Introduction

Over the past several years research on developing efficient methods for the large-scale synthesis of gold nanoparticles (Au NPs) are being intensely pursued. Wide variety of synthetic strategies, including both physical and chemical methods, have been employed to synthesize gold nanoparticles with controllable size, shape, and size distribution [110]. Synthesis of gold nanoparticles by physical methods requires sophisticated equipments and is thus quite expensive. Gold nanoparticles synthesized by chemical methods often require toxic reducing and stabilizing agents. These toxic substances adsorbed on the surfaces of the gold nanoparticles limit its applications in biomedical fields. Therefore, there is an overwhelming need to develop environmentally benign processes for the synthesis of gold nanoparticles without using any toxic chemicals. Biosynthesis of gold nanoparticles thus became an eco-friendly alternative to the currently available physical and chemical methods. Gold nanoparticles have amazing importance due to their unique optical and electronic properties and find applications in optoelectronic devices, drug delivery, biosensing and catalysis [1114]. Besides, surface funtionalized gold nanoparticles are also known to show excellent antioxidant and antibacterial properties [15, 16]. Biomaterials like bacteria, fungi, different plant parts, and algae have been considered as eco-friendly nano-factories [1721]. Proteins, peptides, and natural biotemplates like eggshell membrane have been efficiently used for the synthesis of fluorescent gold nanoparticles [2224]. Recently, poly-cytosine DNA and poly-adenine DNA were utilized as protecting agents for the preparation of blue emitting gold nanoparticles [25]. Proteins were considered as green templates in the synthesis of fluorescent gold nanoparticles. Xie et al. [26] fabricated fluorescent gold nanoparticles using bovine serum albumin as both capping and reducing agents. An insulin-directed synthesis of red emissive gold nanoparticles is documented where the bioactivity and biocompatibility of insulin were retained [27]. Algae mediated synthesis of fluorescent gold nanoparticles did not appear to have been reported earlier. Recently, protein capped silver and gold nanoparticles synthesized using Escherichia coli were found to show potent antibacterial and antioxidant properties [28]. Silver and gold nanoparticles were accessed using aqueous extract of Solanum torvum fruit and their antibacterial and antioxidant properties have also been documented [29]. Comprehensive review on the biosynthesis of nanoparticles by various marine organisms has appeared recently [30]. Algae are the naturally occurring plant organisms that are the important source of phytochemicals responsible for the production of metal nanoparticles. Cyanobacteria and green algae have recently been demonstrated to yield gold nanoparticles [31]. Biosynthesis of gold nanoparticles using brown seaweed, Sargassum wightii is on record [32]. Another brown seaweed, Fucus vesiculosus was found to be capable of gold(III) biosorption and bioreduction [33]. Seaweeds apart, microalgae such as diatoms (Navicula atomus, Diadesmis gallica) are also known to afford gold nanoparticles, and gold–silica nanocomposites [34]. As a part of our ongoing studies on algal diversity of Manipur, a remotely located north-eastern state of India, we came across a rare freshwater edible red alga, L. fluviatilis [35]. Use of the red alga, L. fluviatilis, in the biosynthesis of noble metal nanoparticles did not appear to have been accomplished earlier. Gold ashes are traditionally known to be used as therapeutic agents in the Indian Ayurveda medicine to combat many clinical disorders [3638]. Accordingly, we report herein the biosynthesis of highly stable, fluorescent gold nanoparticles using the freshwater red alga, L. fluviatilis and antioxidant activity of the biomatrix loaded nanoparticles.

Experimental

Materials and physical measurements

The red alga, L. fluviatilis was collected from the Thoubal district (93°45′–94°15′ East longitude and 23°43′–24°45′ North latitude) of the state of Manipur, North East India. The alga grows luxuriantly during winter (November to January) in the rocks and boulders of river Chakpi situated at an elevation of ~790 m from sea level. The specimen was brought to the laboratory cleaned thoroughly by fresh water followed by distilled water and then shade dried for a week. The algal morphology was examined under an optical microscope and using standard keys the specimen was identified to be L. fluviatilis [39]. The herbarium is deposited in the department of Ecology and Environmental Sciences, Assam University, Silchar, India. The dried thalli were ground to powder in a glass mortar. Chloroauric acid was purchased from Sigma-Aldrich. Double distilled water was used throughout the experiment. Absorption spectrum was taken on a Shimadzu 1601 PC UV–visible scanning spectrophotometer. X-ray diffraction (XRD) measurement was carried out on a Bruker AXS D8-Advance powder X-ray diffractometer with Cu–Kα radiation (λ = 1.5418 Å) with a scan speed of 2°/min. Transmission electron microscopy (TEM) images were obtained on a JEOL, JEM2100 equipment. TEM grids were prepared using a few drops of the nanoparticles followed by drying. The particle size distribution was determined by dynamic light scattering (DLS) technique using a particle size analyser (Delsa Nano S, Beckman Coulter, USA). FT-IR spectrum was recorded on a Shimadzu Varian 4300 spectrometer on KBr pellets. Photoluminescence (PL) spectrum was recorded on a Shimadzu RF-5301 PC spectrofluorophotometer.

Biosynthesis of gold nanoparticles

1 g of dry algal powder was added to 100 ml (10−3 M) aqueous solution of chloroauric acid and was stirred at room temperature for 12 h. The progress of the reaction was routinely monitored by observing color change as well as recording UV–visible spectrum. The initial light yellow color of chloroauric acid solution turned to red indicating formation of colloidal gold. The supernatant containing gold nanoparticles were collected by centrifugation at 10,000 rpm and used for further characterization. The purple colored biomass loaded with gold nanoparticles obtained after centrifugation was washed repeatedly with double distilled water to remove any unreacted chloroauric acid and dried.

Assessment of antioxidant activity

The antioxidant activity of the gold nanoparticles loaded within the biomatrix was assessed using a modified DPPH method [40]. At first 20 mg of the powdered sample was taken in a test tube and to it 3 mL of 100 µM methanolic solution of DPPH was added. To enhance the surface reaction between the sample and the DPPH reagent, the mixture was further sonicated and kept in the dark. After centrifugation at 10,000 rpm, the supernatant was collected and absorbance was measured at 515 nm. Methanol was kept as blank. A DPPH control was also measured as reference. The aforementioned procedure was followed to examine the time-dependent DPPH scavenging at an interval of 5, 15, 30, 45 and 60 min. The percentage scavenging was calculated using the formula

$${\text{DPPH scavenging }}\left( \% \right) \, = \, \left[ {\left( {A_{\text{c}} {-}A_{\text{s}} } \right)/A_{\text{c}} } \right] \times 100,$$

where A C and A S are absorbances of the control DPPH and DPPH with the biomatrix loaded gold nanoparticles at 515 nm, respectively. For evaluating SC50 (the amount of samples required to scavenge 50 % of DPPH) a similar procedure is adopted with 10, 20, 30, 50, 70, and 100 mg of the samples and absorbances were recorded after 30 min in each case.

Results and discussion

Gold nanoparticles were accessed via bioreduction of aqueous chloroauric acid solution with the dried biomass of an edible freshwater red alga, L. fluviatilis. The protein molecules present in the alga served both as reductant and stabilizer. The as-synthesized nanoparticles were characterized by UV–visible, XRD, TEM, DLS, and FT-IR studies. Gold nanoparticles show surface plasmon resonance (SPR) at around 510–560 nm [41]. Fig. 1 shows the UV–visible spectra of the aqueous chloroauric acid-L. fluviatilis reaction medium as a function of reaction time. Gold nanoparticles synthesized in the present study showed SPR at around 530 nm with a gradual increase in intensity of absorption with reaction time. The bioreduction of the aqueous chloroaurate ions was completed in 12 h. The inset of Fig. 1 shows the change in solution color (light yellow to red). The synthesized nanoparticles being capped with biomolecules are fairly stable (up to 3 months) as indicated by retention of red color of the solution and lack of any significant change in SPR band position.

Fig. 1
figure 1

UV–visible spectra of the aqueous chloroauric acid–L. fluviatilis reaction medium as a function of reaction time. (A) Aqueous chloroauric acid solution, (B) colloidal gold solution

The XRD pattern (Fig. 2) of the purple colored biomass showed five diffraction peaks at 2θ = 38.47°, 44.57°, 64.73°, 77.68°, and 81.75° which corresponds to (111), (200), (220), (311), and (222) planes of the face-centered cubic gold (space group Fm3m, JCPDS File No.89-3697). No peaks attributable to impurities were observed. The broad diffraction peaks clearly suggested reduced crystallite size. The average crystallite size of the gold nanoparticles estimated by the Debye–Scherrer formula, using a Gaussian fit was found to be 5.9 nm.

Fig. 2
figure 2

XRD pattern of gold nanoparticles

The TEM image (Fig. 3) showed that the synthesized gold nanoparticles were polydispersed. The particles were nearly spherical in shape with sizes in the range of 5–15 nm. The low magnification TEM image also revealed that the nanoparticles have a strong tendency to assemble together to form chain-like structure. The HRTEM image showed the lattice fringes between the two adjacent planes to be 0.231 nm apart which corresponds to the interplanar separation of the (111) plane of face-centered cubic gold. The electron diffraction (ED) pattern indicated polycrystalline nature of the synthesized material.

Fig. 3
figure 3

a, b TEM images, c HRTEM image, and d ED pattern of gold nanoparticles

The differential intensity related to particle size distributions of the as-synthesized gold nanoparticles was obtained from DLS study (Fig. 4a). The average particle diameter was found to be 47.6 ± 61.3 nm. The cumulative mean diameter was found to be 35.8 nm. The larger particle size and more polydispersity observed by DLS as compared to TEM are due to the fact that the measured size also included the biomaterials covering the surface of gold nanoparticles. FT-IR spectrum was recorded to discern the possible biomolecules responsible for effective capping and stabilization of the gold nanoparticles. The FT-IR spectrum of the dried gold loaded purple colored biomass (Fig. 4b) showed bands at 3,314 and 1,158 cm−1 due to N–H and C–N stretching vibrations of primary amines, respectively [42]. The band at 2,944 cm−1 arose due to C–H stretching, those at 1,670 and 1,453 cm−1 corresponds to the amide I of the polypeptides and symmetric stretching of the carboxylate groups in the amino acid residues of the protein molecules [43]. This gives a clear indication of the presence of proteins and other organic molecules in the material which might have been produced by L. fluviatilis extracellularly.

Fig. 4
figure 4

a Particle size distributions obtained from DLS study and b FT-IR spectrum of gold nanoparticles

Gold nanoparticles have been reported to exhibit photoluminescence in the wavelength 500–590 nm and 410–430 nm [44, 45]. The emissions in the range 500–590 nm occur due to the electronic transitions between the sp band just below the Fermi level and the first d band and those in the range 410–430 nm due to the recombination of electrons with holes in the lower energy band. The photoluminescence spectrum (Fig. 5) of the gold nanoparticles excited at 300 nm showed blue emission at around 440 nm. The blue emission has been observed earlier in case of nanosize gold clusters [46]. The presence of Au8 magic cluster has been found responsible for blue emission from gold nanodots [47, 48]. Blue emission at 411 nm has also been observed earlier for proteins/biotins functionalized gold nanoparticles [49]. Our present study clearly reveals that bioreduction of aqueous chloroaurate ions with the red alga, L. fluviatilis could in fact produce fluorescent gold nanoparticles.

Fig. 5
figure 5

Photoluminescence spectrum of gold nanoparticles

The DPPH is a stable and well-known free radical for evaluating antioxidant potency of compounds. It is reduced by accepting the hydrogen or electron. The DPPH reducing ability of the biomatrix loaded gold nanoparticles was assessed spectrophotometrically by observing color change from purple to yellow. The control DPPH does not show any change of absorbance with time. However, DPPH with biomatrix loaded gold nanoparticles showed a steady decrease of absorbance at 515 nm with time (Fig. 6a). The DPPH scavenging (%) can be calculated from the decrease of absorbance at 515 nm, which corresponds to the quantity of DPPH in the methanolic solution. The DPPH scavenging (%) values for different weights of the sample were thus determined (vide experimental). The SC50 value, ascertained graphically from the plot of DPPH scavenging (%) vs. different weights of the sample (Fig. 6b) was found to be 18.10 mg. The observed antioxidant activity is attributed to the neutralization of free radical character of DPPH by the transfer of an electron [50]. Liu and co-worker [51] first observed enhanced DPPH radical scavenging activity by the gold nanoparticles coated with trolox, a vitamin E analogue. Very recently, their group put forward the possible mechanism and performed cellular kinetic studies on the enhancement of antioxidant activity by employing surface functionalization of gold nanoparticles with the antioxidant salvianic acid A [52]. Enhancement of antioxidant activity of gold nanoparticle embedded 3,6-dihydroxyflavone has also been reported recently [53]. The strategy described here resulted in biomatrix loaded gold nanoparticles having good antioxidant activity without any additional surface functionalizations.

Fig. 6
figure 6

a Time-dependent DPPH scavenging by biomatrix loaded gold nanoparticles and b DPPH scavenging (%) at different weights of biomatrix loaded gold nanoparticles

Conclusion

Fluorescent gold nanoparticles have been successfully synthesized using the dried biomass of an edible freshwater red alga, L. fluviatilis following a green procedure. The methodology adopted herein is simple, low-cost, and non-toxic. The protein molecules present in the alga served a twofold role as reducing and stabilizing agent. No external reducing agent or surfactants were needed for the synthesis of gold nanoparticles. The biomatrix loaded gold nanoparticles has been demonstrated to be a potent antioxidant. The use of red alga, L. fluviatilis for the fabrication of gold nanoparticles, indicated its potential in future production of other valuable nanostructures in the emerging field of nanobiotechnology. Owing to the inherent ability of antioxidants to elicit free radical scavenging activity, their formulation as nanomaterials might enhance their efficiency. Utilization of biomatrix loaded gold nanoparticles in antioxidant activity study might prove to be a suitable alternative to traditional methods, where separation of nanoparticles from a biological system is cumbersome.