled water at 4°C in a sonicating bath for 1 hour while occasional mixing. The mixture was centrifuged at 12000 rpm for 1 min to remove chunks of debris and the supernatant was filtered through a 0.22 μm filter (Millex®GP, Millipore) to remove impurities. Large agglomerates of ivy nanoparticles were also removed from the resulting decentralized solution. The resulting filtrate was then dialyzed with a 300 kDa cut-off dialysis membrane (Spectra/Por® Biotech) against distilled water for three days with five changes to further purify the ivy nanoparticles and homogenize the size. Most of the small molecules such as soluble proteins, pigments and salts, were removed during dialysis. Isolated ivy nanoparticles were preserved in distilled water at 4°C for further study. Protein concentration of ivy nanoparticles was quantitatively determined by BCA protein assay kit (Thermo, IL).
Influence of temperature variations on ivy nanoparticles
Freshly extracted ivy nanoparticles were diluted 6 times with distilled water to a final concentration of 500 μg/ml. 4 ml of diluted ivy nanoparticles were then treated at 7 different temperatures (-70°C, -20°C, 0°C, 20°C, 30°C, 40°C, 100°C) for two hours. After returning to room temperature (20°C), the size distribution, mean size and zeta potential of differently treated ivy nanoparticles were analyzed using dynamic light scattering (DLS, Zetasizer nano series, Malvern) measurements. The UV extinction spectra of differently treated ivy nanoparticles were measured using a UV-Vis spectrophotometer (Thermo Scientific Evolution 600 UV-Visible spectrophotometer, Thermo Fisher Scientific) from 260 nm to 400 nm. The optical length of the quartz cuvette was 1 cm. Detailed studies on the influence of an extreme temperature (100°C) on ivy nanoparticles were conducted using spectrofluorimetry (LS-50B, Perkin Elmer). Structural changes or unfolding of the ivy nanoparticles was monitored by changes of intrinsic protein fluorescence as described [33, 34]. Emission spectra were recorded in triplicate between 260 and 420 nm using an excitation wavelength of 280 nm. The path length of the microvolume quartz cuvette was 1 cm. Emission spectra of ivy nanoparticles treated at other 6 temperatures (-70°C, -20°C, 0°C, 20°C, 30°C, 40°C) were recorded as the control.
Influence of pH value changes on ivy nanoparticles
Freshly extracted ivy nanoparticles were diluted 6 times with distilled water and acetate buffer (0.1 M, pH 4.0) or phosphate buffer (0.1 M, pH 7.4) to a final concentration of 500 μg/ml. The pH value was adjusted during dilution. The final buffers used in this study were acetate buffer (0.02 M) with 3 different pH values (pH 4.0, pH 5.0 and pH 6.0) and phosphate buffer (0.02 M) with 4 different pH values (pH 7.4, pH 8.0, pH 9.0 and pH 10.0). Ivy nanoparticles dispersed in each buffer were incubated at room temperature for 2 hours followed by DLS measurements. The UV extinction spectra of the ivy nanoparticles at different pH values were measured as described earlier.
Morphological study of ivy nanoparticles
To study the morphology of the ivy nanoparticles and the function of protein on maintaining this nano-morphology, atomic force microscopy (AFM) was performed using an Agilent 6000ILM/AFM (Agilent Technologies, CA). 10 μg of lyophilized ivy nanoparticles were dispersed in 400 μl distilled water and treated with an equal volume of phenol: chloroform: isoamyl alcohol (25: 24: 1, v/v/v). The mixture was stirred for 5 s and centrifuged at 12000 rpm for 10 min at room temperature. The aqueous phase was removed and stored at 4°C prior to analysis. 20 μl of the resulting ivy nanoparticles extract was deposited on a freshly cleaved mica substrate followed by air-drying overnight. Mica substrates were then stored in a desiccator at room temperature prior to AFM analysis. Samples were imaged at room temperature (20°C) using Picoview™ in AC mode. AFM probes were commercially available silicon probes PPP-NCHR-20 (Nanosensors™) with a force constant of 10-130 N/m and resonance frequency of 204-497 kHz. Scan rate was 0.5 ln/s. Un-treated ivy nanoparticles at the same concentration were scanned with the same AFM setting as the control.
Influence of UV radiation on ivy nanoparticles
Freshly isolated ivy nanoparticles were diluted with distilled water 6 times to a final concentration of 500 μg/ml. Diluted samples were added to 12-well tissue culture polystyrene plates (TCPs, Becton Dickinson) at 2 ml/well. TCPs were allowed to air-dry overnight at room temperature. Each well of the TCPs was then covered by one coverslip. Subsequently, TCPs were placed into a biological safety cabinet (BSC, 1300 Series A2, Thermo Scientific) and irradiated with ultraviolet light followed by removing one column of coverslips at a fixed time (0 h, 8 h, 11 h). The UV source was a USHIO G36T5L 39-W/UV-C quartz lamp emitting radiation peaking at 253.7 nm. The distance between the TCPs and the ultraviolet lamp was 75 cm. After 12 h irradiation, ivy nanoparticle precipitates in each well were re-suspended and dispersed with 2 ml of distilled water followed by UV-Vis measurements to record the UV extinction spectra of the ivy nanoparticles under different ultraviolet exposure times. The BSA with the same concentration was treated based on the same procedure as the control.
Visual transparency analysis and MTT assay
Lyophilized ivy nanoparticles were dispersed with distilled water at the concentration of 500 μg/ml, 100 μg/ml and 10 μg/ml. The transparency of dispersed ivy nanoparticles was visually compared to TiO2 and ZnO nanoparticles with the same concentration. MTT assay was also performed to compare the cytotoxicity of ivy nanoparticles with TiO2 and ZnO nanoparticles. A549 and B16BL6 tumor cells were cultured in a DMEM with 10% FBS and an atmosphere of 5% CO2 in air at 37°C. After incubating with serial diluted nanoparticles for 48 hours, MTT assay was conducted and absorbance at 570 nm was recorded.
All quantitative results are representative of three independent experiments. Data were expressed as the mean ± standard deviation (SD). Statistical analysis was performed using one-way ANOVA, performed with a computer statistical program (PASW Statistics 18). A value of P < 0.05 was considered to be statistically significant. Tukey post hoc multiple comparisons were performed to determine differences between every two groups.
Ivy nanoparticle isolation and purification
Subsequently, the influence of temperature on the UV extinction spectra was further evaluated by UV-Vis spectrophotometry. 3 ml aqueous solutions of ivy nanoparticles treated at different temperatures were added to quartz cuvettes, and the absorbance was recorded. Figure 2c shows that the ivy nanoparticles demonstrated strong extinction spectra from 260 to 400 nm (UVA/UVB range), which was consistent with previous reports . However, the UVA/UVB extinction spectra of ivy nanoparticles treated at 100°C displayed a distinct increase compared to other samples. Compared to the results obtained from DLS, this increased absorbance was attributed to the 5.2% small nano-groups (11.61-32 nm) caused by partial decomposition of the ivy nanoparticles after treating at 100°C. The increased surface-to-volume ratio is believed to enhance the UV absorption of this sample.
Stability of ivy nanoparticles to pH
The UV extinction spectra of ivy nanoparticles dispersed in buffers at different pH’s were also recorded using UV-Vis spectrophotometry. As shown in Figure 4c, the UV extinction spectra were measured from 260 to 400 nm. Within the wavelength between 260 and 320 nm (UVB), no distinct spectral difference was observed among different pH values, whereas the UV extinction spectra from 320 to 400 nm (UVA) decreased significantly accompanying with the decrease of pH values. This sub-regional extinction decrease may be attributed to agglomeration of the ivy nanoparticles (Figure 4b). Reduced surface-to-volume ratio may lower the absorption of ultraviolet light. However, the difference between UVA and UVB regions needs to be further investigated. Also, this sub-regional absorbance difference provided a unique channel to utilize ivy nanoparticles in sunscreen products.
UV irradiation influence
Nanoparticles transparency analysis and cytocompatibility
Ivy nanoparticles have been proposed as a potential substitute for metal oxide nanoparticles in sunscreens due to their effective UV extinction potential, low toxicity, and biodegradability . In this study, the stability of the ivy nanoparticles, specifically their UV protective capabilities, to changes in temperature, pH, and prolonged UV exposure were investigated. Results showed that ivy nanoparticles demonstrated relatively strong temperature, pH and UV irradiation tolerance. However, at 100°C, ivy nanoparticles were partially degraded and displayed increased agglomeration, which were modulated by partial protein unfolding. This degradation led to an increase in the UV extinction spectra of ivy nanoparticles. Considering that 100°C falls well outside of the range necessary for a sunscreen product, the stability analysis from -20°C to 40°C shows that the ivy nanoparticles meet the criteria necessary for stable sunscreen filler. Since high temperatures may still be encountered in the process of manufacturing a sunscreen product incorporating the ivy nanoparticles, such as the sterilization of the ivy nanoparticles using autoclaving, this study had certain guiding significance to the practical operation. Results about the influence of pH variation on ivy nanoparticles showed that the UVA extinction spectra slightly decreased with a decrease of pH values. Nanoparticles were more stable in alkaline solutions than in acidic environments. It was also observed that protein played an important role in modulating three-dimensional structures of ivy nanoparticles. The morphology study showed that after removing most protein from ivy nanoparticles, there were still some small residues which displayed irregular and asymmetric structures on the surface of mica. Furthermore, the influence of UV irradiation on the ivy nanoparticles was evaluated by UV-Vis spectroscopy and the results indicated that the impact was small and time-independent. In summary, ivy nanoparticles demonstrate the necessary stability to be used as sunscreen filler, with advantages over currently used metal oxide nanoparticles. The increased visual transparency and safety of these nanoparticles make them an attractive candidate to replace metal oxide nanoparticles, leading to less concern over the environmental impact of these nanomaterials. Future studies will focus on isolation and identification proteins from ivy nanoparticles. The practical application of ivy nanoparticles for UV protection will also be evaluated.
This research is partially sponsored by the Army Research Office (W911NF-10-1-0114) and the National Science Foundation (CMMI: 1029953, CBET: 0965877). The authors are grateful for the support.
- Sadrieh N, Wokovich AM, Gopee NV, Zheng J, Haines D, Parmiter D, Siitonen PH, Cozart CR, Patri AK, McNeil SE: Lack of significant dermal penetration of titanium dioxide from sunscreen formulations containing nano- and submicron-size TiO2 particles. Toxicol Sci. 2010, 115: 156-166. 10.1093/toxsci/kfq041.View ArticleGoogle Scholar
- Dutta M, Basak D: A novel and simple method to grow beaded nanochains of ZnO with superior photocatalytic activity. Nanotechnology. 2009, 20: 475602-10.1088/0957-4484/20/47/475602.View ArticleGoogle Scholar
- Tyner KM, Wokovich AM, Doub WH, Buhse LF, Sung L-P, Watson SS, Sadrieh N: Comparing methods for detecting and characterizing metal oxide nanoparticles in unmodified commercial sunscreens. Nanomed. 2009, 4: 145-159. 10.2217/17435822.214.171.124.View ArticleGoogle Scholar
- Popov AP, Zvyagin AV, Lademann J, Roberts MS, Sanchez W, Priezzhev AV, Myllyl R: Designing inorganic light-protective skin nanotechnology products. J Biomed Nanotechnol. 2010, 6: 432-451. 10.1166/jbn.2010.1144.View ArticleGoogle Scholar
- Rybaltovskii A, Bagratashvili V, Belogorokhov A, Koltashev V, Plotnichenko V, Popov A, Priezzhev A, Sviridova A, Zaĭtseva K, Tutorskii I, Ishchenko A: Spectral features of composite oil-in-water emulsions containing silicon nanoparticles. Opt Spectrosc. 2006, 101: 590-596. 10.1134/S0030400X06100146.View ArticleGoogle Scholar
- Xia L, Lenaghan S, Zhang M, Zhang Z, Li Q: Naturally occurring nanoparticles from English ivy: an alternative to metal-based nanoparticles for UV protection. J Nanobiotechnol. 2010, 8: 12-10.1186/1477-3155-8-12.View ArticleGoogle Scholar
- Popov AP, Lademann J, Priezzhev AV, Myllyla R: Effect of size of TiO2 nanoparticles embedded into stratum corneum on ultraviolet-A and ultraviolet-B sun-blocking properties of the skin. J Biomed Opt. 2005, 10: 064037-10.1117/1.2138017.View ArticleGoogle Scholar
- Tyner KM, Wokovich AM, Godar DE, Doub WH, Sadrieh N: The state of nano-sized titanium dioxide (TiO2) may affect sunscreen performance. Int J Cosmet Sci. 2011, 33: 234-244. 10.1111/j.1468-2494.2010.00622.x.View ArticleGoogle Scholar
- Barnard AS: One-to-one comparison of sunscreen efficacy, aesthetics and potential nanotoxicity. Nat Nano. 2010, 5: 271-274. 10.1038/nnano.2010.25.View ArticleGoogle Scholar
- Barnard AS: Nanohazards: knowledge is our first defence. Nat Mater. 2006, 5: 245-248. 10.1038/nmat1615.View ArticleGoogle Scholar
- Serpone N, Salinaro A, Emeline A: Deleterious effects of sunscreen titanium dioxide nanoparticles on DNA: efforts to limit DNA damage by particle surface modification. Proc SPIE. 2001, 4258: 86-98. 10.1117/12.430765.View ArticleGoogle Scholar
- Nel A, Xia T, Mädler L, Li N: Toxic potential of materials at the nanolevel. Science. 2006, 311: 622-627. 10.1126/science.1114397.View ArticleGoogle Scholar
- Newman MD, Stotland M, Ellis JI: The safety of nanosized particles in titanium dioxide– and zinc oxide–based sunscreens. J Am Acad Dermatol. 2009, 61: 685-692. 10.1016/j.jaad.2009.02.051.View ArticleGoogle Scholar
- Zhang LW, Monteiro-Riviere NA: Assessment of quantum dot penetration into intact, tape-stripped, abraded and flexed rat skin. Skin Pharmacol Physiol. 2008, 21: 166-180. 10.1159/000131080.View ArticleGoogle Scholar
- Vogt A, Combadiere B, Hadam S, Stieler KM, Lademann J, Schaefer H, Autran B, Sterry W, Blume-Peytavi U: 40 nm, but not 750 or 1,500 nm, nanoparticles enter epidermal CD1a+ cells after transcutaneous application on human skin. J Invest Dermatol. 2006, 126: 1316-1322. 10.1038/sj.jid.5700226.View ArticleGoogle Scholar
- Brunner TJ, Wick P, Manser P, Spohn P, Grass RN, Limbach LK, Bruinink A, Stark WJ: In vitro cytotoxicity of oxide nanoparticles: comparison to asbestos, silica, and the effect of particle solubility. Environ Sci Technol. 2006, 40: 4374-4381. 10.1021/es052069i.View ArticleGoogle Scholar
- Kaegi R, Ulrich A, Sinnet B, Vonbank R, Wichser A, Zuleeg S, Simmler H, Brunner S, Vonmont H, Burkhardt M, Boller M: Synthetic TiO2 nanoparticle emission from exterior facades into the aquatic environment. Environ Pollut. 2008, 156: 233-239. 10.1016/j.envpol.2008.08.004.View ArticleGoogle Scholar
- Zhu S, Oberdörster E, Haasch ML: Toxicity of an engineered nanoparticle (fullerene, C60) in two aquatic species, Daphnia and fathead minnow. Mar Environ Res. 2006, 62 (1): S5-S9.View ArticleGoogle Scholar
- McCall MJ: Environmental, health and safety issues: nanoparticles in the real world. Nat Nano. 2011, 6: 613-614. 10.1038/nnano.2011.169.View ArticleGoogle Scholar
- Christian P, Von der Kammer F, Baalousha M, Hofmann T: Nanoparticles: structure, properties, preparation and behaviour in environmental media. Ecotoxicology. 2008, 17: 326-343. 10.1007/s10646-008-0213-1.View ArticleGoogle Scholar
- Zhang M, Liu M, Prest H, Fischer S: Nanoparticles secreted from ivy rootlets for surface climbing. Nano Lett. 2008, 8: 1277-1280. 10.1021/nl0725704.View ArticleGoogle Scholar
- Li Q, Xia L, Zhang Z, Zhang M: Ultraviolet extinction and visible transparency by ivy nanoparticles. Nanoscale Res Lett. 2010, 5: 1487-1491. 10.1007/s11671-010-9666-2.View ArticleGoogle Scholar
- Lenaghan SC, Serpersu K, Xia L, He W, Zhang M: A naturally occurring nanomaterial from the Sundew (Drosera) for tissue engineering. Bioinspir Biomim. 2011, 6: 046009-10.1088/1748-3182/6/4/046009.View ArticleGoogle Scholar
- Lenaghan SC, Zhang M: Real-time observation of the secretion of a nanocomposite adhesive from English ivy (Hedera helix). Plant Sci. 2012, 183: 206-211.View ArticleGoogle Scholar
- Wu Y, Zhao X, Zhang M: Adhesion mechanics of ivy nanoparticles. J Colloid Interface Sci. 2010, 344: 533-540. 10.1016/j.jcis.2009.12.041.View ArticleGoogle Scholar
- Barnard AS, Curtiss LA: Prediction of TiO2 nanoparticle phase and shape transitions controlled by surface chemistry. Nano Lett. 2005, 5: 1261-1266. 10.1021/nl050355m.View ArticleGoogle Scholar
- Kröger N, Dickerson MB, Ahmad G, Cai Y, Haluska MS, Sandhage KH, Poulsen N, Sheppard VC: Bioenabled synthesis of rutile (TiO2) at ambient temperature and neutral pH. Angew Chem Int Ed. 2006, 45: 7239-7243. 10.1002/anie.200601871.View ArticleGoogle Scholar
- Arroyo R, Córdoba G, Padilla J, Lara VH: Influence of manganese ions on the anatase–rutile phase transition of TiO2 prepared by the sol-gel process. Mater Lett. 2002, 54: 397-402. 10.1016/S0167-577X(01)00600-0.View ArticleGoogle Scholar
- Ranade MR, Navrotsky A, Zhang HZ, Banfield JF, Elder SH, Zaban A, Borse PH, Kulkarni SK, Doran GS, Whitfield HJ: Energetics of nanocrystalline TiO2. Proc Natl Acad Sci USA. 2002, 99: 6476-6481. 10.1073/pnas.251534898.View ArticleGoogle Scholar
- Gao Y, Luo H, Mizusugi S, Nagai M: Surfactant-free synthesis of anatase TiO2 nanorods in an aqueous peroxotitanate solution. Cryst Growth Des. 2008, 8: 1804-1807. 10.1021/cg701157j.View ArticleGoogle Scholar
- Jin R, Cao Y, Mirkin CA, Kelly KL, Schatz GC, Zheng JG: Photoinduced conversion of silver nanospheres to nanoprisms. Science. 2001, 294: 1901-1903. 10.1126/science.1066541.View ArticleGoogle Scholar
- Sherry LJ, Chang S-H, Schatz GC, Van Duyne RP, Wiley BJ, Xia Y: Localized surface plasmon resonance spectroscopy of single silver nanocubes. Nano Lett. 2005, 5: 2034-2038. 10.1021/nl0515753.View ArticleGoogle Scholar
- Zhuang P, Blackburn MN, Peterson CB: Characterization of the denaturation and renaturation of human plasma vitronectin. J Biol Chem. 1996, 271: 14323-14332. 10.1074/jbc.271.24.14323.View ArticleGoogle Scholar
- Zhuang P, Chen AI, Peterson CB: Native and multimeric vitronectin exhibit similar affinity for heparin. J Biol Chem. 1997, 272: 6858-6867. 10.1074/jbc.272.11.6858.View ArticleGoogle Scholar
- Murdock RC, Braydich-Stolle L, Schrand AM, Schlager JJ, Hussain SM: Characterization of nanomaterial dispersion in solution prior to in vitro exposure using dynamic light scattering technique. Toxicol Sci. 2008, 101: 239-253. 10.1093/toxsci/kfm240.View ArticleGoogle Scholar
- Powers KW, Brown SC, Krishna VB, Wasdo SC, Moudgil BM, Roberts SM: Research strategies for safety evaluation of nanomaterials. Part VI. Characterization of nanoscale particles for toxicological evaluation. Toxicol Sci. 2006, 90: 296-303.View ArticleGoogle Scholar
- Busti P, Scarpeci S, Gatti C, Delorenzi N: Use of fluorescence methods to monitor unfolding transitions in β-lactoglobulin. Food Res Int. 2002, 35: 871-877. 10.1016/S0963-9969(02)00096-0.View ArticleGoogle Scholar
- Sahihi M, Ghayeb Y, Bordbar A-K: Fluorescence spectroscopic study on interaction of retinol with β-lactoglobulin in the presence of cetylpyridinium chloride. Spectroscopy: An International Journal. 2012, 27: 27-34. 10.1155/2012/856098.View ArticleGoogle Scholar
- Uversky VN: Natively unfolded proteins: a point where biology waits for physics. Protein Sci. 2002, 11: 739-756. 10.1110/ps.4210102.View ArticleGoogle Scholar
- Kim TY, Lee Y-H, Park K-H, Kim SJ, Cho SY: A study of photocatalysis of TiO2 coated onto chitosan beads and activated carbon. Res Chem Intermed. 2005, 31: 343-358. 10.1163/1568567053956581.View ArticleGoogle Scholar
- Xing JY, Bai B, Chen ZH: Effect of UV irradiation on stabilization of collagen. Water Resour Environ Prot. 2011, 4: 2979-2982.Google Scholar
- Jariashvili K, Madhan B, Brodsky B, Kuchava A, Namicheishvili L, Metreveli N: UV damage of collagen: insights from model collagen peptides. Biopolymers. 2012, 97: 189-198. 10.1002/bip.21725.View ArticleGoogle Scholar
- Takahashi T, Kondo T, Tanaka K, Hattori S, Irie S, Kudoh S, Imura S, Kanda H: Measurement of solar UV radiation in antarctica with collagen sheets. Photochem Photobiol Sci. 2012Google Scholar
- Edwards SL, Charlie NK, Milfort MC, Brown BS, Gravlin CN, Knecht JE, Miller KG: A novel molecular solution for ultraviolet light detection in Caenorhabditis elegans. PLoS Biol. 2008, 6: e198-10.1371/journal.pbio.0060198.View ArticleGoogle Scholar
- Slieman TA, Nicholson WL: Role of dipicolinic acid in survival of Bacillus subtilis spores exposed to artificial and solar UV radiation. Appl Environ Microbiol. 2001, 67: 1274-1279. 10.1128/AEM.67.3.1274-1279.2001.View ArticleGoogle Scholar
- Küpfer PA, Leumann CJ: Synthesis, base pairing properties and trans-lesion synthesis by reverse transcriptases of oligoribonucleotides containing the oxidatively damaged base 5-hydroxycytidine. Nucleic Acids Res. 2011, 39: 9422-9432. 10.1093/nar/gkr673.View ArticleGoogle Scholar
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