Ecobiophysical Aspects on Nanosilver Biogenerated from<i> Citrus reticulata</i> Peels, as Potential Biopesticide for Controlling Pathogens and Wetland Plants in Aquatic Media

Barbinta-Patrascu, Marcela Elisabeta; Badea, Nicoleta; Ungureanu, Camelia; Iordache, Stefan Marian; Constantin, Marioara; Purcar, Violeta; Rau, Ileana; Pirvu, Cristian

doi:https://doi.org/10.1155/2017/4214017

Journal of Nanomaterials

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Abstract Introduction Materials and Methods Results and Discussion Conclusions Conflicts of Interest Acknowledgments References Copyright Related Articles

Research Article | Open Access

Volume 2017 | Article ID 4214017 | https://doi.org/10.1155/2017/4214017

Ecobiophysical Aspects on Nanosilver Biogenerated from Citrus reticulata Peels, as Potential Biopesticide for Controlling Pathogens and Wetland Plants in Aquatic Media

Marcela Elisabeta Barbinta-Patrascu,¹Nicoleta Badea,²Camelia Ungureanu,²Stefan Marian Iordache,³Marioara Constantin,¹Violeta Purcar,⁴Ileana Rau,²and Cristian Pirvu²

Academic Editor: R. Torrecillas

Received02 Feb 2017

Revised03 Apr 2017

Accepted20 Apr 2017

Published29 Jun 2017

Abstract

In recent years, a considerable interest was paid to ecological strategies in management of plant diseases and plant growth. Metallic nanoparticles (MNPs) gained considerable interest as alternative to pesticides due to their interesting properties. Green synthesis of MNPs using plant extracts is very advantageous taking into account the fact that plants are easily available and eco-friendly and possess many phytocompounds that help in bioreduction of metal ions. In this research work, we phytosynthesized AgNPs from aqueous extract of Citrus reticulata peels, with high antioxidant, antibacterial, and antifungal potential. These “green” AgNPs were characterized by modern biophysical methods (absorption and FTIR spectroscopy, AFM, and zeta potential measurements). The nanobioimpact of Citrus-based AgNPs on four invasive wetland plants, Cattail (Typha latifolia), Flowering-rush (Butomus umbellatus), Duckweed (Lemna minor), and Water-pepper (Polygonum hydropiper), was studied by absorption spectroscopy, by monitoring the spectral signature of chlorophyll. The invasive plants exhibited different behavior under AgNP stress. Deep insights were obtained from experiments conducted on biomimetic membranes marked with chlorophyll a. Our results pointed out the potential use of Citrus-based AgNPs as alternative in controlling pathogens in aqueous media and in management of aquatic weeds growth.

1. Introduction

Since its invention in 1959 [1], nanotechnology became the most fascinating area of science. Nowadays, the progress in nanotechnology opened new perspectives of metal nanoparticles (MNPs) applications in agriculture, in plant diseases or plant growth management [2, 3]. Among MNPs, silver nanoparticles (AgNPs) gained great popularity in various applications: biomedical, antimicrobial, antioxidant, antifungal, insecticidal, agriculture, and cosmetics industries [2, 4–11].

In last years, plant extracts were the most used resources in various fields: cosmetics [12], agriculture, and medicine [13], as environmentally benign inhibitor toward corrosion of carbon steel in acid media [14] or as precursor for biosynthesis of silver nanoparticles [8, 15–18].

The increasing interest in plants is due to their high abundance in nature, recyclability, and their content rich in bioactive principles. Contrary to chemical synthesis of AgNPs, which used toxic agents, the “green” synthesis of nanosilver using plant extracts is preferred today because it uses eco-friendly chemicals and raw materials.

Our work aimed to study the application of phytosynthesized AgNPs using an aqueous extract of Citrus reticulata (tangerine or mandarin) peels in management of water pond quality and control of invasive aquatic weeds.

In order to get deep insights about the action of AgNPs, the tests were firstly conducted in vitro, on mimicking photosynthetic membranes (artificial lipid bilayers loaded with chlorophyll a).

The studies were further performed on four common Romanian wetland plants: Cattail (Typha latifolia), Flowering-rush (Butomus umbellatus), Duckweed (Lemna minor), and Water-pepper (Polygonum hydropiper). They are invasive plants that rapidly reproduce and invade habitats, displacing many native species. Although these plants give a beautiful landscape and constitute a nutritional source for waterfowl or other birds and also provide protection for different aquatic creatures, they can become harmful in certain situations, when invading irrigation systems, fish lakes, or swimming pools, with dramatic consequences on economy (disrupting hydropower generation; impairment of commercial and recreational navigation; interfering with safe swimming and with fishing; endangering human health and increasing drowning risk; impairing drinking water, etc.) and ecology (suppression of desirable native plants; reducing species diversity; water quality degradation; alteration of animal community interactions; fish killing, etc.) [20]. Uncontrolled growth of these invasive species can be stopped with pesticides, but these chemicals could be harmful for human health and the environment, too. So, novel methods, safer and environmental benign, must be imposed to overcome these problems. Thus, AgNPs biogenerated from C. reticulata peels extract (Citrus-nAg) were tested for application in controlling phytopathogens and invasive plants in aquatic media. Citrus-nAg were firstly characterized by spectral methods (absorption and FTIR spectroscopy), and morphological aspects were obtained from AFM investigations. The stability of Citrus-nAg was checked by zeta potential measurements. Further investigations on bioactivities of Citrus-nAg demonstrated their antioxidant, antibacterial, and antifungal properties. The bioimpact on the tested wetland plants was assayed by treating these herbs with increasing concentrations of Citrus-nAg and monitoring the spectral signature of chlorophyll (Chl).

2. Materials and Methods

2.1. Materials

Soybean lecithin (Calbiochem), KH₂PO₄, Na₂HPO₄, peptone, HCl, H₂O₂, luminol (5-amino-2,3-dihydrophthalazine-1,4-dione), and Tris (hydroxymethyl aminomethane base) were purchased from Merck (Germany). Silver nitrate (AgNO₃) was supplied by Gatt Koller-GmbH, Austria. NaCl, 69% HNO₃, and 37% HCl were purchased from Sigma-Aldrich (Germany). The yeast extract was obtained from Biolife and the agar from Fluka.

Chlorophyll a (Chla) was obtained in our laboratory from fresh spinach (Spinacia oleracea L.) leaves by a chromatographic method as previously described [21, 22], and the purity of this phytopigment was checked by Vis absorption spectra.

2.2. Sample Preparation

2.2.1. Preparation of Citrus reticulata Peels’ Extract

Fresh tangerine peels thoroughly washed with distilled water and dried with filter paper were cut into small pieces and then mixed with distilled water in a final mass ratio Citrus peels/distilled water of 1 : 3 (w/w). The as-prepared mixture was boiled for 5 minutes. After cooling at room temperature and in dark, it was filtered with Whatman filter paper number 1 and then kept in freezer.

2.2.2. Biosynthesis of AgNPs from Citrus reticulata Peels’ Extract (Citrus-nAg)

An amount of 34 mg AgNO₃ was added to 50 mL aqueous extract under continuously stirring at room temperature. The biosynthesis of nanosilver from C. reticulata peels’ extract (named Citrus-nAg) was visually observed via color change of this mixture. Tangerine peel extract, which is eco-friendly, acted as both a reducing and a stabilizing agent.

2.2.3. Preparation of Biomimetic Membranes Marked with Chla

Small unilamellar vesicles (SUVs) labeled with Chla were prepared according to [23, 24], by hydrating a soybean lecithin/Chla (100 : 1, molar ratio) thin film with phosphate buffer (PB, KH₂PO₄-Na₂HPO₄ pH 7.4), followed by mechanical stirring (VIBRAX stirrer-OHIO 43230, USA, 200 rpm, 40 min), and then subjected to ultrasound treatment (Hielscher Ti probe sonicator, UP 100 H-Hielscher Ultrasonics GmbH, 14513 Teltow, Germany).

2.3. Characterization Methods

The absorption spectra were recorded in the 200–800 nm wavelength range on a double beam Lambda 2S Perkin Elmer UV-Vis spectrophotometer, operated at a resolution of 1 nm.

The fluorescence emission spectra of Chla in biomimetic membranes were collected in the wavelength range of 600–800 nm, on a LS55 Perkin Elmer fluorescence spectrometer, by illuminating the samples with 430 nm excitation wavelength.

FTIR spectra of samples were obtained using a Fourier Transform Infrared Spectrophotometer (Tensor 37 from Bruker). For all of the scans, the spectra were collected in the wavenumber range of 400–4000 cm⁻¹, at a spectral resolution of 4 cm⁻¹.

The silver content in the AgNP suspension was determined by atomic absorption spectroscopy, AAS (ContrAA 700, Analytik Jena, Germany), after microwave assisted acid digestion (Milestone, SUA). In order to quantify the silver ion concentration released in time, the AgNP stock suspension was subjected to centrifugation (21000 ×g for 30 minutes, at 0°C, SIGMA 2–16K centrifuge) at different periods. All measurements were performed in triplicate. Prior to AAS analysis, approximately 0.5 g of each sample was completely digested using a mixture of 69% HNO₃, 37% HCl, and 30% H₂O₂.

The morphology of silver nanoparticles was analyzed using an APE Research A100-SGS (Italy) atomic force microscope (AFM), working in contact mode system. Gwyddion software was used to process AFM images.

Zeta potential (ZP) measurement was carried out in an appropriate device of Zetasizer Nano ZS (Malvern Instruments Ltd., UK), by applying an electric field across the analyzed aqueous suspension.

The in vitro antioxidant activity (AA%) of Citrus-nAg was assayed through chemiluminescence method on a Chemiluminometer Turner Design TD 20/20 (USA), by using the system containing: luminol (1 mM), Tris-HCl buffer solution (pH 8.6), and H₂O₂ (10 μM), as free radical generator. The value of AA% was expressed aswhere is the maximum CL intensity at s, for the reaction mixture without the sample, and is the maximum CL intensity for each sample, at s [25].

For determination of Minimum Inhibitory Concentration (MIC value recorded is defined as the lowest concentration of the assayed antimicrobial agent that inhibits the visible growth of the microorganism tested, and it is usually expressed in μg/mL) of Citrus-nAg against the tested microbial strains, each of the tested microorganisms was determined by the broth dilution technique [26]. Serially diluted logarithmic concentrations of the Citrus-nAg ranging from 400 μg/mL to 0.195 μg/mL were inoculated with standardized overnight cultures of the microorganisms and incubated at 37°C. Dilution methods are the most appropriate ones for the determination of MIC values, since they offer the possibility of estimating the concentration of the tested antimicrobial agent in the broth medium [27]. The most recognized standards are provided by the CLSI and the European Committee on Antimicrobial Susceptibility Testing (EUCAST) [28]. The MIC assay was performed in triplicate.

In order to evaluate the antibacterial activity, the Citrus-nAg were tested against pathogenic Escherichia coli ATCC 8738 microbial strain. The bacterial strains were grown in Luria Bertani Agar (LBA) plates at 37°C with following composition: peptone (10 g/L); yeast extract (5 g/L), NaCl (5 g/L); and agar (20 g/L). The stock culture was maintained at 4°C.

Antifungal activity of Citrus-nAg was tested against the fungal aquatic pathogen Fusarium oxysporum ATCC 48112. The stock culture was maintained at 4°C. These strains were cultivated onto potato-dextrose agar (abbreviated “PDA”) from Sigma-Aldrich Company with next composition: potato extract (4 g/L), dextrose (20 g/L), and agar (15 g/L).

Time-kill test is the most appropriate method for determining the bactericidal or fungicidal effect. The time-kill test reveals a time-dependent or a concentration-dependent antimicrobial effect [28, 29]. For bacteria, this test has been well standardized and described in M26-A document of CLSI [30]. Similarly, several antifungal substances were studied by this method [31, 32].

Time-kill test for determining the bactericidal effect was performed in broth culture medium using three tubes containing a bacterial suspension of CFU/mL (colony-forming units/mL). The first and the second tubes contain the extract tested usually at final concentrations of 0.25 MIC and 1 MIC, and the third one is considered as the growth control. 1 mL of each tube was placed onto Bacto-Agar plates. The incubation was done under suitable conditions for 24 h at 37°C to determine the number of viable E. coli in terms of CFU. Then, the percentage of dead cells was calculated relatively to the growth control by determining the number of living cells (CFU/mL) of each tube using the agar plate count method [33].

Time-Kill Test for Determining the Fungicidal Effect. The agar dilution method involves the incorporation of varying desired concentrations (1 MIC and 0.25 MIC) of the Citrus-nAg into an agar medium, followed by the inoculation of a Fusarium oxysporum inoculum onto the agar plate surface. The plates were incubated for 4-5 days at 37°C to see the fungicidal effect [34].

Standard deviation was calculated as the square root of variance using STDEV function in Excel 2010.

3. Results and Discussion

3.1. Characterization of Silver Nanoparticles Biosynthesized from Tangerine Peel Extract

The biosynthesis of silver nanoparticles from aqueous extract of C. reticulata peels was firstly monitored by visual inspection. Thus, after addition of silver ions, the color of tangerine extract turned from orange to dark brown (Figure 1).

The green synthesis of AgNPs was further confirmed by spectral characterization (Figure 2) and AFM analysis (Figure 3). The absorption spectra (Figure 2(a)) showed that, after adding silver nitrate to vegetal extract, a SPR band appeared at 443 nm, which is characteristic for spherical/quasi-spherical silver nanoparticles [8, 35].

(a)

(b)

(a)

(b)

The FTIR transmission spectrum (Figure 2(b)) of aqueous C. reticulata extract showed presence of IR bands at 3850, 3740, and 3321 cm⁻¹ (characteristic of O–H stretching of hydroxyls), 2355 and 2112 cm⁻¹ (N–H stretching vibrations), 1740 cm⁻¹ (C=O cm⁻¹ stretching attributed to aldehyde, ketones, carboxylic acid, or pectin ester), 1639 cm⁻¹ (attributed to amide I; pectin), 1368 cm⁻¹ (C–CH3 bending), 1218 cm⁻¹ (C–O stretch acidic or (C–O–C) of geranyl acetate (acyclic monoterpene)), 1110 cm⁻¹ ((CO), (CC) ring of polysaccharides, and pectin), 1082 cm⁻¹ and 1068 cm⁻¹ (may be due to alcohol, carboxylic acid and esters), and 641 cm⁻¹ (assigned to bending modes of aromatic compounds) [11, 15, 36–38].

After bioreduction of silver ions, the following events were observed:(1)The FTIR bands at 3850, 3740, 1740, and 1639 cm⁻¹ were shifted to 3857, 3743, 1747, and 1633 cm⁻¹, respectively, becoming strong and sharps (3857 and 3743 cm⁻¹) and weaker (1747 and 1633 cm⁻¹).(2)The peaks at 3857 and 3743 are more strong and sharp, while that at 1633 cm⁻¹ weakened.(3)The band at 1068 cm⁻¹ shifted to 1060 cm⁻¹ and became stronger in AgNP spectrum.(4)New peak was observed in the FTIR spectrum of Citrus-nAg: 2927 cm⁻¹ (alkyls C–H stretching) [39].

On the other hand, both Citrus extract and AgNPs presented broad strong FTIR peaks at 3321 and 3384 cm⁻¹, respectively, suggesting the presence of stretch hydrogen bonding. It could be observed from the FTIR spectra of Citrus reticulata peels extract and of Citrus-nAg that hydroxyl and carboxyl groups are predominant.

Our IR results confirmed that phytomolecules like pectin, polyphenols, and proteins played an important role in the bioreduction of silver ions, these biomolecules acting as both reducing and capping agents for silver nanoparticles.

The physical stability of AgNPs was evaluated in terms of zeta potential measurements, via their electrophoretic mobility in an electric field [40]. The obtained ZP value showed that the “green” synthesized AgNPs are quite stable ( mV), their physical stability being achieved through interparticle repulsion forces, due to the presence onto their surface, of the carboxyl groups arising from Citrus reticulata peels extract (see Figure 2(b)).

Few drops of Citrus-nAg suspension were deposited on a silica glass plate and allowed to dry at room temperature in the dark, and then the resulting thin film was analyzed by AFM. Figure 3 illustrates the morphological aspects in three-dimensional AFM image (a) and line profile (b) of Citrus-nAg. As observed, spherical silver nanoparticles with nanoscaled dimension (mean diameter < 135 nm) and good dispersion were obtained by a green route from tangerine peels. The shape of AgNPs was firstly predicted by absorption spectrum and then confirmed by AFM analysis. The average roughness (the arithmetic average texture of one surface) provided by AFM images was nm, and the root mean square parameter () reached the value of 36.6 nm.

The AAS results indicated that the concentration of AgNP stock suspension was 538.3 ppm. The high toxicity of silver ions is well known [41], that is why the silver content was determined in the supernatants (which contain silver ions) of the Citrus-nAg suspensions taken at different times after Citrus-nAg preparation.

The supernatants collected one hour and five hours after addition of silver nitrate to tangerine extract contained silver in concentration of 191.1 and 92.4 ppm, respectively, indicating that the silver bioreduction was not finished after 5 h, and Ag⁺ was still present in suspension. On the contrary, the silver content was 0 ppm in the supernatants collected after 1, 2, 3, and 7 days, indicating that Ag⁺ was not present in any supernatant, the Citrus-nAg being stable even after 7 days.

3.2. The Bioactivities of Citrus-nAg

The in vitro antioxidant activity assay revealed high potential of Citrus-nAg of free radical scavenging, through chemiluminescence method. Their antioxidant activity reached the value of 98.5%. Two main factors are responsible for this strong antioxidant potential:(1)the presence of antioxidant biomolecules (like polyphenols, pectin, etc.) coming from tangerine peel extract (see Figure 2(b)) as capping agents of AgNPs [42];(2)the nanodimensions of Citrus-nAg (Figure 3), which offer high total surface area providing many reaction centres that improve the free radical scavenging capacity [8, 43].

As known, usual microbial contaminants of aquatic media are Escherichia coli and Fusarium oxysporum, which can cause severe diseases [44–48], especially to the immunocompromised hosts [49] so the antimicrobial investigations were conducted on E.coli ATCC 8738 bacterium and Fusarium oxysporum ATCC 48112 fungus.

Results obtained for the antimicrobial susceptibility test of Citrus-nAg on the organism showed MIC of and μg/mL against Escherichia coli and Fusarium oxysporum, respectively (see Table 1).

Antimicrobial susceptibility was determined on 3 different days, and MIC values for each isolate were reported as the median of 3 experiments.

The C. reticulate-based AgNPs exhibited strong antibacterial activity against E.coli ATCC 8738 (Figure 4). On the plate corresponding to the Citrus-nAg, 1 MIC (25 μg/mL), E. coli culture was inhibited (0 CFU/mL of E. coli), confirming the antibacterial effect of this sample (Figure 4(c)). In the plates corresponding to the Citrus-nAg, 0.25 MIC (6.25 μg/mL), a more pronounced growth of E. coli was noticed ( CFU/mL).

(a)

(b)

(c)

This microbial response is due to the presence on the AgNP surface of the capping biomolecules arising from C. reticulata peels (see Figure 2(b)), which have antibacterial properties (pectin, flavonoids, etc.). As observed, Citrus-nAg has great potential for application as disinfectant for pools, ponds, or different aquatic basins.

The antifungal activity investigation of the biogenerated AgNPs was performed as previously described (see Section 2.3). Fungicidal activity of Citrus-nAg against Fusarium oxysporum ATCC 48112, a commonly occurring fungal aquatic pathogen, is illustrated in Figure 5.

(a)

(b)

(c)

Citrus-AgNPs showed a significant effect on morphological structure of this fungus (Figure 6(b)); it induced important changes in the macroscopic appearance of fungal colonies (near halo) and the colonies appeared white and adherent to the surface of the medium. In most cases, the addition of Citrus-nAg led to smaller colonies and partial loss of spore formation (see as colorless colonies).

(a)

(b)

Light microscopic observation on Fusarium oxysporum hyphae exposed to AgNPs revealed considerable morphological alterations in hyphae; these appeared degraded and large vesicles are also visible.

Light microscopy of untreated fungi revealed normal mycelia; however hyphae of the strains grown on media with Citrus-nAg revealed alterations in the morphology of the hyphae and in the sporulation process.

The antifungal activity of these silver nanoparticles is maybe due to their capacity of anchoring to the surface of fungal cells destructing the membrane integrity [50], which caused the cell death. Another key factor responsible for this antifungal ability of Citrus-nAg is the presence of phytomolecules (flavonoids, pectin, volatile oils, etc.), arising from Citrus reticulata peels extract, as capping agents for Citrus-nAg, with fungicide properties [51–53].

3.2.1. The Impact of Citrus-nAg on Biomimetic Membranes

In order to get more information (at molecular level) about the action of Citrus-nAg on the wetland plants, we firstly studied the influence of these nanosilver particles on mimicking cell membranes, because the biomembranes are the first target for any stressor. Increasing concentrations of Citrus-nAg were added to a suspension of biomimetic membranes marked with Chla, which were characterized by absorption and emission spectroscopy (Figure 7). Chla acted as a spectral marker that detects the changes occurring in artificial lipid bilayers. It was observed that the height of the red absorption peak (Figure 7(a)) was reduced under AgNP stress.

(a)

(b)

Chla fluorescence quenching occurred in Citrus-nAg-stressed biomimetic membranes (Figure 7(b)), action that is possible due to an electron-transfer or an energy-transfer process when the fluorophore, which is the porphyrin ring of chlorophyll, attached directly to the surface of AgNPs [54, 55].

3.2.2. The Bioimpact of Citrus-nAg on Wetland Plants

The effects of Citrus-nAg on four native wetland plants, Typha latifolia, Butomus umbellatus, Lemna minor, and Polygonum hydropiper (Figure 8), were studied. These plants were collected from a natural lake in a park from Oltenita, a Romanian city.

The plants (about two months aged) were treated with increasing concentrations of Citrus-nAg (0.42, 0.84, 1.675, 3.35, 6.7, 13.4, 26.8, and 53.5 ppm) and then visually monitored for two weeks. No significant alterations of herbals were observed with the naked eye at Citrus-nAg concentrations less than 13.4 ppm. In all cases, the concentration of 13.4 ppm was critical, because at this concentration of AgNPs, visible modifications on plant morphology could be observed. At concentrations greater than 13.4 ppm, the plants were died. Flowering-rush and Water-pepper were the most sensitive: they started withering after four days of AgNPs-stress. On the contrary, the rush withered just after two weeks. Duckweed was the most resistant; in this case, visible modifications were observed only at AgNP concentration greater than 13.4 ppm.

These visual observations were further confirmed by spectral characterization of the vegetal extracts prepared by shredding the leaves of each wetland plants, in distilled water (the mass ratio leaves/water was 1 : 10). In this respect, we compared the absorption spectra of the extracts prepared from AgNPs (13.4 ppm)-stressed plants with that of untreated ones (Figure 9).

Chlorophyll (Chl) was chosen as an indicator of plant quality. Chl is a key molecule in photosynthesis and plays a vital role for higher plants surviving. The level of Chl is an indicator of physiological status of plants, any change of Chl absorption or Chl fluorescence reflecting the level of photosynthesis [56].

Monitoring the absorption band at the main red peak of Chls, which is a spectral signature of these porphyrins, a decline of this band was observed and hence a decrease in chlorophyll content after nAg stress. This process was also observed in the previous assay performed on biomimetic membranes (see Figure 7). The intensity of the main red peak characteristic for Chl decreased under nAg stress, but in the case of Butomus umbellatus, this band disappeared.

Similar behavior was found by Miao and coworkers [57], which observed a reduction of plant growth, photosynthesis, and chlorophyll production in algae after AgNP treatment. Barbasz et al. highlighted that MNPs significantly affected the physiological properties of plants [58].

In our work, the bioimpact of Citrus-nAg on wetland plants was more pronounced in the case of Butomus umbellatus and nonsignificant in the case of Lemna minor. These findings are in accordance with our visual observations and with the experiments on artificial cell membranes (Figure 7).

Based on these results, we can concluded that Citrus-nAg enter into cell membranes and could induce physiological changes in plants (in a dose-dependent manner), by altering also the chlorophyll content.

4. Conclusions

An eco-friendly method was employed to biogenerate nanosilver, by using the aqueous extract of Citrus reticulata peels that proved to be very good bioreductant of silver ions for the synthesis of AgNPs. The biosynthesized AgNPs exhibited strong antimicrobial activity against Fusarium oxysporum ATCC 48112 fungus and Escherichia coli ATCC 8738 bacterium and also high antioxidant capacity.

The bioeffect of Citrus-nAg on four living wetland plants (Typha latifolia, Butomus umbellatus, Lemna minor, and Polygonum hydropiper) was studied through both in vivo and in vitro assays, by choosing the natural photopigment, chlorophyll, as an indicator of plant quality. A dose-dependent effect of AgNPs on the tested plants was observed. Furthermore, the optical signature of chlorophyll embedded in biomimetic membranes offered useful information about Citrus-nAg stress, at molecular level. The exposure to Citrus-nAg at an appropriate concentration could only sanitize the aquatic basins, keeping intact the weed flora. But in certain concentrations, these AgNPs could kill even the invasive plants.

The use of phytosynthesized AgNPs in aquatic media is a safer procedure, because the capping agents are biogenic and benign for environment.

Our results suggest that this “green” nanosilver biogenerated from aqueous extract of Citrus reticulata peels could be used in fabrication of eco-friendly disinfectants to fight against fungi and bacteria in wet media (swimming pools, shower drainages, SPA retreats, water filters, wetlands, etc.) and also in herbicidal nanoformulations to manage and keep under control the invasive aquatic plants.

Conflicts of Interest

The authors declare that there are no conflicts of interest regarding the publication of this paper.

Acknowledgments

This work was cofinanced from the European Social Fund through the Sectorial Operational Programme Human Resources Development 2007–2013, Contract Code: POSDRU/187/1.5/S/155559, multidisciplinary doctoral research on European competitiveness (CdocMD) (M. Constantin). S. M. Iordache acknowledges research support provided under UEFISCDI Ctr. no. 142/2014 and Ctr. no. 46/2014.

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Copyright © 2017 Marcela Elisabeta Barbinta-Patrascu et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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