# Evaluation of the Antimicrobial Activity of Nanostructured Materials of Titanium Dioxide Doped with Silver and/or Copper and Their Effects onArabidopsis thaliana

Authors: Cristina Garcidueñas-Piña; Iliana E. Medina-Ramírez; Plinio Guzmán; Roberto Rico-Martínez; José Francisco Morales-Domínguez; Isidoro Rubio-Franchini
Journal: International Journal of Photoenergy
 (2016)

---

## Abstract

Nanostructured materials (NSMs) of silver (Ag@TiO2) and copper (TiO2-Cu2+) doped titanium dioxide were synthesized, fully characterized, and evaluated for their antimicrobial efficiency and effects onArabidopsis thaliana. The NSMs were prepared using an environmentally benign route. The physicochemical properties of the materials were determined with analytical techniques. These materials are active under visible light, exhibit a small size (10–12 nm), are crystalline (anatase), and liberate metal ions (Ag+ and Cu2+) in solution. Microbicide activity was observed inE. coli C600 andS. cerevisiae W303 strains treated with several concentrations of Ag@TiO2 and TiO2-Cu2+, radiated and nonradiated, and after different times. Higher inactivation was achieved with Ag@TiO2 inE. coli, with value of log inactivation of 2.2 with 0.5 mg/mL after 4 h, than inS. cerevisiae, with a log inactivation of 2.6 with 10 mg/mL after 24 h. The impact of these NSMs in plants was evaluated inArabidopsis thaliana Col-0 strain exposed to such materials at different conditions and concentrations, and physical and biochemical effects were analyzed. Seeds exposed to NSMs did not show effects on germination and growth. However, seedlings treated with these materials modified their growth and their total chlorophyll content.


---

## Body

## 1. Introduction

Nanostructured materials (NSMs) have become the focus of numerous investigations due to their unique physicochemical properties which are different from the same materials with larger dimensions [1]; these properties have been exploited for the development of several new products with different technological and medical applications [2, 3]. Lately, engineered NSMs can be produced with specific physicochemical properties for advanced applications. Some of these NSMs have demonstrated microbicide activity and are being used as disinfectants for water purification, with several advantages over the traditional water disinfection technologies. Researchers have a special interest in metal/semiconductor oxide composites since they have been shown to be efficient bifunctional materials, which can be used in numerous physical, biological, biomedical, and pharmaceutical applications [4]. Among the various materials, titanium dioxide (TiO2) has been widely studied because of its chemical stability, low toxicity, abundance, and excellent photocatalytic activity [5]. It has also been demonstrated that coupling TiO2 with noble metals renders visible light active materials with increased photocatalytic and photoelectrochemical responses of the composite material by reducing the fast recombination of the photogenerated charge carriers [6, 7]. It has been demonstrated that Ag@TiO2 efficiently removes several pathogenic microorganisms from water, air, and surfaces [8–11]; however, the ecological impact of this material has been scarcely studied [12–14]. Although to a lesser extent than Ag@TiO2 composites, the bactericidal effect of TiO2-Cu2+ materials has been lately investigated [15–17]. We have been working on the implementation of green routes for the synthesis of metal doped NSMs with enhanced activity [18–20]. Ag@TiO2 and/or TiO2-Cu2+ synthetized by that methodology need a systematic study of characterization, photocatalytic activity, antimicrobial activity, and toxicological impact. The study of the antimicrobial activity in model organisms has the advantage of obtaining results in a reproducible, easy, cheap, and fast way.Escherichia coli C600 strain is a harmless gram negative bacterium of easy handling in the laboratory. Furthermore,Saccharomyces cerevisiae W303a strain is a fungus unicellular yeast with a comparable lifespan to that ofE. coli. Therefore, both microorganisms were selected to study antimicrobial activity of Ag@TiO2 and TiO2-Cu2+ to determine the range of effective antimicrobial concentrations. The seeds disinfection like potential use of these materials was considered, so that the antimicrobial activity was evaluated in seeds and in fungal contaminants seeds too.The impact of interaction of plants with NSMs is becoming a priority since plants can serve as reservoirs of NSMs, and plants are directly exposed to soil, water, and air, where NSMs could be dispersed. As a result of that interaction, uptake and accumulation of NSMs is likely to take place giving rise to deleterious effects in plants or they may become one of the main routes of exposure to NSMs for higher species [21]. Despite the preliminary efforts to determine the potential hazard of NSMs in plants, currently published results are contradictory regarding phytotoxicity of NSMs. For instance, Shaw and Hossain [22] reported that the interaction of NSMs (CuO) with plants affects their development and productivity, whereas Li and coworkers [23] indicate that the interaction of NSMs (Fe3O4) with watermelon seedlings is beneficial, since increased accumulation of chlorophyll is observed. In the same direction, Kole and coworkers [24] reported on the effects of seed treatment with fullerol NSMs that resulted in increasing plant biomass, fruit yield, and phytomedicine content in bitter melon; thus, the authors suggest the use of fullerol for crop improvement. In view of the contradictory findings described in the above-mentioned reports and due to the lack of standards and guidance for NSMs toxicity evaluation, it is evident that many technical challenges must be surpassed to achieve objective information regarding toxicity evaluation of NSMs.Arabidopsis thaliana is being used as model organism, because of its small size, little space requirements, and short life cycle. Its small seed size results in a relatively large surface area to volume ratio, which is conducive to higher sensitivity to toxicants.A. thaliana is also the first plant to have its genome sequenced, which facilitates future work on its molecular response to NSMs [25]. Therefore, the goals of this work are as follows: (a) to report on the synthesis and characterization of TiO2-Cu2+, (b) to evaluate the antimicrobial activity of Ag@TiO2 and TiO2-Cu2+ in two model organisms:E. coli andS. cerevisiae and in fungi isolated from seeds, and (c) to analyze the effects of the interaction of Ag@TiO2 and TiO2-Cu2+ onA. thaliana.


## 2. Materials and Methods

### 2.1. Synthesis and Characterization of Ag@TiO2 and TiO2-Cu2+

#### 2.1.1. Synthesis of NSMs

Ag@TiO2 were synthesized according to previously reported protocol by our research group [18]. TiO2-Cu2+ were synthesized following the similar procedure for Ag@TiO2 materials, with slight modifications: in a flask, copper sulfate (CuSO4) was dissolved in acetic acid (C2H4O2) and titanium isopropoxide Ti(OCH(CH3)2)4 was added slowly and stirred continuously. Arabic gum was added and the mixture was dried in a heating mantle and then thermally treated in a furnace at 350°C for 3 h. The resulting powders were washed with a mixture of H2O : ethanol (3 : 1) and allowed to dry.


#### 2.1.2. Characterization of NSMs

The TiO2-Cu2+ were characterized by X-ray diffraction (XRD), scanning electron microscopy-energy dispersive spectrometry (SEM-EDS), dynamic light scattering, and atomic absorption spectroscopy (AAS). The powder XRD patterns of the samples were recorded in a Brucker D Advance Diffractometer using Cu Kα radiation (λ
=
1.5418
Å) at a scanning rate of 0.05°/min for 2θ ranging from 10° to 85°. The XRD patterns were analyzed using standard ICDD files. The average particle size distribution in the samples was measured by dynamic light scattering using a Malvern particle size analyzer. The particle surface charge of the samples was analyzed by measuring the ζ potential of the samples.


### 2.2. Evaluation of Antimicrobial Activity of Ag@TiO2 and TiO2-Cu2+

The antimicrobial activity of Ag@TiO2 and TiO2-Cu2+ was investigated in the bacteriumE. coli strain C600 (F-tonA21 thi-1 thr-1 leuB6 lacY1 glnV44 rfbC1 fhuA1 λ-) and the yeastS. cerevisiae strain W303 (MATa/MATα  leu2-3,112 trp1-1 can1-100 ura3-1 ade2-1 his3-11,15 [phi+]), both laboratory strains and model organisms. They were cultivated using standard microbiological techniques.E. coli C600 was cultured on LB (Luria-Bertani) andS. cerevisiae W303 in PD (Potato-Dextrose) solid media. A colony was taken and inoculated in 5 mL of liquid medium and incubated for 24 h under stirring at 37°C forE. coli and 28°C forS. cerevisiae. Then, a volume of 1.5 mL of the culture was placed in a microcentrifuge tube and centrifuged at 12,000 rpm for 5 min; the supernatant was removed and the pellet was suspended in sterile potassium phosphate buffer 0.05 M pH 7. This microbial suspension was diluted to obtain a title of 106 CFU/mL (colony forming units per milliliter) forE. coli C600 and 104 CFU/mL forS. cerevisiae W303. A volume of 1 mL of the microorganism suspension was placed in test tube and NSMs were added to have concentrations of 0.00, 0.5, 1, 2.5, 5, and 10 mg/mL. Colloidal silver BacDyn Plus® 0.015 mM, a commercial disinfectant (A
g
0), and CuSO4 (1 mM) were used as controls. The suspensions were mixed and incubated at 25°C with shaking at 150 rpm. The inactivation of microorganisms (MOs) was measured at different time intervals (2, 4, 6, 8, and 24 h). To evaluate the antimicrobial effect of metal (A
g
0 or Cu2+), some suspensions were incubated in the dark; to demonstrate the synergistic effect of NSMs (metal + photocatalysis), other suspensions were incubated under radiation (8 ft., 75-Watt cool white linear fluorescent light bulb). After incubation, aliquots of suspensions were inoculated in solid medium (LB forE. coli C600 and PD forS. cerevisiae W303) and after incubation the number of colonies was counted to calculate the surviving number of CFU/mL. The log inactivation was calculated as log
10
⁡
(
N
/
N
0
), where N
0 represent the initial CFU/mL and N the CFU/mL surviving to treatment. Experiments were performed in triplicate and sterile conditions were maintained.


### 2.3. Evaluation of the Antimicrobial Action of Ag@TiO2 and TiO2-Cu2+ for Crop Protection

To evaluate the efficiency of NSMs (Ag@TiO2 and TiO2-Cu2+) for microbial control in crop protection, treatment of fungal pathogensin vitro and disinfection ofA. thaliana seeds were examined. The efficiency of NSMs for disinfection ofA. thaliana seeds was investigated with different conditions. The biological material (50 seeds) was exposed to NSMs (10 mg/mL of Ag@TiO2 or TiO2-Cu2+) and the effect of the pretreatment of the seeds (previous exposition to NSMs) with ethanol (70% v/v) solution or Tween (0.15% w/v) was also evaluated. Treatment with sodium hypochlorite and Tween 20 (common disinfection agents) was used as positive control, and sterile H2O was used as negative control. Experiments were performed in triplicate and sterile conditions were maintained.Anin vitro assay was conducted to assess the capacity for the treatment of plant pathogens of the NSMs under study; thus, microorganisms were isolated fromA. thaliana seeds and exposed to disinfection agent at different concentrations using a sterile potassium phosphate buffer (0.05 M, pH 7). The suspensions were incubated at 25°C in a shaker incubator under visible light for 24 h. After that, 100 μL of the suspension was spread in PD agar and incubated at 25°C for 3 days.Antifungal activity of NSMs was evaluated using two fungal species (isolated microorganisms from nondisinfected seeds ofA. thaliana culturedin vitro):Aspergillus spp. andFusarium spp. fungi (1000 spores/mL) and NSMs (10 mg/mL of Ag@TiO2 or TiO2-Cu2+) were incubated under visible light for 24 h at 25°C. After that, 10 μL aliquot of the suspensions was placed in PD agar medium and incubated at 25°C for 3 days. Growth inhibition was measured by calculating radial inhibition against control group. Experiments were conducted in triplicate. Radial inhibition (RI%) was calculated in accordance with the following equation [26]:(1)
R
I
%
=
D
-
d
×
100
D
,where D is diameter of fungal growth (control group) and d is diameter of fungal growth (exposed to NSMs).


### 2.4. Evaluation of Effects onA. thaliana Exposed to Ag@TiO2 and TiO2-Cu2+

Seeds ofA. thaliana were disinfected using traditional techniques (sodium hypochlorite and Tween 20), incubated at 4°C for 3 days, and exposed to NSMs under several conditions: (a) exposition of seeds to NSMs under visible light for a day to analyze germination in filter paper and development in Murashige and Skoog medium (MS) [27]; (b) exposition of seeds-seedlings to NSMs in distilled water or MS liquid medium for a period of a week to analyze elongation of seedlings; (c) exposition of two-day-old seedlings to NSMs in distilled water under visible light and/or dark conditions for a day to analyze elongation of seedling after 4 days. Media were supplemented with 0, 0.5, 1, 2.5, 5, and 10 mg/mL of NSMs (Ag@TiO2 or TiO2-Cu2+), 0.015 mM of A
g
0, or 1 mM of CuSO4 (Table 1). The length of seedlings was measured with image analysis using the software Motic Images Plus 2.0.Table 1
Treatments of exposition ofA. thaliana to NSM.
Treatment
A. thaliana
Exposure medium
Exposure time
Parameter
1
Seeds
H2O distilled
24 h
Germination and development
Phosphate buffer pH 5.7
2
Seeds-seedlings
H2O distilled
1 week
Elongation of seedling
MS liquid
3
Two-day-old seedlings
H2O distilled
24 h
Elongation of seedling
Exposure media were supplemented with 0, 0.5, 1, 2.5, 5, and 10 mg/mL of NSM (Ag@TiO2 or TiO2-Cu2+), 0.015 mM Ag0, or 1 mM CuSO4.


### 2.5. Quantification of Chlorophyll and Anthocyanin

Total chlorophyll content was determined by using a modified method described by Nair and Chung [28], with slight modifications: seedlings treated with NSMs both, for a day and for a week, were incubated in 96% (v/v) ethanol (50 mg of tissue for 10 mL of ethanol) under dark conditions at 4°C for 3 days. The absorbance of the supernatant was measured at wavelengths of 665 (A
665) and 649 (A
649) nm using a spectrophotometer (Thermo Scientific Genesys 10S UV-Vis). Total chlorophyll contents were determined by using the following formula:(2)
Chlorophyll  a  (Chla)
=
13.95
A
665
-
6.88
A
649
,
Chlorophyll  b  (Chlb)
=
24.96
A
649
-
7.32
A
665
,
Total  chlorophyll
=
C
h
l
a
+
C
h
l
b
.The anthocyanin content was determined as described by Nair and Chung [28] with slight modifications: seedlings were incubated in a 99 : 1 methanol : HCl (v/v) solution at 4°C overnight. Supernatant was separated and light absorption was measured at 530 and 657 nm (A
530 and A
657) using a UV-Vis spectrophotometer (Thermo Scientific Genesys 10S). The relative units of anthocyanin (RUA) levels were determined with the following equation:(3)
R
U
A
/
g
=
A
530
-
0.25
×
A
657
.


### 2.6. Quantification of Silver and Copper by Atomic Absorption Spectrophotometry

Seedlings were washed with either sterile distilled H2O and/or 10 mM EDTA solution (with a pH of 6) to remove metal adhered on the plants surface; they were dried at 75°C for 48 h, digested with concentrated HNO3 at 115°C for 1 h, and diluted with sterile distilled H2O to obtain 1 mg of tissue/mL. The processed seedlings and the exposure mediums were filtered and acidified with HNO3 and analyzed using AAS (Analyst AS-90Plus).


### 2.7. Statistical Analysis

Results were compared by one-way analysis of variance (ANOVA) followed by Duncan’s test for comparison and lineal regression analysis. All data were expressed as mean ± one standard deviation. A value ofp
<
0.05 was considered statistically significant.


## 2.1. Synthesis and Characterization of Ag@TiO2 and TiO2-Cu2+

### 2.1.1. Synthesis of NSMs

Ag@TiO2 were synthesized according to previously reported protocol by our research group [18]. TiO2-Cu2+ were synthesized following the similar procedure for Ag@TiO2 materials, with slight modifications: in a flask, copper sulfate (CuSO4) was dissolved in acetic acid (C2H4O2) and titanium isopropoxide Ti(OCH(CH3)2)4 was added slowly and stirred continuously. Arabic gum was added and the mixture was dried in a heating mantle and then thermally treated in a furnace at 350°C for 3 h. The resulting powders were washed with a mixture of H2O : ethanol (3 : 1) and allowed to dry.


### 2.1.2. Characterization of NSMs

The TiO2-Cu2+ were characterized by X-ray diffraction (XRD), scanning electron microscopy-energy dispersive spectrometry (SEM-EDS), dynamic light scattering, and atomic absorption spectroscopy (AAS). The powder XRD patterns of the samples were recorded in a Brucker D Advance Diffractometer using Cu Kα radiation (λ
=
1.5418
Å) at a scanning rate of 0.05°/min for 2θ ranging from 10° to 85°. The XRD patterns were analyzed using standard ICDD files. The average particle size distribution in the samples was measured by dynamic light scattering using a Malvern particle size analyzer. The particle surface charge of the samples was analyzed by measuring the ζ potential of the samples.


## 2.1.1. Synthesis of NSMs

Ag@TiO2 were synthesized according to previously reported protocol by our research group [18]. TiO2-Cu2+ were synthesized following the similar procedure for Ag@TiO2 materials, with slight modifications: in a flask, copper sulfate (CuSO4) was dissolved in acetic acid (C2H4O2) and titanium isopropoxide Ti(OCH(CH3)2)4 was added slowly and stirred continuously. Arabic gum was added and the mixture was dried in a heating mantle and then thermally treated in a furnace at 350°C for 3 h. The resulting powders were washed with a mixture of H2O : ethanol (3 : 1) and allowed to dry.


## 2.1.2. Characterization of NSMs

The TiO2-Cu2+ were characterized by X-ray diffraction (XRD), scanning electron microscopy-energy dispersive spectrometry (SEM-EDS), dynamic light scattering, and atomic absorption spectroscopy (AAS). The powder XRD patterns of the samples were recorded in a Brucker D Advance Diffractometer using Cu Kα radiation (λ
=
1.5418
Å) at a scanning rate of 0.05°/min for 2θ ranging from 10° to 85°. The XRD patterns were analyzed using standard ICDD files. The average particle size distribution in the samples was measured by dynamic light scattering using a Malvern particle size analyzer. The particle surface charge of the samples was analyzed by measuring the ζ potential of the samples.


## 2.2. Evaluation of Antimicrobial Activity of Ag@TiO2 and TiO2-Cu2+

The antimicrobial activity of Ag@TiO2 and TiO2-Cu2+ was investigated in the bacteriumE. coli strain C600 (F-tonA21 thi-1 thr-1 leuB6 lacY1 glnV44 rfbC1 fhuA1 λ-) and the yeastS. cerevisiae strain W303 (MATa/MATα  leu2-3,112 trp1-1 can1-100 ura3-1 ade2-1 his3-11,15 [phi+]), both laboratory strains and model organisms. They were cultivated using standard microbiological techniques.E. coli C600 was cultured on LB (Luria-Bertani) andS. cerevisiae W303 in PD (Potato-Dextrose) solid media. A colony was taken and inoculated in 5 mL of liquid medium and incubated for 24 h under stirring at 37°C forE. coli and 28°C forS. cerevisiae. Then, a volume of 1.5 mL of the culture was placed in a microcentrifuge tube and centrifuged at 12,000 rpm for 5 min; the supernatant was removed and the pellet was suspended in sterile potassium phosphate buffer 0.05 M pH 7. This microbial suspension was diluted to obtain a title of 106 CFU/mL (colony forming units per milliliter) forE. coli C600 and 104 CFU/mL forS. cerevisiae W303. A volume of 1 mL of the microorganism suspension was placed in test tube and NSMs were added to have concentrations of 0.00, 0.5, 1, 2.5, 5, and 10 mg/mL. Colloidal silver BacDyn Plus® 0.015 mM, a commercial disinfectant (A
g
0), and CuSO4 (1 mM) were used as controls. The suspensions were mixed and incubated at 25°C with shaking at 150 rpm. The inactivation of microorganisms (MOs) was measured at different time intervals (2, 4, 6, 8, and 24 h). To evaluate the antimicrobial effect of metal (A
g
0 or Cu2+), some suspensions were incubated in the dark; to demonstrate the synergistic effect of NSMs (metal + photocatalysis), other suspensions were incubated under radiation (8 ft., 75-Watt cool white linear fluorescent light bulb). After incubation, aliquots of suspensions were inoculated in solid medium (LB forE. coli C600 and PD forS. cerevisiae W303) and after incubation the number of colonies was counted to calculate the surviving number of CFU/mL. The log inactivation was calculated as log
10
⁡
(
N
/
N
0
), where N
0 represent the initial CFU/mL and N the CFU/mL surviving to treatment. Experiments were performed in triplicate and sterile conditions were maintained.


## 2.3. Evaluation of the Antimicrobial Action of Ag@TiO2 and TiO2-Cu2+ for Crop Protection

To evaluate the efficiency of NSMs (Ag@TiO2 and TiO2-Cu2+) for microbial control in crop protection, treatment of fungal pathogensin vitro and disinfection ofA. thaliana seeds were examined. The efficiency of NSMs for disinfection ofA. thaliana seeds was investigated with different conditions. The biological material (50 seeds) was exposed to NSMs (10 mg/mL of Ag@TiO2 or TiO2-Cu2+) and the effect of the pretreatment of the seeds (previous exposition to NSMs) with ethanol (70% v/v) solution or Tween (0.15% w/v) was also evaluated. Treatment with sodium hypochlorite and Tween 20 (common disinfection agents) was used as positive control, and sterile H2O was used as negative control. Experiments were performed in triplicate and sterile conditions were maintained.Anin vitro assay was conducted to assess the capacity for the treatment of plant pathogens of the NSMs under study; thus, microorganisms were isolated fromA. thaliana seeds and exposed to disinfection agent at different concentrations using a sterile potassium phosphate buffer (0.05 M, pH 7). The suspensions were incubated at 25°C in a shaker incubator under visible light for 24 h. After that, 100 μL of the suspension was spread in PD agar and incubated at 25°C for 3 days.Antifungal activity of NSMs was evaluated using two fungal species (isolated microorganisms from nondisinfected seeds ofA. thaliana culturedin vitro):Aspergillus spp. andFusarium spp. fungi (1000 spores/mL) and NSMs (10 mg/mL of Ag@TiO2 or TiO2-Cu2+) were incubated under visible light for 24 h at 25°C. After that, 10 μL aliquot of the suspensions was placed in PD agar medium and incubated at 25°C for 3 days. Growth inhibition was measured by calculating radial inhibition against control group. Experiments were conducted in triplicate. Radial inhibition (RI%) was calculated in accordance with the following equation [26]:(1)
R
I
%
=
D
-
d
×
100
D
,where D is diameter of fungal growth (control group) and d is diameter of fungal growth (exposed to NSMs).


## 2.4. Evaluation of Effects onA. thaliana Exposed to Ag@TiO2 and TiO2-Cu2+

Seeds ofA. thaliana were disinfected using traditional techniques (sodium hypochlorite and Tween 20), incubated at 4°C for 3 days, and exposed to NSMs under several conditions: (a) exposition of seeds to NSMs under visible light for a day to analyze germination in filter paper and development in Murashige and Skoog medium (MS) [27]; (b) exposition of seeds-seedlings to NSMs in distilled water or MS liquid medium for a period of a week to analyze elongation of seedlings; (c) exposition of two-day-old seedlings to NSMs in distilled water under visible light and/or dark conditions for a day to analyze elongation of seedling after 4 days. Media were supplemented with 0, 0.5, 1, 2.5, 5, and 10 mg/mL of NSMs (Ag@TiO2 or TiO2-Cu2+), 0.015 mM of A
g
0, or 1 mM of CuSO4 (Table 1). The length of seedlings was measured with image analysis using the software Motic Images Plus 2.0.Table 1
Treatments of exposition ofA. thaliana to NSM.
Treatment
A. thaliana
Exposure medium
Exposure time
Parameter
1
Seeds
H2O distilled
24 h
Germination and development
Phosphate buffer pH 5.7
2
Seeds-seedlings
H2O distilled
1 week
Elongation of seedling
MS liquid
3
Two-day-old seedlings
H2O distilled
24 h
Elongation of seedling
Exposure media were supplemented with 0, 0.5, 1, 2.5, 5, and 10 mg/mL of NSM (Ag@TiO2 or TiO2-Cu2+), 0.015 mM Ag0, or 1 mM CuSO4.


## 2.5. Quantification of Chlorophyll and Anthocyanin

Total chlorophyll content was determined by using a modified method described by Nair and Chung [28], with slight modifications: seedlings treated with NSMs both, for a day and for a week, were incubated in 96% (v/v) ethanol (50 mg of tissue for 10 mL of ethanol) under dark conditions at 4°C for 3 days. The absorbance of the supernatant was measured at wavelengths of 665 (A
665) and 649 (A
649) nm using a spectrophotometer (Thermo Scientific Genesys 10S UV-Vis). Total chlorophyll contents were determined by using the following formula:(2)
Chlorophyll  a  (Chla)
=
13.95
A
665
-
6.88
A
649
,
Chlorophyll  b  (Chlb)
=
24.96
A
649
-
7.32
A
665
,
Total  chlorophyll
=
C
h
l
a
+
C
h
l
b
.The anthocyanin content was determined as described by Nair and Chung [28] with slight modifications: seedlings were incubated in a 99 : 1 methanol : HCl (v/v) solution at 4°C overnight. Supernatant was separated and light absorption was measured at 530 and 657 nm (A
530 and A
657) using a UV-Vis spectrophotometer (Thermo Scientific Genesys 10S). The relative units of anthocyanin (RUA) levels were determined with the following equation:(3)
R
U
A
/
g
=
A
530
-
0.25
×
A
657
.


## 2.6. Quantification of Silver and Copper by Atomic Absorption Spectrophotometry

Seedlings were washed with either sterile distilled H2O and/or 10 mM EDTA solution (with a pH of 6) to remove metal adhered on the plants surface; they were dried at 75°C for 48 h, digested with concentrated HNO3 at 115°C for 1 h, and diluted with sterile distilled H2O to obtain 1 mg of tissue/mL. The processed seedlings and the exposure mediums were filtered and acidified with HNO3 and analyzed using AAS (Analyst AS-90Plus).


## 2.7. Statistical Analysis

Results were compared by one-way analysis of variance (ANOVA) followed by Duncan’s test for comparison and lineal regression analysis. All data were expressed as mean ± one standard deviation. A value ofp
<
0.05 was considered statistically significant.


## 3. Results and Discussion

### 3.1. Synthesis and Characterization of Ag@TiO2 and TiO2-Cu2+

The synthesis of Ag@TiO2 and TiO2-Cu2+ nanostructured materials was achieved using an environmentally friendly sol-gel procedure. The amount of silver or copper into the materials was formulated to be 1% (mol/mol; Ag/Ti or Cu2+/Ti). Results of analysis of Ag@TiO2 composites by SEM-EDX indicate that the TiO2 is spherical with a mean size diameter of ~10 nm (Figure 1(a)). Silver nanoparticles show a mean diameter smaller than 10 nm; thus, it was not possible to determine their mean size by SEM analysis. EDX analysis demonstrates the existence of Ti, O, and Ag in accordance with the molar ratio of the formulation (Figure 1(b)). SEM analysis of TiO2-Cu2+ also indicates a spherical shape and mean size of ~10 nm (Figure 1(c)). The presence of Ti, O, and Cu in the appropriate mole ratio was demonstrated by EDX data (Figure 1(d)). The materials were obtained as crystalline nanostructured powders after thermal annealing at 350°C. The materials exhibit anatase crystalline structure.Figure 1
Characterization of NSMs. (a) SEM image of Ag@TiO2. (b) Elemental composition of Ag@TiO2 (EDX). (c) SEM image of TiO2-Cu2+. (d) Elemental composition of TiO2-Cu2+ (EDX).
(a)
(b)
(c)
(d)The aggregation state of NSMs is a critical factor for experimentally assessing their toxic activity. It is well known that independent of the primary particle size (as solid state materials) NSMs tend to agglomerate when suspended in different media. The biological components present in the culture media and electrolytes may interact with NSMs to change their physicochemical properties (i.e., modification of surface properties) and aggregation state. The stability of these materials was evaluated using TiO2 (Sigma-Aldrich) as control. Dynamic light scattering analysis of the materials suspended in distilled water or Physiological Saline Solution (PSS) was performed and these results indicate that the materials form bigger aggregates in saline solution than in distilled water. The hydrodynamic radio of the materials is 477 nm (TiO2), 467 nm (Ag@TiO2), and 360 nm (TiO2-Cu2+) when suspended in distilled water. For the suspensions in PSS, the agglomerates exhibit a mean size of 774 nm (TiO2), 776 nm (Ag@TiO2), and 750 nm (TiO2-Cu2+). Zeta potential of the suspension was also evaluated. For distilled water suspensions, the following zeta potential values were encountered: +10.39 mV (TiO2), −27.83 mV (Ag@TiO2), and +14.73 mV (TiO2-Cu2+). In the case of PSS suspensions, the following results were encountered: +48.01 mV (TiO2), +81.94 mV (Ag@TiO2), and +6.85 mV (TiO2-Cu2+). The studied materials present a positive surface charge when suspended in PSS. It has been reported that positively charged nanoparticles interact more strongly with biomolecules due to favored electrostatic interactions since at physiological pH value biomolecules are negatively charged, thus facilitating interaction of NSMs and biomolecules.


### 3.2. Antimicrobial Activity of Ag@TiO2 and TiO2-Cu2+ inE. coli andS. cerevisiae

Two sets of inactivation kinetics assays (under visible light and in the dark) were conducted to evaluate theE. coli inactivation rate (Figures 2(a) and 2(b)). The results obtained indicate that Ag@TiO2 exerted strong bacterial inactivation (3 U log) in a short time period (2 h with 10 mg/mL of NSMs). It was also observed that lower amounts of NSMs exhibit longer inhibition times: 2.2 U log with 0.5 mg/mL at 4 h and 2.9 U log with 1 mg/mL at 4 h (Figure 2(a)). There are no significant differences for inactivation rate and extent of inactivation when assays are performed under radiation or in the dark (Figures 2(a) and 2(b)), which indicates that the principal mechanism for inactivation is the release of Ag+ ions from Ag@TiO2 materials [8, 29]. There is no inactivation ofE. coli growth as a consequence of exposure to visible light radiation. Colloidal silver inhibited bacteria growth with 6 U log at 2 h (Figures 2(a) and 2(b)). Although the inactivation rate of colloidal silver is higher than the one observed for Ag@TiO2 composites, both materials exerted efficient bactericidal effect.Figure 2
Inactivation of microorganisms by NSMs:E. coli with Ag@TiO2 (a) under visible light and (b) in dark;S. cerevisiae with Ag@TiO2 (c) under visible light and (d) in dark; (e)E. coli with TiO2-Cu2+; (f)S. cerevisiae with TiO2-Cu2+. As positive control, Ag0 for Ag@TiO2 and CuSO4 for TiO2-Cu2+. Bars represent standard deviation; each treatment was performed in triplicate.
(a)
(b)
(c)
(d)
(e)
(f)In general,S. cerevisiae was more resistant thanE. coli to colloidal silver and Ag@TiO2 NSMs microbicidal activity (Figures 2(c) and 2(d)). Longer exposure times at high concentrations of NSMs were necessary to achieve a good inhibition ofS. cerevisiae growth, with a maximum inactivation of 2.6 U log with 10 mg/mL under visible light after 24 h (Figure 2(c)). The tolerance observed by yeast to the microbicidal activity of Ag NSMs is due to the more complex structure (the presence of a cell wall, composed of beta-glucans, chitin, and mannoproteins, limits the passage of Ag+ ion) of these microorganisms [30]. When the variable under study was light radiation, slight differences were observed for the inhibition ofS. cerevisiae with Ag@TiO2, with 1.9 U log with 10 mg/mL, in dark after 24 h (Figure 2(d)). ForE. coli, an inhibition growth mechanism based on Ag+ activity was suggested since no enhancement in the rate or extent of inactivation was observed when the assay was conducted under visible light radiation. In accordance with several previously published reports, metal doped TiO2 NSMs, when activated with visible light, generate reactive oxygen species (ROS) that are associated with cell damage in microorganisms [7, 31]. For the growth inhibition ofS. cerevisiae, the effect of ROS is more significant since the components of the cell wall can be susceptible to oxidation.The TiO2-Cu2 antimicrobial activity was evaluated under the same conditions reported for Ag@TiO2 materials. Regarding highE. coli densities (106 CFU/mL), TiO2-Cu2+ NSMs did not show bactericidal activity even at the highest concentration (10 mg/mL) (Figure 2(e)). As observed for silver based materials, the activity of TiO2-Cu2+ againstE. coli depends on the amount of metal ions liberated into solution; however, since the microbicidal activity of silver is higher in comparison to copper, larger amounts of Cu2+ must be released to achieve bacterial inactivation [8, 12]. By comparing the effect of colloidal silver and copper sulfate solution, inactivation rate and extent of inactivation are lower for copper sulfate, corroborating that higher concentrations of this ion are required to achieve inactivation of elevated microbial densities (106 CFU/mL). Nonradiated samples did not show inhibitory effect.In the evaluation of the growth inhibition forS. cerevisiae using TiO2-Cu2+ materials, results indicate similar behavior to Ag@TiO2; the viability ofS. cerevisiae diminished as a function of material concentration, time of exposure, and visible light radiation. The maximum inactivation was of 1.9 U log with 10 mg/mL after 24 h (Figure 2(f)).It has been postulated that the microbicidal activity of Ag@TiO2 is proportional to the amount of silver ions released into the medium [8, 29]. To correlate the activity of the NSMs under investigation to their liberation of metal ions into solution, supernatants of the exposition medium were analyzed by AAS. Reported results indicate the presence of silver at a concentration of 0.16 ppm in the exposure medium (phosphate buffer pH 7; Table 2). Copper was also found in the exposition medium (Table 2) at very low concentration (0.5 ppm). Although the amount of Cu2+ released into the medium is higher in comparison to released Ag+, better performance of silver based materials is achieved due to enhanced microbicidal activity of Ag+.Table 2
Determination of copper and silver by atomic absorption spectrophotometry.
⁢Seedling treated in MS for a weeka
⁢Seedling treated in H2O for 24 ha
NSMs
(Ag) mg/g
(Cu) mg/g
(Ag) mg/g
(Cu) mg/g
Ag@TiO2
0.58 ± 0.03
—
0.23 ± 0.23
—
TiO2-Cu2+
—
0.29 ± 0.06
—
0.31 ± 0.03
Ag0
0.2 ± 0.05
—
0.12 ± 0.01
—
Control (−)
0
0.12 ± 0.016
0
0.13 ± 0.01
⁢MS medium after a weekb
⁢H2O after a weekb
NSMs
(Ag) ppm
(Cu) ppm
(Ag) ppm
(Cu) ppm
Ag@TiO2
0.17 ± 0.01
—
0
—
TiO2-Cu2+
—
3.17 ± 0.148
—
0.08 ± 0.02
Ag0
0.085 ± 0.03
—
0.47 ± 0.01
—
Control (−)
0
0.11 ± 0.05
0
0.04 ± 0.002
H2O after 24 hb
⁢Phosphate buffer pH 5.7 after 24 hb
NSMs
(Ag) ppm
(Cu) ppm
(Ag) ppm
(Cu) ppm
Ag@TiO2
0.06 ± 0.003
—
0.1 ± 0.01
—
TiO2-Cu2+
—
0.25 ± 0.03
—
0.47 ± 0.07
Ag0
0.63 ± 0.02
—
0.25 ± 0.02
—
Control (−)
0
0.11 ± 0.05
0
0.03 ± 0.001
⁢Phosphate buffer pH 7 after 24 hc
NSMs
(Ag) ppm
(Cu) ppm
Ag@TiO2
0.16 ± 0.02
—
TiO2-Cu2+
—
0.5 ± 0.01
Ag0
0.2 ± 0.04
—
Control (−)
0
0.1 ± 0.03
aSeedling treated, bexposure medium of seedlings, and cexposure medium of microorganisms with 1 mg/mL of Ag@TiO2, 1 mg/mL of TiO2-Cu2+, and 0.015 mM Ag0.


### 3.3. Activity of Ag@TiO2 and TiO2-Cu2+ in Seed Disinfection

Several experiments were conducted to assess Ag@TiO2 and TiO2-Cu2+ use as disinfectants for axenic conditions.A. thaliana seeds were treated with 10 mg/mL of NSMs for 24 h and then cultured in MS agar medium. Results are summarized in Figure 3(a) and indicate that total seed disinfection was not observed with this treatment. Although inhibition of microbial growth was observed for the samples treated with NSMs, the activity of the materials is insufficient forin vitro culture of seeds (Ag@TiO2: 72% inhibition; TiO2-Cu2+: 36% inhibition; control: 41% inhibition). It is important to remark that the materials show good microbicidal activity when they are evaluated using a single microorganisms species (i.e.,E. coli orS. cerevisiae); however, when the materials are exposed to microorganisms consortiums, the activity of the materials seems to be diminished.Figure 3
Seeds and their contaminants treated with Ag@TiO2 and TiO2-Cu2+. (a) Treatment ofA. thaliana seeds with 10 mg/mL of NSMs prior to cultivationin vitro; (b) fungal contaminants seeds exposed to 10 mg/mL of NSMs; each treatment was performed in triplicate.
(a)
(b)In a different experiment, two fungi species (Aspergillus spp. andFusarium spp.) isolated fromA. thaliana seeds (without disinfection) cultivated were treated with 10 mg/mL of Ag@TiO2 and 10 mg/mL of TiO2-Cu2+ under visible light for 24 h. After that, 10 μL was inoculated and incubated in PD agar. Results indicate radial inhibition of fungal growth in the groups treated with NSMs (Figure 3(b)). The inhibition was calculated measuring diameters of colonies and expressed as radial inhibition percentage (RI%). In the case ofAspergillus spp., RI% was as follows: 35% (Ag@TiO2) and 45% (TiO2-Cu2+). ForFusarium spp., the values encountered for RI% were as follows: 17% (Ag@TiO2) and 34% (TiO2-Cu2+). We observed that copper doped materials show better antimicrobial activity against the fungal species under study, withAspergillus spp. being more sensible to the treatment. Kim and coworkers [26] reported the activity of silver NSMs against several plant pathogenic fungi; an RI% of 100% was observed which is ascribed to metal toxicity. It is important to remark that, in the last decade, caution has been suggested regarding the industrial application of nanosilver formulations, since USEPA (2008) has classified all products containing nanostructured silver as pesticides and also recommended the analysis of their potential risks to human and environmental health [3]. Although the efficiency of these materials is lower regarding growth inhibition of fungi, as previously mentioned, it is worth remarking that these materials are doped with very low amounts of the metal impurity (1 mol%). Thus, it is predicted that TiO2-Cu2+ or Ag@TiO2 at higher dopant concentration should be considered as potential candidates for the treatment of plant pathogenic microorganisms.


### 3.4. Effects onA. thaliana by Exposure to Ag@TiO2 and TiO2-Cu2+

This work aims to elucidate the impact that metal doped NSMs might pose on plants.A. thaliana seeds or seedlings were exposed to metal doped NSMs (Ag@TiO2 or TiO2-Cu2+). After interaction with NSMs, evaluation of plant growth and development ofA. thaliana was investigated. Different sets of experiments were conducted to achieve this goal. First, seeds were exposed for 24 h to different NSMs or metal ions (Ag@TiO2, TiO2-Cu2+, A
g
0, and Cu2+) using different media (distilled water or potassium phosphate buffer pH 5.7). Germination and development of seeds was evaluated. The interaction of NSMs with seeds ofA.thaliana does not affect germination (100%) or their development (Figures 4(a) and 4(b)). A more detailed microscopic analysis of the seeds indicates that Ag@TiO2 and TiO2-Cu2+ are adhered to the seed surface (Figure 4(c)). However, this physical interaction did not interrupt the flow of water inside the seed. Also, it can be inferred that the seed coat acts like a membrane with selective permeability, which protects the embryo from dangerous substances (present in the surrounding medium), preventing the entry of these materials; for that reason, the germination or development of seedlings was not affected. Germination ofA. thaliana seeds was not affected by the exposition media (distilled water or potassium phosphate buffer pH 5.7) used for evaluation of interaction of NSMs with plants.Figure 4
Seeds ofA. thaliana exposed to Ag@TiO2 and TiO2-Cu2+. (a) Seedlings grown in MS agar medium, n
=
10; (b) germinated seeds, n
=
90; (c) NSMs adhered on seeds.
(a)
(b)
(c)Nanosilver formulations and copper salts are currently being used as insecticides or fungicides for plant protection applications. However, the risk assessment of these formulations has been poorly investigated [12]. In this work, the activity of colloidal silver and Cu2+ ions was evaluated since these metals are used as dopants and lately they have been associated with deleterious effects or bioaccumulation in plants [3]. Thus, seeds ofA. thaliana were exposed to commercial formulation of colloidal silver (0.015 mM A
g
0) or to a solution of CuSO4 1 mM. The interaction ofA. thaliana with colloidal silver did not affect the germination of seeds and/or the growth of the seedlings. Metal ions are associated with the toxic effects exerted by metallic nanoparticles (MNPs), since MNPs are insoluble in water and also have a tendency to agglomerate in this medium, which limits the flow of these materials into the plant. However, MNPs are reactive and prone to oxidation, giving rise to the liberation of metal ions into solution. In this study, the concentration of free Ag+ ions was not sufficient to induce changes in germination and/or growth ofA. thaliana (Figures 4(a) and 4(b)). On the other hand, the seeds exposed to 1 mM CuSO4 solution exhibited a total inhibition of germination. The AAS results showed that although exposure medium contains metal ions (Table 2) dissociated from NSMs, H2O (silver 0.06
±
0.003 mg/L; copper 0.24
±
0.03 mg/L), and phosphate buffer pH 5.7 (silver 0.1
±
0.008
m
g
/
L; copper 0.47
±
0.067 mg/L), such amount of metal ions did not produce toxicity inA. thaliana seeds. Meanwhile, seeds exposed to 0.015 mM A
g
0 had normal germination and growth (Figures 4(a) and 4(b)), although silver found in the exposure medium with A
g
0 was ten times more concentrated (0.6
±
0.02 mg/L) than exposure medium with Ag@TiO2 (Table 2). The results reported in this work agree with previous reports that describe inhibition of germination due to the exposure of seeds to high concentrations of Cu2+. For instance, Ivanova and coworkers [32] found that the germination ofBrassica napus L. can be inhibited in the presence of CuSO4 0.3 mM. Later, Sethy and Ghosh [33] suggested that copper prevents water ingress to the seed and affects sucrose metabolism, inhibiting germination.There are more reports on the evaluation of acute toxicity than on the evaluation of chronic toxicity of NSMs towards diverse living organisms. In this work, we evaluated the effect of time of exposure of plants to NSMs. Seeds ofA. thaliana were exposed to NSMs for a time period of a week; in general, seedlings exhibited growth inhibition as a result of interaction with NSMs; also, differences were encountered regarding growth inhibition, depending on the exposition medium (distilled water or MS) ofA. thaliana to NSMs. Results are schematically represented in Figures 5 and 6. Growth inhibition of the treated seedlings is easily observed when compared to control group. Significant differences (with respect to control group) are observed at NSMs concentrations equal to or higher than 2.5 mg/mL, independent of the chemical composition of the material (Ag@TiO2 or TiO2-Cu2+) when the exposition medium is MS (Figures 5(a), 5(b), 6(a), and 6(b)). If exposure medium is distilled water, growth inhibition is dependent on the chemical composition of the material; for instance, TiO2-Cu2+ exert toxic effect at lower concentration (0.5 mg/mL) than Ag@TiO2 (2.5 mg/mL) (Figures 5(c), 5(d), 6(a), and 6(b)). To justify the differences in the toxicity exerted for NSMs under study, AAS was employed to determine the translocation of silver and/or copper into the seedlings. Results are summarized in Table 2. When seedlings were exposed to NSMs for a period of a week using MS as exposure medium, it was observed that seedlings exposed to Ag@TiO2 accumulate higher amount of silver (0.58 mg/g of tissue) in comparison to control group (0 mg/g of tissue) or the group exposed to colloidal silver (0.2 mg/g of tissue). Although the total amount of silver in the colloidal solution is higher than the one encountered in Ag@TiO2 NSMs, it is likely that the particle size of colloidal solution is bigger; also, particles might agglomerate or precipitate from the medium, reducing the bioavailability of the metal. In the case of Ag@TiO2 materials, silver nanoparticles are very small but are supported on the TiO2 matrix; thus, the leaching of Ag+ ions is controlled, resulting in a higher bioavailability. From Figure 6(a), we can see that seedlings exposed to Ag@TiO2 (2.5 mg of NSMs/mL) showed an elongation of 0.45 cm versus the elongation observed for the seedlings exposed to colloidal silver which was encountered to be 0.61 cm. From here we can see that toxicity (growth inhibition) of NSMs is directly related to the amount of free Ag+ ions, in accordance with results published in literature [34].Figure 5
Seedlings ofA. thaliana exposed to NSMs. (a) Ag@TiO2 and (b) TiO2-Cu2+ in MS broth medium for a week; (c) Ag@TiO2 and (d) TiO2-Cu2+ in H2O for a week; (e) Ag@TiO2 and (f) TiO2-Cu2+ in H2O, radiated for 24 h; (g) Ag@TiO2 and (h) TiO2-Cu2+ in H2O, nonradiated for 24 h. Numbers indicate NSMs concentrations (0, 0.5 1, 2.5, 5, and 10 mg/mL).
(a)
(b)
(c)
(d)
(e)
(f)
(g)
(h)Figure 6
Seedlings elongation after exposure to NSMs: (a) Ag@TiO2 and (b) TiO2-Cu2+. Columns represent the mean and the bars represent ± one standard deviation; n
=
10.
(a)
(b)As previously discussed, copper is an essential element in plants but the redox properties of this element also contribute to its inherent toxicity. The amount of copper in seedlings exposed to 1 mg/mL of TiO2-Cu2+ for a week in MS was determined by AAS, and it was found to be 0.29 mg/g of tissue, while the average content of Cu in plant tissue has been reported as 6 μg/g dry weight (Table 2) [35]. Leaching of copper ions from the material was also determined by means of AAS, after interaction with biological samples. It was observed that the amount of residual Cu2+ is higher in MS medium than the amount of Cu2+ encountered in distilled water. On the contrary, biological samples exposed to NSMs in MS medium contain less amount of copper than samples exposed to NSMs using distilled water. The bioavailability of Cu2+ ion in the presence of EDTA contained in MS medium is reduced due to the formation of metal complexes. EDTA is added to MS medium in order to form Fe2+-EDTA complexes (log
⁡
K
f
=
14.3) and avoid iron precipitation [36]. Since EDTA is a good metal chelator, it can also form complexes with Cu2+ (log
⁡
K
f
=
18.8); thus, as Cu2+ ion leaches from TiO2-Cu2+ material, it is complexed and thereby its bioavailability reduced. In summary, for seedlings exposed to NSMs using water as medium for exposition, the amount of copper translocated into the plant was higher than the one encountered for seedlings exposed in MS medium (Table 2). Also, the toxicity of Cu2+ ions (growth inhibition) is clearly observed when plants are exposed using distilled water as exposure medium (Figure 6(b)).In a different experiment, two-day-old seedlings were exposed to NSMs suspended in distilled water (Treatment 3, Table1) for a day. Results are summarized and schematically represented in Figures 5(e), 5(f), 5(g), 5(h), and 6. Dose-response experiments indicate that the interaction ofA. thaliana seedlings with Ag@TiO2 favors seedling growth at concentrations ≤ 2.5 mg/mL under visible light for a period of 24 h (Figures 5(e) and 6(a)). Treated seedlings under these conditions showed larger growth (with a length of 2
±
0.5 cm) than seedlings without interaction with NSMs (with a length of 1.3
±
0.3 cm) (Figures 5(e) and 6(a)). Beneficial effects due to the interaction of plants with silver NSMs and/or TiO2 materials have been previously reported. For instance, Shams and coworkers [37] reported an improvement in the development of cucumber due to its interaction with Ag NSMs. Silver doped titanium dioxide can be activated under visible light radiation generating e−/h+ reactive species that interact with molecular oxygen and/or water to produce reactive oxygen species (ROS), particularly the hydroxyl radical (HO·), a very strong oxidizing agent that has been associated with participating in the loosening of the plant cell wall, resulting in root elongation [38]. On the other hand, deleterious effects due to the interaction of Ag NSMs with plants have been reported. For instance, Wang and coworkers [34] reported stimulatory effect on root elongation, fresh weight, and evapotranspiration of poplars andA. thaliana when exposed to low concentrations of Ag NSMs, whereas Ag NSMs were phytotoxic above specific concentrations. Phytostimulation (seedling elongation) ofA. thaliana due to the interaction with Ag@TiO2 at low concentrations (0.5, 1, and 2.5 mg/mL) was observed. However, at higher concentrations (≥5 mg/mL) stimulatory effect was not observed (Figures 5(e) and 6(a)). The synergistic activity of the composite material was demonstrated, since there are no significant differences in elongation (in comparison to control group) ofA. thaliana when exposed to Ag@TiO2 without radiation (Figures 5(g) and 6(a)).In a related experiment, two-day-old seedlings exposed to TiO2-Cu2+ for 24 h (Treatment 3, Table 1) were measured 4 days after exposure. Seedlings exposed to NSMs showed lower elongation than control group seedlings (Figures 5(f), 5(h), and 6(b)). The difference of elongation was significant at concentrations higher than 0.5 mg/mL under visible light and 5 mg/mL in the dark (Figure 6(b)). Those results showed that visible light potentiates TiO2-Cu2+ effect onA. thaliana, probably because plant stress is higher in those conditions. This result may be due to the photocatalytic activity of the material that generates ROS which are responsible for oxidative stress in diverse living organisms. Also, liberation of Cu2+ ions into solution is favored as a result of the photoactivation of the catalyst [39]. Previous reports associate stress with a greater production of ethylene, which limits root elongation [35]. Seedlings treated with CuSO4 showed less elongation too (Figures 5(f), 5(h), and 6(b)); that effect has been known for some time; although copper has important functions (e.g., cofactor of cytochrome oxidase enzyme), copper rapidly becomes toxic in liquid plant cultures [35]. Copper has affinity for sulfhydryl groups in membranes which induce lipoperoxidation, producing damage in cell membrane or free radicals, and lower permeability of root cells [40]. To determine the amount of leached copper, exposure media and plants exposed to TiO2-Cu2+ were analyzed by atomic absorption spectrometry. Copper was found in water medium exposed for 24 h to TiO2-Cu2+ (0.2
±
0.03 mg/L); in water medium without NSMs, the amount of copper was 0.1
±
0.05 mg/L (Table 2), which indicates that copper was dissociated from NSMs. Copper content in seedlings was higher in those exposed to TiO2-Cu2+ (0.3
±
0.03 mg/g of tissue) than in those that were not exposed (0.1
±
0.01 mg/g) (Table 2), which suggests that copper participates in the observed deleterious effects (Figures 5(f) and 5(h)).


### 3.5. Total Chlorophyll and Anthocyanin Content

Total chlorophyll content was measured to analyze the effect of NSMs on the production of photosynthetic pigment in seedlings ofA. thaliana. Seedlings exposed to 1 mg/mL of NSMs in MS for a week showed increased production of chlorophyll; the values were 1.8
±
0.3 mg/g of tissue for Ag@TiO2, 1.6
±
0.08 mg/g for TiO2-Cu2+, and 1
±
0.2 mg/g for negative control (seedlings that were not exposed to NSMs) (Figure 7(a)). However, seedlings exposed to 2.5 mg/mL of NSMs for a week suffer a reduction to 0.3
±
0.02 mg/g of total chlorophyll for both NSMs (Figures 7(a) and 7(b)). Regarding positive controls, the chlorophyll content of seedlings exposed for a week to Ag0 was 0.7
±
0.15 mg/g and CuSO4  0.01
±
0.001 mg/g. In another experiment, seedlings exposed for 24 h did not show significant differences in the total chlorophyll content of the seedlings in some conditions: (a) 1 mg/mL of Ag@TiO2 (1.4
±
0.36 mg/g), (b) 1 mg/mL of TiO2-Cu2+ (1.4
±
0.37 mg/g), (c) A
g
0 (1.3
±
0.24 mg/g), and (d) negative control without NSMs (1.2
±
0.35 mg/g) (Figures 7(a) and 7(b)). However, in different conditions the total chlorophyll content was lower than in negative control, for example, in seedlings exposed to 5 mg/mg of Ag@TiO2 (0.5
±
0.07 mg/g of tissue), 5 mg/mL of TiO2-Cu2+ (0.4
±
0.14 mg/g of tissue), and CuSO4 (0.3
±
0.02 mg/g of tissue) (Figures 7(a) and 7(b)).Figure 7
Total chlorophyll and anthocyanin content. Total chlorophyll content (mg/g of tissue) in seedling exposed to (a) Ag@TiO2 and (b) TiO2-Cu2+; anthocyanin content (relative units of anthocyanin (RUA)/g of tissue) in seedlings exposed to (c) Ag@TiO2 and (d) TiO2-Cu2+; columns represent the mean and the bars represent ± one standard deviation; n
=
3.
(a)
(b)
(c)
(d)There are some reports that indicate an increase in the amount of chlorophyll in plants upon exposition to TiO2 NSMs; for instance, Morteza and coworkers [41] suggested that exposition ofZea mays L., in reproductive stage, to TiO2 NSMs contributes to stabilizing the integrity of the chloroplast membrane, protecting chlorophyll. Although other studies report a decrease of chlorophyll content, for example, Nair and Chung suggest that seedlings ofOryza sativa L. exposed to silver NSMs [28] and seedlings ofBrassica juncea L. exposed to copper oxide NSMs [42] showed a reduction of total chlorophyll content due to damage caused to chloroplast membranes as a result of lipid peroxidation by oxidative stress produced by the excess of metal or as result of depletion of iron (Fe) by copper or due to reduced biomass.To examine the impact of NSM inA. thaliana, the anthocyanin content was measured. Anthocyanins are flavonoids that are responsible for coloration in flowers and fruits of higher plants. They are pigments with protective functions against UV radiation; ROS, microorganisms, and the total amount of anthocyanin in plants can change due to some type of stress [43]. Seedling exposed to lower concentrations of NSMs in MS for a week does not show significant differences into the anthocyanin with respect to control group without NSMs (1.4
±
0.4 relative units of anthocyanin per gram of tissue (RUA/g)), for example, (a) 0.5 mg/mL of TiO2-Cu2+ (1.3
±
0.1 RUA/g) and (b) 1 mg/mL of Ag@TiO2 (1.3
±
0.3 RUA/g) (Figures 7(c) and 7(d)); but the anthocyanin content was increased in seedling exposed to 2.5 mg/mL and higher concentration of Ag@TiO2 (4.4
±
0.3 RUA/g). The anthocyanin content in seedlings exposed for 24 h was significantly higher with respect to negative control (0.67
±
0.14 RUA/g) in some conditions, for example, in seedlings exposed to 5 mg/mL of Ag@TiO2 (1.4
±
0.05 RUA/g) and 2.5 mg/mL of TiO2-Cu2+ (1.2
±
0.2 RUA/g) (Figures 7(c) and 7(d)). Syu and coworkers [44] suggest that the increase of anthocyanin content inA. thaliana is due to oxidative stress produced by exposition to Ag NSM and NSMs studied in the present work produce ROS and metal (Ag and Cu) is leached by the materials, which could cause oxidative stress stimulating the anthocyanin production.


## 3.1. Synthesis and Characterization of Ag@TiO2 and TiO2-Cu2+

The synthesis of Ag@TiO2 and TiO2-Cu2+ nanostructured materials was achieved using an environmentally friendly sol-gel procedure. The amount of silver or copper into the materials was formulated to be 1% (mol/mol; Ag/Ti or Cu2+/Ti). Results of analysis of Ag@TiO2 composites by SEM-EDX indicate that the TiO2 is spherical with a mean size diameter of ~10 nm (Figure 1(a)). Silver nanoparticles show a mean diameter smaller than 10 nm; thus, it was not possible to determine their mean size by SEM analysis. EDX analysis demonstrates the existence of Ti, O, and Ag in accordance with the molar ratio of the formulation (Figure 1(b)). SEM analysis of TiO2-Cu2+ also indicates a spherical shape and mean size of ~10 nm (Figure 1(c)). The presence of Ti, O, and Cu in the appropriate mole ratio was demonstrated by EDX data (Figure 1(d)). The materials were obtained as crystalline nanostructured powders after thermal annealing at 350°C. The materials exhibit anatase crystalline structure.Figure 1
Characterization of NSMs. (a) SEM image of Ag@TiO2. (b) Elemental composition of Ag@TiO2 (EDX). (c) SEM image of TiO2-Cu2+. (d) Elemental composition of TiO2-Cu2+ (EDX).
(a)
(b)
(c)
(d)The aggregation state of NSMs is a critical factor for experimentally assessing their toxic activity. It is well known that independent of the primary particle size (as solid state materials) NSMs tend to agglomerate when suspended in different media. The biological components present in the culture media and electrolytes may interact with NSMs to change their physicochemical properties (i.e., modification of surface properties) and aggregation state. The stability of these materials was evaluated using TiO2 (Sigma-Aldrich) as control. Dynamic light scattering analysis of the materials suspended in distilled water or Physiological Saline Solution (PSS) was performed and these results indicate that the materials form bigger aggregates in saline solution than in distilled water. The hydrodynamic radio of the materials is 477 nm (TiO2), 467 nm (Ag@TiO2), and 360 nm (TiO2-Cu2+) when suspended in distilled water. For the suspensions in PSS, the agglomerates exhibit a mean size of 774 nm (TiO2), 776 nm (Ag@TiO2), and 750 nm (TiO2-Cu2+). Zeta potential of the suspension was also evaluated. For distilled water suspensions, the following zeta potential values were encountered: +10.39 mV (TiO2), −27.83 mV (Ag@TiO2), and +14.73 mV (TiO2-Cu2+). In the case of PSS suspensions, the following results were encountered: +48.01 mV (TiO2), +81.94 mV (Ag@TiO2), and +6.85 mV (TiO2-Cu2+). The studied materials present a positive surface charge when suspended in PSS. It has been reported that positively charged nanoparticles interact more strongly with biomolecules due to favored electrostatic interactions since at physiological pH value biomolecules are negatively charged, thus facilitating interaction of NSMs and biomolecules.


## 3.2. Antimicrobial Activity of Ag@TiO2 and TiO2-Cu2+ inE. coli andS. cerevisiae

Two sets of inactivation kinetics assays (under visible light and in the dark) were conducted to evaluate theE. coli inactivation rate (Figures 2(a) and 2(b)). The results obtained indicate that Ag@TiO2 exerted strong bacterial inactivation (3 U log) in a short time period (2 h with 10 mg/mL of NSMs). It was also observed that lower amounts of NSMs exhibit longer inhibition times: 2.2 U log with 0.5 mg/mL at 4 h and 2.9 U log with 1 mg/mL at 4 h (Figure 2(a)). There are no significant differences for inactivation rate and extent of inactivation when assays are performed under radiation or in the dark (Figures 2(a) and 2(b)), which indicates that the principal mechanism for inactivation is the release of Ag+ ions from Ag@TiO2 materials [8, 29]. There is no inactivation ofE. coli growth as a consequence of exposure to visible light radiation. Colloidal silver inhibited bacteria growth with 6 U log at 2 h (Figures 2(a) and 2(b)). Although the inactivation rate of colloidal silver is higher than the one observed for Ag@TiO2 composites, both materials exerted efficient bactericidal effect.Figure 2
Inactivation of microorganisms by NSMs:E. coli with Ag@TiO2 (a) under visible light and (b) in dark;S. cerevisiae with Ag@TiO2 (c) under visible light and (d) in dark; (e)E. coli with TiO2-Cu2+; (f)S. cerevisiae with TiO2-Cu2+. As positive control, Ag0 for Ag@TiO2 and CuSO4 for TiO2-Cu2+. Bars represent standard deviation; each treatment was performed in triplicate.
(a)
(b)
(c)
(d)
(e)
(f)In general,S. cerevisiae was more resistant thanE. coli to colloidal silver and Ag@TiO2 NSMs microbicidal activity (Figures 2(c) and 2(d)). Longer exposure times at high concentrations of NSMs were necessary to achieve a good inhibition ofS. cerevisiae growth, with a maximum inactivation of 2.6 U log with 10 mg/mL under visible light after 24 h (Figure 2(c)). The tolerance observed by yeast to the microbicidal activity of Ag NSMs is due to the more complex structure (the presence of a cell wall, composed of beta-glucans, chitin, and mannoproteins, limits the passage of Ag+ ion) of these microorganisms [30]. When the variable under study was light radiation, slight differences were observed for the inhibition ofS. cerevisiae with Ag@TiO2, with 1.9 U log with 10 mg/mL, in dark after 24 h (Figure 2(d)). ForE. coli, an inhibition growth mechanism based on Ag+ activity was suggested since no enhancement in the rate or extent of inactivation was observed when the assay was conducted under visible light radiation. In accordance with several previously published reports, metal doped TiO2 NSMs, when activated with visible light, generate reactive oxygen species (ROS) that are associated with cell damage in microorganisms [7, 31]. For the growth inhibition ofS. cerevisiae, the effect of ROS is more significant since the components of the cell wall can be susceptible to oxidation.The TiO2-Cu2 antimicrobial activity was evaluated under the same conditions reported for Ag@TiO2 materials. Regarding highE. coli densities (106 CFU/mL), TiO2-Cu2+ NSMs did not show bactericidal activity even at the highest concentration (10 mg/mL) (Figure 2(e)). As observed for silver based materials, the activity of TiO2-Cu2+ againstE. coli depends on the amount of metal ions liberated into solution; however, since the microbicidal activity of silver is higher in comparison to copper, larger amounts of Cu2+ must be released to achieve bacterial inactivation [8, 12]. By comparing the effect of colloidal silver and copper sulfate solution, inactivation rate and extent of inactivation are lower for copper sulfate, corroborating that higher concentrations of this ion are required to achieve inactivation of elevated microbial densities (106 CFU/mL). Nonradiated samples did not show inhibitory effect.In the evaluation of the growth inhibition forS. cerevisiae using TiO2-Cu2+ materials, results indicate similar behavior to Ag@TiO2; the viability ofS. cerevisiae diminished as a function of material concentration, time of exposure, and visible light radiation. The maximum inactivation was of 1.9 U log with 10 mg/mL after 24 h (Figure 2(f)).It has been postulated that the microbicidal activity of Ag@TiO2 is proportional to the amount of silver ions released into the medium [8, 29]. To correlate the activity of the NSMs under investigation to their liberation of metal ions into solution, supernatants of the exposition medium were analyzed by AAS. Reported results indicate the presence of silver at a concentration of 0.16 ppm in the exposure medium (phosphate buffer pH 7; Table 2). Copper was also found in the exposition medium (Table 2) at very low concentration (0.5 ppm). Although the amount of Cu2+ released into the medium is higher in comparison to released Ag+, better performance of silver based materials is achieved due to enhanced microbicidal activity of Ag+.Table 2
Determination of copper and silver by atomic absorption spectrophotometry.
⁢Seedling treated in MS for a weeka
⁢Seedling treated in H2O for 24 ha
NSMs
(Ag) mg/g
(Cu) mg/g
(Ag) mg/g
(Cu) mg/g
Ag@TiO2
0.58 ± 0.03
—
0.23 ± 0.23
—
TiO2-Cu2+
—
0.29 ± 0.06
—
0.31 ± 0.03
Ag0
0.2 ± 0.05
—
0.12 ± 0.01
—
Control (−)
0
0.12 ± 0.016
0
0.13 ± 0.01
⁢MS medium after a weekb
⁢H2O after a weekb
NSMs
(Ag) ppm
(Cu) ppm
(Ag) ppm
(Cu) ppm
Ag@TiO2
0.17 ± 0.01
—
0
—
TiO2-Cu2+
—
3.17 ± 0.148
—
0.08 ± 0.02
Ag0
0.085 ± 0.03
—
0.47 ± 0.01
—
Control (−)
0
0.11 ± 0.05
0
0.04 ± 0.002
H2O after 24 hb
⁢Phosphate buffer pH 5.7 after 24 hb
NSMs
(Ag) ppm
(Cu) ppm
(Ag) ppm
(Cu) ppm
Ag@TiO2
0.06 ± 0.003
—
0.1 ± 0.01
—
TiO2-Cu2+
—
0.25 ± 0.03
—
0.47 ± 0.07
Ag0
0.63 ± 0.02
—
0.25 ± 0.02
—
Control (−)
0
0.11 ± 0.05
0
0.03 ± 0.001
⁢Phosphate buffer pH 7 after 24 hc
NSMs
(Ag) ppm
(Cu) ppm
Ag@TiO2
0.16 ± 0.02
—
TiO2-Cu2+
—
0.5 ± 0.01
Ag0
0.2 ± 0.04
—
Control (−)
0
0.1 ± 0.03
aSeedling treated, bexposure medium of seedlings, and cexposure medium of microorganisms with 1 mg/mL of Ag@TiO2, 1 mg/mL of TiO2-Cu2+, and 0.015 mM Ag0.


## 3.3. Activity of Ag@TiO2 and TiO2-Cu2+ in Seed Disinfection

Several experiments were conducted to assess Ag@TiO2 and TiO2-Cu2+ use as disinfectants for axenic conditions.A. thaliana seeds were treated with 10 mg/mL of NSMs for 24 h and then cultured in MS agar medium. Results are summarized in Figure 3(a) and indicate that total seed disinfection was not observed with this treatment. Although inhibition of microbial growth was observed for the samples treated with NSMs, the activity of the materials is insufficient forin vitro culture of seeds (Ag@TiO2: 72% inhibition; TiO2-Cu2+: 36% inhibition; control: 41% inhibition). It is important to remark that the materials show good microbicidal activity when they are evaluated using a single microorganisms species (i.e.,E. coli orS. cerevisiae); however, when the materials are exposed to microorganisms consortiums, the activity of the materials seems to be diminished.Figure 3
Seeds and their contaminants treated with Ag@TiO2 and TiO2-Cu2+. (a) Treatment ofA. thaliana seeds with 10 mg/mL of NSMs prior to cultivationin vitro; (b) fungal contaminants seeds exposed to 10 mg/mL of NSMs; each treatment was performed in triplicate.
(a)
(b)In a different experiment, two fungi species (Aspergillus spp. andFusarium spp.) isolated fromA. thaliana seeds (without disinfection) cultivated were treated with 10 mg/mL of Ag@TiO2 and 10 mg/mL of TiO2-Cu2+ under visible light for 24 h. After that, 10 μL was inoculated and incubated in PD agar. Results indicate radial inhibition of fungal growth in the groups treated with NSMs (Figure 3(b)). The inhibition was calculated measuring diameters of colonies and expressed as radial inhibition percentage (RI%). In the case ofAspergillus spp., RI% was as follows: 35% (Ag@TiO2) and 45% (TiO2-Cu2+). ForFusarium spp., the values encountered for RI% were as follows: 17% (Ag@TiO2) and 34% (TiO2-Cu2+). We observed that copper doped materials show better antimicrobial activity against the fungal species under study, withAspergillus spp. being more sensible to the treatment. Kim and coworkers [26] reported the activity of silver NSMs against several plant pathogenic fungi; an RI% of 100% was observed which is ascribed to metal toxicity. It is important to remark that, in the last decade, caution has been suggested regarding the industrial application of nanosilver formulations, since USEPA (2008) has classified all products containing nanostructured silver as pesticides and also recommended the analysis of their potential risks to human and environmental health [3]. Although the efficiency of these materials is lower regarding growth inhibition of fungi, as previously mentioned, it is worth remarking that these materials are doped with very low amounts of the metal impurity (1 mol%). Thus, it is predicted that TiO2-Cu2+ or Ag@TiO2 at higher dopant concentration should be considered as potential candidates for the treatment of plant pathogenic microorganisms.


## 3.4. Effects onA. thaliana by Exposure to Ag@TiO2 and TiO2-Cu2+

This work aims to elucidate the impact that metal doped NSMs might pose on plants.A. thaliana seeds or seedlings were exposed to metal doped NSMs (Ag@TiO2 or TiO2-Cu2+). After interaction with NSMs, evaluation of plant growth and development ofA. thaliana was investigated. Different sets of experiments were conducted to achieve this goal. First, seeds were exposed for 24 h to different NSMs or metal ions (Ag@TiO2, TiO2-Cu2+, A
g
0, and Cu2+) using different media (distilled water or potassium phosphate buffer pH 5.7). Germination and development of seeds was evaluated. The interaction of NSMs with seeds ofA.thaliana does not affect germination (100%) or their development (Figures 4(a) and 4(b)). A more detailed microscopic analysis of the seeds indicates that Ag@TiO2 and TiO2-Cu2+ are adhered to the seed surface (Figure 4(c)). However, this physical interaction did not interrupt the flow of water inside the seed. Also, it can be inferred that the seed coat acts like a membrane with selective permeability, which protects the embryo from dangerous substances (present in the surrounding medium), preventing the entry of these materials; for that reason, the germination or development of seedlings was not affected. Germination ofA. thaliana seeds was not affected by the exposition media (distilled water or potassium phosphate buffer pH 5.7) used for evaluation of interaction of NSMs with plants.Figure 4
Seeds ofA. thaliana exposed to Ag@TiO2 and TiO2-Cu2+. (a) Seedlings grown in MS agar medium, n
=
10; (b) germinated seeds, n
=
90; (c) NSMs adhered on seeds.
(a)
(b)
(c)Nanosilver formulations and copper salts are currently being used as insecticides or fungicides for plant protection applications. However, the risk assessment of these formulations has been poorly investigated [12]. In this work, the activity of colloidal silver and Cu2+ ions was evaluated since these metals are used as dopants and lately they have been associated with deleterious effects or bioaccumulation in plants [3]. Thus, seeds ofA. thaliana were exposed to commercial formulation of colloidal silver (0.015 mM A
g
0) or to a solution of CuSO4 1 mM. The interaction ofA. thaliana with colloidal silver did not affect the germination of seeds and/or the growth of the seedlings. Metal ions are associated with the toxic effects exerted by metallic nanoparticles (MNPs), since MNPs are insoluble in water and also have a tendency to agglomerate in this medium, which limits the flow of these materials into the plant. However, MNPs are reactive and prone to oxidation, giving rise to the liberation of metal ions into solution. In this study, the concentration of free Ag+ ions was not sufficient to induce changes in germination and/or growth ofA. thaliana (Figures 4(a) and 4(b)). On the other hand, the seeds exposed to 1 mM CuSO4 solution exhibited a total inhibition of germination. The AAS results showed that although exposure medium contains metal ions (Table 2) dissociated from NSMs, H2O (silver 0.06
±
0.003 mg/L; copper 0.24
±
0.03 mg/L), and phosphate buffer pH 5.7 (silver 0.1
±
0.008
m
g
/
L; copper 0.47
±
0.067 mg/L), such amount of metal ions did not produce toxicity inA. thaliana seeds. Meanwhile, seeds exposed to 0.015 mM A
g
0 had normal germination and growth (Figures 4(a) and 4(b)), although silver found in the exposure medium with A
g
0 was ten times more concentrated (0.6
±
0.02 mg/L) than exposure medium with Ag@TiO2 (Table 2). The results reported in this work agree with previous reports that describe inhibition of germination due to the exposure of seeds to high concentrations of Cu2+. For instance, Ivanova and coworkers [32] found that the germination ofBrassica napus L. can be inhibited in the presence of CuSO4 0.3 mM. Later, Sethy and Ghosh [33] suggested that copper prevents water ingress to the seed and affects sucrose metabolism, inhibiting germination.There are more reports on the evaluation of acute toxicity than on the evaluation of chronic toxicity of NSMs towards diverse living organisms. In this work, we evaluated the effect of time of exposure of plants to NSMs. Seeds ofA. thaliana were exposed to NSMs for a time period of a week; in general, seedlings exhibited growth inhibition as a result of interaction with NSMs; also, differences were encountered regarding growth inhibition, depending on the exposition medium (distilled water or MS) ofA. thaliana to NSMs. Results are schematically represented in Figures 5 and 6. Growth inhibition of the treated seedlings is easily observed when compared to control group. Significant differences (with respect to control group) are observed at NSMs concentrations equal to or higher than 2.5 mg/mL, independent of the chemical composition of the material (Ag@TiO2 or TiO2-Cu2+) when the exposition medium is MS (Figures 5(a), 5(b), 6(a), and 6(b)). If exposure medium is distilled water, growth inhibition is dependent on the chemical composition of the material; for instance, TiO2-Cu2+ exert toxic effect at lower concentration (0.5 mg/mL) than Ag@TiO2 (2.5 mg/mL) (Figures 5(c), 5(d), 6(a), and 6(b)). To justify the differences in the toxicity exerted for NSMs under study, AAS was employed to determine the translocation of silver and/or copper into the seedlings. Results are summarized in Table 2. When seedlings were exposed to NSMs for a period of a week using MS as exposure medium, it was observed that seedlings exposed to Ag@TiO2 accumulate higher amount of silver (0.58 mg/g of tissue) in comparison to control group (0 mg/g of tissue) or the group exposed to colloidal silver (0.2 mg/g of tissue). Although the total amount of silver in the colloidal solution is higher than the one encountered in Ag@TiO2 NSMs, it is likely that the particle size of colloidal solution is bigger; also, particles might agglomerate or precipitate from the medium, reducing the bioavailability of the metal. In the case of Ag@TiO2 materials, silver nanoparticles are very small but are supported on the TiO2 matrix; thus, the leaching of Ag+ ions is controlled, resulting in a higher bioavailability. From Figure 6(a), we can see that seedlings exposed to Ag@TiO2 (2.5 mg of NSMs/mL) showed an elongation of 0.45 cm versus the elongation observed for the seedlings exposed to colloidal silver which was encountered to be 0.61 cm. From here we can see that toxicity (growth inhibition) of NSMs is directly related to the amount of free Ag+ ions, in accordance with results published in literature [34].Figure 5
Seedlings ofA. thaliana exposed to NSMs. (a) Ag@TiO2 and (b) TiO2-Cu2+ in MS broth medium for a week; (c) Ag@TiO2 and (d) TiO2-Cu2+ in H2O for a week; (e) Ag@TiO2 and (f) TiO2-Cu2+ in H2O, radiated for 24 h; (g) Ag@TiO2 and (h) TiO2-Cu2+ in H2O, nonradiated for 24 h. Numbers indicate NSMs concentrations (0, 0.5 1, 2.5, 5, and 10 mg/mL).
(a)
(b)
(c)
(d)
(e)
(f)
(g)
(h)Figure 6
Seedlings elongation after exposure to NSMs: (a) Ag@TiO2 and (b) TiO2-Cu2+. Columns represent the mean and the bars represent ± one standard deviation; n
=
10.
(a)
(b)As previously discussed, copper is an essential element in plants but the redox properties of this element also contribute to its inherent toxicity. The amount of copper in seedlings exposed to 1 mg/mL of TiO2-Cu2+ for a week in MS was determined by AAS, and it was found to be 0.29 mg/g of tissue, while the average content of Cu in plant tissue has been reported as 6 μg/g dry weight (Table 2) [35]. Leaching of copper ions from the material was also determined by means of AAS, after interaction with biological samples. It was observed that the amount of residual Cu2+ is higher in MS medium than the amount of Cu2+ encountered in distilled water. On the contrary, biological samples exposed to NSMs in MS medium contain less amount of copper than samples exposed to NSMs using distilled water. The bioavailability of Cu2+ ion in the presence of EDTA contained in MS medium is reduced due to the formation of metal complexes. EDTA is added to MS medium in order to form Fe2+-EDTA complexes (log
⁡
K
f
=
14.3) and avoid iron precipitation [36]. Since EDTA is a good metal chelator, it can also form complexes with Cu2+ (log
⁡
K
f
=
18.8); thus, as Cu2+ ion leaches from TiO2-Cu2+ material, it is complexed and thereby its bioavailability reduced. In summary, for seedlings exposed to NSMs using water as medium for exposition, the amount of copper translocated into the plant was higher than the one encountered for seedlings exposed in MS medium (Table 2). Also, the toxicity of Cu2+ ions (growth inhibition) is clearly observed when plants are exposed using distilled water as exposure medium (Figure 6(b)).In a different experiment, two-day-old seedlings were exposed to NSMs suspended in distilled water (Treatment 3, Table1) for a day. Results are summarized and schematically represented in Figures 5(e), 5(f), 5(g), 5(h), and 6. Dose-response experiments indicate that the interaction ofA. thaliana seedlings with Ag@TiO2 favors seedling growth at concentrations ≤ 2.5 mg/mL under visible light for a period of 24 h (Figures 5(e) and 6(a)). Treated seedlings under these conditions showed larger growth (with a length of 2
±
0.5 cm) than seedlings without interaction with NSMs (with a length of 1.3
±
0.3 cm) (Figures 5(e) and 6(a)). Beneficial effects due to the interaction of plants with silver NSMs and/or TiO2 materials have been previously reported. For instance, Shams and coworkers [37] reported an improvement in the development of cucumber due to its interaction with Ag NSMs. Silver doped titanium dioxide can be activated under visible light radiation generating e−/h+ reactive species that interact with molecular oxygen and/or water to produce reactive oxygen species (ROS), particularly the hydroxyl radical (HO·), a very strong oxidizing agent that has been associated with participating in the loosening of the plant cell wall, resulting in root elongation [38]. On the other hand, deleterious effects due to the interaction of Ag NSMs with plants have been reported. For instance, Wang and coworkers [34] reported stimulatory effect on root elongation, fresh weight, and evapotranspiration of poplars andA. thaliana when exposed to low concentrations of Ag NSMs, whereas Ag NSMs were phytotoxic above specific concentrations. Phytostimulation (seedling elongation) ofA. thaliana due to the interaction with Ag@TiO2 at low concentrations (0.5, 1, and 2.5 mg/mL) was observed. However, at higher concentrations (≥5 mg/mL) stimulatory effect was not observed (Figures 5(e) and 6(a)). The synergistic activity of the composite material was demonstrated, since there are no significant differences in elongation (in comparison to control group) ofA. thaliana when exposed to Ag@TiO2 without radiation (Figures 5(g) and 6(a)).In a related experiment, two-day-old seedlings exposed to TiO2-Cu2+ for 24 h (Treatment 3, Table 1) were measured 4 days after exposure. Seedlings exposed to NSMs showed lower elongation than control group seedlings (Figures 5(f), 5(h), and 6(b)). The difference of elongation was significant at concentrations higher than 0.5 mg/mL under visible light and 5 mg/mL in the dark (Figure 6(b)). Those results showed that visible light potentiates TiO2-Cu2+ effect onA. thaliana, probably because plant stress is higher in those conditions. This result may be due to the photocatalytic activity of the material that generates ROS which are responsible for oxidative stress in diverse living organisms. Also, liberation of Cu2+ ions into solution is favored as a result of the photoactivation of the catalyst [39]. Previous reports associate stress with a greater production of ethylene, which limits root elongation [35]. Seedlings treated with CuSO4 showed less elongation too (Figures 5(f), 5(h), and 6(b)); that effect has been known for some time; although copper has important functions (e.g., cofactor of cytochrome oxidase enzyme), copper rapidly becomes toxic in liquid plant cultures [35]. Copper has affinity for sulfhydryl groups in membranes which induce lipoperoxidation, producing damage in cell membrane or free radicals, and lower permeability of root cells [40]. To determine the amount of leached copper, exposure media and plants exposed to TiO2-Cu2+ were analyzed by atomic absorption spectrometry. Copper was found in water medium exposed for 24 h to TiO2-Cu2+ (0.2
±
0.03 mg/L); in water medium without NSMs, the amount of copper was 0.1
±
0.05 mg/L (Table 2), which indicates that copper was dissociated from NSMs. Copper content in seedlings was higher in those exposed to TiO2-Cu2+ (0.3
±
0.03 mg/g of tissue) than in those that were not exposed (0.1
±
0.01 mg/g) (Table 2), which suggests that copper participates in the observed deleterious effects (Figures 5(f) and 5(h)).


## 3.5. Total Chlorophyll and Anthocyanin Content

Total chlorophyll content was measured to analyze the effect of NSMs on the production of photosynthetic pigment in seedlings ofA. thaliana. Seedlings exposed to 1 mg/mL of NSMs in MS for a week showed increased production of chlorophyll; the values were 1.8
±
0.3 mg/g of tissue for Ag@TiO2, 1.6
±
0.08 mg/g for TiO2-Cu2+, and 1
±
0.2 mg/g for negative control (seedlings that were not exposed to NSMs) (Figure 7(a)). However, seedlings exposed to 2.5 mg/mL of NSMs for a week suffer a reduction to 0.3
±
0.02 mg/g of total chlorophyll for both NSMs (Figures 7(a) and 7(b)). Regarding positive controls, the chlorophyll content of seedlings exposed for a week to Ag0 was 0.7
±
0.15 mg/g and CuSO4  0.01
±
0.001 mg/g. In another experiment, seedlings exposed for 24 h did not show significant differences in the total chlorophyll content of the seedlings in some conditions: (a) 1 mg/mL of Ag@TiO2 (1.4
±
0.36 mg/g), (b) 1 mg/mL of TiO2-Cu2+ (1.4
±
0.37 mg/g), (c) A
g
0 (1.3
±
0.24 mg/g), and (d) negative control without NSMs (1.2
±
0.35 mg/g) (Figures 7(a) and 7(b)). However, in different conditions the total chlorophyll content was lower than in negative control, for example, in seedlings exposed to 5 mg/mg of Ag@TiO2 (0.5
±
0.07 mg/g of tissue), 5 mg/mL of TiO2-Cu2+ (0.4
±
0.14 mg/g of tissue), and CuSO4 (0.3
±
0.02 mg/g of tissue) (Figures 7(a) and 7(b)).Figure 7
Total chlorophyll and anthocyanin content. Total chlorophyll content (mg/g of tissue) in seedling exposed to (a) Ag@TiO2 and (b) TiO2-Cu2+; anthocyanin content (relative units of anthocyanin (RUA)/g of tissue) in seedlings exposed to (c) Ag@TiO2 and (d) TiO2-Cu2+; columns represent the mean and the bars represent ± one standard deviation; n
=
3.
(a)
(b)
(c)
(d)There are some reports that indicate an increase in the amount of chlorophyll in plants upon exposition to TiO2 NSMs; for instance, Morteza and coworkers [41] suggested that exposition ofZea mays L., in reproductive stage, to TiO2 NSMs contributes to stabilizing the integrity of the chloroplast membrane, protecting chlorophyll. Although other studies report a decrease of chlorophyll content, for example, Nair and Chung suggest that seedlings ofOryza sativa L. exposed to silver NSMs [28] and seedlings ofBrassica juncea L. exposed to copper oxide NSMs [42] showed a reduction of total chlorophyll content due to damage caused to chloroplast membranes as a result of lipid peroxidation by oxidative stress produced by the excess of metal or as result of depletion of iron (Fe) by copper or due to reduced biomass.To examine the impact of NSM inA. thaliana, the anthocyanin content was measured. Anthocyanins are flavonoids that are responsible for coloration in flowers and fruits of higher plants. They are pigments with protective functions against UV radiation; ROS, microorganisms, and the total amount of anthocyanin in plants can change due to some type of stress [43]. Seedling exposed to lower concentrations of NSMs in MS for a week does not show significant differences into the anthocyanin with respect to control group without NSMs (1.4
±
0.4 relative units of anthocyanin per gram of tissue (RUA/g)), for example, (a) 0.5 mg/mL of TiO2-Cu2+ (1.3
±
0.1 RUA/g) and (b) 1 mg/mL of Ag@TiO2 (1.3
±
0.3 RUA/g) (Figures 7(c) and 7(d)); but the anthocyanin content was increased in seedling exposed to 2.5 mg/mL and higher concentration of Ag@TiO2 (4.4
±
0.3 RUA/g). The anthocyanin content in seedlings exposed for 24 h was significantly higher with respect to negative control (0.67
±
0.14 RUA/g) in some conditions, for example, in seedlings exposed to 5 mg/mL of Ag@TiO2 (1.4
±
0.05 RUA/g) and 2.5 mg/mL of TiO2-Cu2+ (1.2
±
0.2 RUA/g) (Figures 7(c) and 7(d)). Syu and coworkers [44] suggest that the increase of anthocyanin content inA. thaliana is due to oxidative stress produced by exposition to Ag NSM and NSMs studied in the present work produce ROS and metal (Ag and Cu) is leached by the materials, which could cause oxidative stress stimulating the anthocyanin production.


## 4. Conclusions

The synthesis of TiO2-Cu2+ and Ag@TiO2 was achieved using an environmentally friendly sol-gel procedure. The nanometric nature, crystallinity, and purity of the materials were demonstrated. Ag@TiO2 and TiO2-Cu2+ showed antimicrobial activity againstE. coli andS. cerevisiae, due to either the photocatalytic property or the metals toxicity. Ag@TiO2 was more active than TiO2-Cu2+, whileE. coli was more sensitive to Ag@TiO2 thanS. cerevisiae. These NSMs showed moderate inhibitory activity against filamentous fungi. The interaction of Ag@TiO2 withA. thaliana showed the following: (a) germination was not affected; (b) seedlings exposed to low concentrations and under light for 24 h had higher elongation; (c) seedling exposed for a week grew less; and (d) total chlorophyll content decreased and anthocyanin increased in seedlings exposed at high concentrations for a week, while seedlings exposed to TiO2-Cu2+ showed the following: (a) no effect on germination; (b) lower elongation, depending on concentration; and (c) lower total chlorophyll content in seedlings exposed at higher concentrations.



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*Source: 8060847-2016-05-22.xml*