Abstract
Understanding the mechanism of nanosilver-dependent antibacterial activity against microorganisms helps optimize the design and usage of the related nanomaterials. In this study, we prepared four kinds of 10 nm-sized silver nanoparticles (AgNPs) with dictated surface chemistry by capping different ligands, including citrate, mercaptopropionic acid, mercaptohexanoic acid, and mercaptopropionic sulfonic acid. Their surface-dependent chemistry and antibacterial activities were investigated. Owing to the weak bond to surface Ag, short carbon chain, and low silver ion attraction, citrate-coated AgNPs caused the highest silver ion release and the strongest antibacterial activity against Escherichia coli, when compared to the other tested AgNPs. The study on the underlying antibacterial mechanisms indicated that cellular membrane uptake of Ag, NAD+/NADH ratio increase, and intracellular reactive oxygen species (ROS) generation were significantly induced in both AgNP and silver ion exposure groups. The released silver ions from AgNPs inside cells through a Trojan-horse-type mechanism were suggested to interact with respiratory chain proteins on the membrane, interrupt intracellular O2 reduction, and induce ROS production. The further oxidative damages of lipid peroxidation and membrane breakdown caused the lethal effect on E. coli. Altogether, this study demonstrated that AgNPs exerted antibacterial activity through the release of silver ions and the subsequent induction of intracellular ROS generation by interacting with the cell membrane. The findings are helpful in guiding the controllable synthesis through the regulation of surface coating for medical care purpose.
Keywords: silver nanoparticles, surface chemistry, silver ion release, Trojan-horse-type mechanism, respiratory chain, oxidative stress
Introduction
Due to the excellent antimicrobial effects of nanosilver against a wide range of microbes, such as bacteria, fungi, and even some viruses, this kind of nanomaterial is becoming more and more popular.1 Its disinfection efficiency has been widely explored in diverse aspects, including water treatment, medical care, and food packages. Since 2013, nanosilver-related commercial products have expanded to >400 types and occupied more than one-half of the nanotechnology-based consumer product amounts,2 revealing the increasing demands and promising commercial values in the production of nanosilver.
Currently available studies have indicated that nanosilver with different characteristics may exert distinct antibacterial capabilities against diverse microorganisms. For example, the minimum inhibitory concentrations (MICs) of silver nanoparticles (AgNPs, 13.4 nm) were 6.6 and 33 nM for Escherichia coli and Staphylococcus aureus, respectively.3 Another study indicated that the effective growth inhibition concentrations of myramisin-capped AgNPs with the particle size of 10 nm were 2.5 and 5 μM for these two bacteria, respectively.4 As for the commercial silver nanopowder, the colony forming units (CFU) of E. coli were completely inhibited when the exposure concentration was 300 μg/mL.5 Apparently, the factors, including particle size, surface capper, and the particle shape, greatly influenced the antibacterial abilities of nano-silver. On-purpose design for the time- and dose-controllable formula of AgNPs has been an important subject regarding the optimization of their antibacterial properties in related commercial products.
The surface ligand-dependent chemistry and potential biological effects have been widely discussed for diverse nanomaterials, including AgNPs.6–8 Under ambient condition, O2 molecule would chemisorb on AgNPs and oxidize the surface Ag atom into monovalent ion of Ag+. It is supposed to be one of the key reactions contributing to the antibacterial activity of AgNPs.1,9–12 Controlled release of biologically active silver from nanosilver can be regulated by the surface ligands. Due to the relatively higher silver ion release ratio, citrate-capped AgNPs significantly enhanced the antibacterial zone of E. coli, when compared to 11-mercaptoundecanoic acid-capped AgNPs based on the Kirby-Bauer disk susceptibility test.12 In contrast, the dissolution rate and the amount of silver ions from polyvinylpyrrolidone-stabilized AgNPs were higher than those from citrate-stabilized AgNPs, because citrate coating was relatively more efficient in preventing silver ions from releasing.13 Branched polyethylenimine-capped AgNPs with positive charges tended to adsorb more on the membrane of gram-positive bacteria than did neutral polyvinylpyrrolidone-coated AgNPs and negatively charged citrate-coated AgNPs, thus causing more effective sterilization.14 Accordingly, the modification of AgNPs with surface ligands based on the adjustment of their coordination atom, carbon chain length, or the terminal group is very promising in regulating the antibacterial activities of AgNPs.
Understanding the antibacterial mechanisms of AgNPs is helpful in guiding the rational design and synthesis of ideal products, as this still remains ambiguous. O2 molecules may chemically adsorb on the 111 facet of AgNP surface and then be incompletely reduced to reactive oxygen species (ROS, ·OH, O2−·). The biologically active radical species are capable of attacking the cell membrane, posing oxidative stress, or even causing death to the cells.15–17 Meanwhile, the released silver ions can approach negatively charged cell membrane and interfere with its integrity.1 Moreover, the internalized AgNPs through endocytosis or pinocytosis may pose a Trojan-horse-type effect, releasing silver ions in the cytoplasm through the reactions with organelles such as mitochondria.1 The intracellular silver ions can directly bind with the thiol-containing enzymes, such as respiratory chain complex I, causing the interruption of electron transfer and ROS production that induces oxidative stress and lesions to cells.18,19 Thus, whether the extracellular ROS generated from AgNP surface or interrupted cellular machinery induced by a Trojan-horse-type effect leads to the intracellular hazardous effects still remains an open question.
Previous studies on surface-coating effect of AgNPs were based on the commercially available AgNPs,3 which might limit the rational comparison of AgNP effects mediated by the different ligand structural factors. In this study, four types of 10 nm-sized AgNPs with different organic ligands, including citrate (Cit), mercaptopropionic acid (MPA), mercaptohexanoic acid (MHA), and mercaptopropionic sulfonic acid (MPS), were intentionally prepared, with regard to the structural factors of coordination atom, carbon chain length, and terminal group. Using E. coli in 2 mM NaHCO3 as the experimental model, the ligand-dependent chemistry and the antibacterial activity of AgNPs were evaluated. The results indicated that the tested nanosilver exerted antibacterial activities in both time- and concentration-dependent manners. The capabilities of nanosilver in inhibiting bacteria were ascribed to the surface ligand-mediated silver ion release from both extracellular process and intracellular manner through a Trojan-horse-type effect. The studies using Cit@ AgNPs showed that internalized AgNPs caused cell damage through binding with the respiratory chain-related proteins and interrupting the electron transfer process. The findings herein have provided a promising strategy for the intended construction of nanosilver by surface chemistry regulation on the basis of understanding its underlying antibacterial mechanism.
Materials and methods
The synthesis and characterization of AgNPs
The Cit@AgNPs was synthesized according to the previously reported method.20 In brief, 5 mM sodium citrate (Sinopharm) and 25 μM tannic acid (Sigma-Aldrich) were added into the 250 μM AgNO3 (Sinopharm) solution. The mixture was continuously stirred and refluxed until the solution turned to light yellow. Cit@AgNPs was purified by ultrafiltration (10 kDa cutoff; Millipore) and washed twice with deionized water. The suspension (40 μg/mL) was stored at 4°C in darkness until use.
The other three kinds of nanoparticles, including MPA@ AgNPs, MHA@AgNPs, and MPS@AgNPs, were synthesized by ligand exchange, which included mixing and overnight stirring 20 μg/mL Cit@AgNPs (6.0 nM) and the respective ligand molecules of 264 μg/mL MPA, 64 μg/mL MHA, and 108 μg/mL MPS (Alfa-Aesar) in 10 mM phosphate-buffered saline (PBS) (pH 7.4) at ambient temperature. The concentrations of the ligands were selected based on the optimization of ligand/AgNP molar ratio in preliminary studies, ie, the molar ratios of MPA, MHA, and MPS to AgNPs were 50,000:1, 500,000:1, and 10,000:1, respectively. The unreacted reagents were removed by ultrafiltration, and the products were further washed with deionized water twice to obtain the MPA@ AgNPs, MHA@AgNPs, and MPS@AgNPs. The prepared NP suspensions were kept at 4°C in darkness.
The morphologies of AgNPs were observed with transmission electron microscopy (TEM, 2100f; JEOL). The measurements, including X-ray photoelectron-binding energy analysis (AXIS UltraDLD; Kratos), UV–vis absorption (DU-800; Beckman), hydrodynamic size, and zeta potential (Mastersizer 2000; Malvern), were conducted to characterize the surface modification of these four kinds of AgNPs.
As for the determination of silver ion release, the as-prepared four AgNPs were resuspended in the exposure medium of 2 mM NaHCO3 (Sinopharm) at the concentrations of 1, 5, and 15 μg/mL, respectively, and incubated at 37°C under shaking (220 rpm) for 6 and 24 h. The filtrates obtained by ultrafiltration with 3 kDa cutoff membrane (Millipore) were used for the quantification of silver ion release. After sufficient digestion of filtrates by acid mixture (65% HNO3:30% H2O2, 1:1; Sinopharm), inductively coupled plasma mass spectrometry (ICP-MS, Agilent 8800) was utilized to quantify the released silver ions from AgNP suspension.
AgNP exposure to E. coli
One colony of E. coli (MG 1655) was inoculated into liquid Luria–Bertani (LB; Sigma-Aldrich) medium and grew at 37°C under shaking. The aliquots of suspension (200 μL) were collected at intervals of 30 or 60 min for the determination of the optical density at 600 nm (OD600) using UV–vis spectrophotometer (DU-800; Beckman) to plot the growth curve of E. coli. The exponential growth phase of E. coli was reached after 3 h culture in LB growth medium, according to the growth curve (Figure S1). Therefore, E. coli entering into this rapid growth period was used for the exposure experiments.
The exposure of E. coli was conducted according to the previously reported protocol.21 After 3 h incubation, E. coli was centrifuged, washed, and resuspended in 2 mM NaHCO3 at the concentration of 107 cfu/mL. The exposure groups included AgNPs (1, 5, and 15 μg/mL) and AgNO3 (5, 20, 50, 200, and 1,000 ng/mL). The treatment was performed on a shaker at 37°C with the rotary speed of 220 rpm. After 6 h exposure, the mixture was centrifuged at 1,000× g for 5 min. The precipitate was washed with NaHCO3 medium. The pellet of E. coli was resuspended in 100 μL of LB culture medium and transferred to the transparent 96-well plate. The treated E. coli grew in the incubator (KS 4000i control, IKA®, Staufen, Germany) overnight at 37°C under the rotary speed of 220 rpm. The values of OD600 were determined to evaluate the viabilities of E. coli upon diverse stimuli.
The additional exposure groups were also designed to investigate the antagonistic effects of glutathione (GSH) (Sigma-Aldrich) and Na2S2O3 (Sinopharm) on AgNPs and silver ions, respectively. More specifically, E. coli was stimulated with AgNPs (1, 5, and 15 μg/mL) or AgNO3 (5, 20, 50, 200, and 1,000 ng/mL) in the presence of 1 mM GSH or 0.1 mM Na2S2O3 for 6 h, respectively. The bacterial viability in each group was evaluated as described earlier. Regarding the antagonistic effects of these two chemicals in toxicological studies, four exposure groups including 15 μg/mL Cit@AgNPs, 15 μg/mL Cit@AgNPs plus 1 mM GSH, 15 μg/mL Cit@AgNPs plus 0.1 mM Na2S2O3, and 0.5 μg/mL AgNO3 were set up, and E. coli in each group was stimulated for 6 h. After the exposure was terminated, the bacterial samples were washed with PBS and submitted to the subsequent pretreatments for the morphological observation, silver uptake evaluation, NAD+/NADH ratio test, malonyl-dialdehyde (MDA), and 8-oxoguanine assays.
Morphological observation of E. coli
After the exposure, E. coli from each group was resuspended in 2.5% glutaraldehyde/PBS (SP1-CHEM). The fixation was processed overnight at 4°C. The dehydration was successively performed using 30, 50, 70, 80, 90, 95, and 100% ethanol (Sinopharm). Isobutyl acetate (Sinopharm) was used to replace ethanol for scanning electronic microscope (SEM, SU8020; Hitachi) observation.
Ag uptake and distribution by E. coli
E. coli samples from the control, 15 μg/mL Cit@AgNP, and 0.5 μg/mL AgNO3 exposure groups were submitted to the digestion with 2 mL of acidic mixture (65% HNO3:30% H2O2, 1:1; Sinopharm) for the determination of total Ag uptake. The equivalent E. coli samples from exposure groups were lysed via intermittent sonication on ice for 1 min. The samples were subsequently centrifuged at 30,000× g for 30 min. The supernatant and precipitate were separately collected and digested to obtain the membrane and cytoplasm fractions of E. coli. Silver concentrations in both fractions were quantitatively measured with ICP-MS for Ag distribution in E. coli.
NAD+/NADH ratio test
The assay of NAD+/NADH ratio was used to evaluate the disturbance of AgNPs on the respiration chain in E. coli. The exposed samples were treated with 0.2 M NaOH and 0.2 M HCl (Sinopharm) at 100°C for 10 min to extract NADH and NAD+, respectively. After 5 min centrifugation, the supernatant samples were collected and analyzed using the NAD+/NADH Assay Kit (ab65348; Abcam).
Intracellular ROS assay
E. coli were exposed using the similar protocol to other assays, such as morphological observation and NAD+/NADH ratio. After the exposure was terminated, E. coli in each group was incubated with ROS probe of 10 μM 2,7-dichlorodi-hydrofluorescein diacetate (DCFH-DA) (Sigma-Aldrich) at 37°C for 30 min. After removing the redundant probes outside cells, the fluorescent signal (λex/λem =484/525 nm) was measured with the microplate reader (Varioskan® Flash; Thermo Fisher Scientific, Waltham, MA, USA) to evaluate the intracellular ROS production in the exposed E. coli.
MDA generation in E. coli
The content of MDA in AgNP-exposed E. coli was quantified by the lipid peroxidation assay kit (Abcam). Briefly, the bacteria were harvested and washed with cold PBS after exposure. Then, the cells were homogenized in MDA lysis buffer and centrifuged at 13,000× g for 10 min. The supernatant was collected for MDA measurement. MDA in samples reacted with thiobarbituric acid (TBA) and formed adducts with red color. The level of MDA production in each exposure group was quantified according to the specific absorbance of adducts at 532 nm.22
8-Oxoguanine determination using liquid chromatography-mass spectrometry/mass spectrometry (LC-MS/MS)
The oxidative stress can induce DNA damage, resulting in the formation of 8-oxoguanine (8-oxo-dG). After the stimulation, E. coli sample from each group was extracted and processed for enzymatic hydrolysis using Bacterial DNA Kit (Omega). The levels of 8-oxo-dG were measured with LC-MS/MS using the pair ions of m/z 284/168 as the quantitative ions. The detection limit of the analytical method was 2 nM.
Statistical analysis
All the data were acquired from three independent experiments, and the values were expressed as average ± standard deviation. The statistical analysis was performed using Student’s t-test. The significant difference was demonstrated by P<0.05.
Results and discussion
Characterization of AgNPs
AgNPs with particle size not more than 10 nm exhibited surface-dependent ion release and toxicity.7 In this study, the monodisperse citrate-coated AgNPs of ~10 nm were synthesized by chemically reducing silver citrate with trace tannic acid according to the previously reported method.20 The characterization results of the prepared nanoparticles are presented in Figure 1. The size distribution of Cit@AgNPs based on TEM image is 10.2±2.3 nm. X-ray photoelectron spectroscopy (XPS) data in Figure S2 reveal the doublet Ag3d peaks at 368.2 and 374.2 eV, demonstrating that Ag core of Cit@AgNPs mainly stays at zero valence. C1s spectra can be fitted into four peaks with the corresponding binding energies of C-C, C-O, free O=C-O, and Ag coordinated O=C-O of citrate (Figure S2).23,24 Thus, based on electronic effect and steric effect, the interface structure as shown in the cartoon (Figure 1) was suggested. Citrate ligand capped the thermodynamic-stabilized AgNPs through the coordination of two carboxyl groups to the surface Ag atoms. The other free carboxyl group in citrate oriented outward and constituted the outer layer of AgNPs, resulting in negative surface charges (−47.4 mV) of Cit@AgNPs and high stability in aqueous dispersion.
The selection of the other three ligands was based on the structural factors including the coordination atom (O or S), carbon chain length (3C or 6C), and the terminal group (−COO− or −SO−3). These factors could control the surface Ag atom activity, O2 access, and Ag+ release of the synthesized AgNPs. The exchange of the surface citrate with free ligands of MPA, MHA, and MPS on silver core produced MPA@AgNPs, MHA@AgNPs, and MPS@AgNPs, respectively. Considering the replacing ligands were superfluous in the reactions and they had relatively higher binding affinities to Ag surface than citrate, these three synthesized AgNPs were qualified for the subsequent experiments after the ligand exchange equilibrium reached and the complete wash of the products with deionized water using 10 kDa cutoff ultrafiltration devices. The TEM images showed that they were spherically shaped and monodispersive. The respective particle sizes were 10.2±2.5 nm for MPA@ AgNPs, 10.2±2.2 nm for MHA@AgNPs, and 9.9±2.0 nm for MPS@AgNPs. The similar particle sizes of the four synthesized AgNPs showed that no changes in particle aggregation occurred during the surface ligand exchange of the nanoparticles. XPS data in Figure S2 indicate that they share similar characteristics: 1) AgNPs have a weakened resolved peak of Ag coordinated O=C-O and an enhanced peak of C-S in C1s spectra, and 2) the doublet electronic-binding energy for S2p spectra is decreased. This suggested that instead of citrate, the ligands of MPA, MHA, and MPS anchored to the surface of AgNPs through the coordination between thiol groups and Ag atom, thus forming MPA@ AgNPs, MHA@AgNPs, and MPS@AgNPs, respectively.23,24 In addition, the S2p spectra of MPS@AgNPs showed a fitted peak at 167.9 eV assigned to the sulfonic acid group of MPS molecule.25 The free carboxyl groups and sulfonic acid in outer layers of AgNPs endowed them with the negatively charged surfaces, and the zeta potentials in water were −34.5 mV for MPA@AgNPs, −29.1 mV for MHA@ AgNPs, and −32.6 mV for MPS@AgNPs. The maximum absorbance of surface plasmon resonance (SPR) was in the narrow range of 392–396 nm, indicating the dispersion systems for these four AgNPs were robust and the particles had high monodispersity.
Surface ligands regulate silver ion release from AgNPs in vitro
Until now, the question as to whether the released silver ions or ROS mainly explain AgNP-induced antibacterial activities has been hotly debated. Herein, silver ion release from four as-prepared AgNPs in 2 mM NaHCO3 solution was determined after 6 and 24 h incubation at 37°C. The results shown in Figure 2A and B indicate that ionic silver levels in the solutions exhibit both concentration- and time-dependent increase. Namely, silver ion release increased with AgNP concentrations ranging from 1 to 15 μg/mL. As the incubation time proceeded from 6 to 24 h, AgNPs released more silver ions into the solution. Silver ion release from AgNPs could be explained by the in vitro process in which the ambient O2 contacted and chemosorbed on AgNP surface, subsequently oxidized core Ag0 into Ag+ that freely diffused into the surrounding solutions.9 When the effect of the surface ligand on silver ion release from AgNPs was investigated, it was found that during the monitoring time scale (6–24 h), AgNPs in NaHCO3 released silver ions in the following order: Cit@AgNPs > MPS@AgNPs > MPA@ AgNPs > MHA@AgNPs. For example, at the concentration of 15 μg/mL, the ionic silver released from AgNPs was 68.9 ng/mL for Cit@AgNPs, 35.8 ng/mL for MPS@ AgNPs, 22.1 ng/mL for MPA@AgNPs, and 18.9 ng/mL for MHA@AgNPs after 24 h incubation at 37°C. In contrast to the other three AgNPs with sulfur atom of the ligands binding on the surface, the ligand of citrate anchored to the surface of silver core through oxygen atoms with relatively weaker binding affinity, facilitating adsorption exchange with surrounding O2, and further oxidative dissolution of Ag0.26,27 The shortest carbon chain of citrate among four tested ligands had the weakest capacity for oxygen isolation and caused the highest dissolution of Ag0 via easiest exposure access of silver core to environmental O2.28 Among three AgNPs coated with thiol groups, the terminal group of −SO−3 in the ligand MPS had lower affinity to release Ag+ than −COO−, thus causing less dissolved silver ions retaining on the particle surface and more ions being liberated to the surrounding solution.9 According to the results described earlier, the determined silver ion release order for all four tested AgNPs was closely dependent on their surface ligands. Therefore, the theoretical design through structural ligand regulation might specifically control the silver core oxidation by ambient O2 and the further release of silver ions, which could subsequently be involved with their biological effects. This also offered a promising approach for uncovering the underlying mechanism for AgNP-induced antibacterial activities by synthesizing diverse AgNPs with the specific characteristics to be tested.
AgNPs produce antibacterial activities via a Trojan-horse-type mechanism
E. coli can be cultured in simple media, such as NaHCO3, which has little effect on chemistry and bioavailability of the active species produced by nanosilver. Thus, E. coli in 2 mM NaHCO3 was used as the model organism to study the antibacterial activities and the related mechanism of nanosilver. As shown in Figure 3A, when the exposure concentrations were controlled at 1, 5, and 15 μg/mL, all four AgNPs exhibited an obvious concentration-dependent inhibition on E. coli viability after 6 h exposure. Based on the comparison of the bacterial viabilities in different treatments (Figure 3A), the inhibition efficiency of AgNPs on bacterial growth was in the following order: Cit@AgNPs > MPS@AgNPs > MPA@AgNPs > MHA@AgNPs, indicating the surface coating could obviously mediate the antibacterial activities of AgNPs. The surface coating effect that was previously reported indicated that citrate-coated AgNPs exerted higher toxicities when compared to those coated with biodegradable polymer,29 although no differences were observed between AgNPs with polyvinylpyrrolidone or oleic acid coatings in an earthworm study.30 The antibacterial order observed was exactly consistent with the trend of silver ion release from these AgNPs (Figure 2). This suggested that the released silver ions might mainly contribute to AgNP-induced antibacterial activities.
In order to further clarify the roles of released silver ions, the antibacterial activities were further evaluated by adding the reductase of GSH or ion ligand of Na2S2O3 in AgNP exposure systems. The results in Figure 3B and C show that both 1 mM GSH and 0.1 mM Na2S2O3 can efficiently block AgNP exposure-dependent toxicity to E. coli, and the bacterial activities in diverse treatments are completely recovered. It has been shown that GSH could eliminate ROS generation and stabilize AgNPs, and Na2S2O3 could decrease the bioavailability of Ag+ by binding with free dissolved Ag+, thus reducing the biological activities of the ionic silver.31 The protection of E. coli by both GSH and Na2S2O3 observed earlier suggested that the compromised bacterial growth with AgNP treatments could be dominantly regulated by the oxidation process of AgNPs concomitant with silver ion release and ROS generation.
As the positive control, the effects of silver ions were also tested regarding the antibacterial activities against E. coli. The results in Figure 3D show that silver ions can induce significant bacterial growth inhibition in a concentration-dependent manner within the range of 50–1,000 ng/mL. When compared to AgNPs, silver ions had relatively higher toxicities to E. coli, which was consistent with the findings reported previously.7 Similarly, both reagents, GSH and Na2S2O3, could completely recover the suppressed bacterial viabilities of E. coli induced by silver ion exposure, which was similar to the results obtained from AgNP exposure experiments. Therefore, it was suggested that AgNP-induced bacterial toxicity could be regulated by silver ion release from the nanosized Ag core.
Nevertheless, when in vitro silver ion release was evaluated, it was found that 6 h incubation of 1–15 μg/mL AgNPs released low levels of silver ions (<20 ng/mL, Figure 2A). However, 1–15 μg/mL AgNPs significantly inhibited the bacterial activity, as shown in Figure 3A (bacterial toxicity: 56.5%–95.5% for Cit@AgNPs, 32.4%–95.4% for MPS@ AgNPs, 0.8%–47.4% for MPA@AgNPs, and 0–22.8% for MHA@AgNPs), while 20 ng/mL silver ions hardly caused any effects (bacterial viability: ~100%, Figure 3D). This indicated that the released silver ions in medium might influence but not dominate AgNP-induced toxicities to E. coli. Accordingly, the effects of the extracellular ROS generation from the in vitro dissolution of AgNPs were also limited. The particle-specific effects could be the predominant mediator in AgNP exposure-induced bacterial growth inhibition, rather than the negligible effects from the released ionic silver or extracellular ROS generated in vitro. It was well known that AgNPs might cause cytotoxicity by a Trojan-horse-type mechanism, which explained how AgNPs facilitated the release of free toxic silver ions in cells, where the particles entered and were then ionized.32–34 Accordingly, intracellular silver ion release greatly contributed to the antibacterial activities of AgNPs. The surface ligand might also regulate this process in the similar way to what happened in vitro, thus explaining the toxicity order of the four tested AgNPs described earlier. In addition, the intracellular oxidative intermediates (H2O2, etc.) and acidic condition of the organelle (lysosome, etc.) might facilitate the oxidation of the silver core,32 potentially inducing the generation of more silver ions and ROS, which could trigger the corresponding biological effects, such as antibacterial activities. With regard to the quantification for the percentage of particulate effect, this is still challenging due to the complexity of the antibacterial mode of AgNPs, and the hot debate on this question continues in the related toxicological studies.
Cit@AgNPs perturb the bacterial respiratory chain through binding with the bacterial membrane, thus increasing intracellular ROS generation
The cellular uptake of AgNPs might provide the substantial basis for their biological effects occurring in vivo. Using Cit@AgNPs as the representative AgNPs, the distribution of Ag in E. coli was studied after 6 h exposure. As shown in Figure 4A (left panel), the total Ag levels were similar (~120 ng/107 cfu) in E. coli samples treated with 15 μg/mL Cit@AgNPs or 0.5 μg/mL Ag+, showing the relatively higher biouptake efficiency of silver in Ag+ exposure groups when compared to Cit@AgNP-treated ones. As the silver ion release ratio of 15 μg/mL Cit@AgNPs was less than 0.02 μg/mL in the medium after 6 h incubation, particulate Ag greatly contributed to the silver biouptake in Cit@AgNP-treated bacteria. Regarding silver distribution, cytoplasmic Ag levels were a little bit higher than membrane Ag levels, providing the evidence that the extracellular silver either in particulate or in ionic forms could bind with the membrane and enter into the bacterial bodies. The internalization of Ag enabled the biological effects that might happen on the membrane or in cytoplasm through a Trojan-horse-type mechanism for Cit@AgNPs.
It was well known that there were abundant biological enzymes in the bacterial membrane, for example, dehydrogenase, oxidative phosphorylation enzyme, and respiratory chain enzymes.18,35 Therefore, the membrane was an important location for energy transfer. More specifically, the respiratory chain in the bacterial membrane was in charge of electron and energy transfer, in which, the reductive coenzyme of NADH was converted into oxidative coenzyme of NAD+, and O2 was reduced to H2O by gaining the electron, and the energy was released for the subsequent ATP synthesis in the biological system.35 The occurrence of membrane silver might pose high risks for the disruption of the respiratory chain, which led to intracellular NADH consumption and ROS accumulation.36,37 The evaluation for the respiratory chain of E. coli (Figure 4B) shows that NAD+/NADH ratios are significantly increased by both Cit@ AgNPs (0.57) and Ag+ treatments (0.62) comparing to the control (0.48), indicating the imbalance of the key elements in the respiratory chain. The addition of GSH or Na2S2O3 efficiently erased the increase in NAD+/NADH ratio induced by Cit@AgNP exposure. This result was consistent with the finding from the bacterial viability assay. As the internalized AgNPs might exert hazardous biological effects through a Trojan-horse-type mechanism, the released Ag+ could bind/interact with the essential enzymes on membrane, interrupt the electron transfer, generate excessive ROS, and induce oxidative stress in E. coli. Therefore, the elimination of intracellular ROS and free Ag+ by the reagents, GSH and Na2S2O3, blocked the abnormal effects, such as dysfunction of the respiratory chain, induced by AgNPs.
As mentioned earlier, AgNP exposure might affect the bacterial respiratory chain, potentially causing the imbalance of oxidative–antioxidative system in vivo. The oxidative stress was usually triggered by excessive ROS generation in cells due to the collapse of the antioxidation system.38 The intracellular ROS generation was thus evaluated based on DCFH-DA assay. The result in Figure 4C shows that, similar to Ag+, Cit@AgNP stimulation significantly elevates intracellular ROS level, showing the potential oxidative stress in the treated E. coli. The cotreatment with reductase GSH and Na2S2O3 decreased ROS elevation induced by Cit@AgNPs, thus providing efficient protection on the bacteria from the subsequent hazardous impacts. It was widely reported that AgNP-induced biological effects or toxicities were mainly involved with silver ion release or intracellular ROS generation,7,11,39 although some studies emphasized that AgNPs could efficiently induce oxidative stress through excessive ROS production, which was distinct from silver ions.17 The results obtained herein revealed the concurrence of Ag+ and ROS in AgNP-exposed bacterial system, showing the complexity of the antibacterial effects induced by AgNPs.
Cit@AgNP exposure induces oxidative damage in E. coli
Oxidative stress induced by intracellular excessive ROS generation might pose high risks for the occurrence of oxidative damage, thus causing the structural lesions to the essential biomacromolecules, such as lipids and DNA. The peroxidation of lipid by active free oxidative radicals could produce oxidized products of aldehydes, such as MDA and 4-hydroxyl nonenal (4-NHE), resulting in the loss of cell membrane integrity and even damage on cell structure.22,40 MDA, as a common biomarker, was quantitatively measured in E. coli treated with Cit@AgNPs and Ag+ to evaluate the potential lipid peroxidation. The results in Figure 5A show that Cit@AgNPs and Ag+ treatments slightly increase MDA levels in E. coli, indicating the existence of lipid peroxidation due to oxidative damage. Similar to the findings from bacterial activity, NAD+/NADH ratio, and ROS assays, the protection effect was observed in the coexposure groups of Cit@AgNPs plus GSH and Cit@AgNPs plus Na2S2O3, which further confirmed that Ag+ release and ROS generation played important roles in the mediation of Cit@AgNP-induced oxidative damage in E. coli.
Morphological observation using scanning electron microscopy might provide direct evidence on the surface changes in the organisms. Figure 5B shows that the control E. coli is in rod-like shape with the longitudinal diameter of ~2 μm. The bacterial surface was smooth and intact. The treatments of Cit@AgNPs and Ag+ caused cell collapse of E. coli structure, which was characterized by the rough surfaces and even breakdown in some bacterial bodies (Figure 5C and D). The coincubation of GSH and Na2S2O3 efficiently blocked the morphological damages caused by Cit@AgNP exposure, and the bacterial bodies were as intact as the controls. This finding was consistent with the results of MDA assay and the protection effects of these two reagents observed earlier.
The imbalance of oxidation–antioxidation system due to intracellular excessive ROS generation might also lead to deleterious effects, such as the alterations of DNA structure.41,42 The oxidative modification on certain sites of DNA could form representative products. For example, hydroxylation on the eighth carbon atom of guanine moiety produced 8-oxo-dG, which was commonly used as a sensitive biomarker for DNA oxidative damage. The analysis based on LC-MS/MS showed that no detectable levels of 8-oxo-dG (<2 nM) were found in E. coli samples with diverse treatments (Figure 5G), revealing that, in contrast to lipid peroxidation, no DNA oxidative damage occurred upon AgNP or Ag+ stimulations.
In summary, the coating ligands of AgNPs regulated Ag+ release in vitro and in vivo. By binding with or entering into the plasma membrane, AgNPs disturbed the respiratory chain in E. coli and caused oxidative stress through a Trojan-horse-type mechanism. The corresponding deleterious effects, including lipid peroxidation, loss in the integrity of plasma membrane, and bacterial growth inhibition, could be efficiently attenuated by the coexposure of GSH or Na2S2O3, confirming the critical roles of ROS concomitant with the released Ag+ in antibacterial activities of AgNPs. The overall proposed process is sketched in Scheme 1.
Conclusion
In this study, ligand-dependent Ag+ release was found based on the comparison of four 10 nm-sized AgNPs coated with Cit, MPA, MHA, and MPS, respectively. These ligands possess different coordination atoms, carbon chain lengths, and terminal groups. The particulate Ag coated with citrate had the highest Ag+ release ratio and the strongest antibacterial activities against E. coli due to its short carbon chain and weak binding atom of oxygen, when compared to the other three tested AgNPs. A Trojan-horse-type mechanism was proposed as AgNP-induced toxicities could not be fully explained by the in vitro Ag+ release. Using Cit@AgNPs as the representative, AgNPs were found to perturb the bacterial respiratory chain through binding with the bacterial membrane, thus raising intracellular ROS generation and the corresponding lipid peroxidation. The findings herein provided new insights into roles of ligands in regulating antibacterial properties of nanosilver and the underlying molecular mechanism. The optimization of the surface ligand, such as coordination atom, carbon chain, and terminal group, is a very promising strategy in nanoparticle manufacture for multiple commercial application purposes.
Supplementary materials
Acknowledgments
This research was jointly supported by the National Basic Research Program of China (2015CB453102), National Natural Science Foundation of China (21307151, 21621064, 21477153, 21677063, and 21461142001), and the Chinese Academy of Science (14040302, QYZDJ-SSW-DQC017). We thank Prof Zhixiong Xie from Wuhan University for kindly providing E. coli strain of MG 1655 and Dr Hua Huang from Research Center for Eco-Environmental Sciences for helping with the measurement of 8-oxo-dG.
Footnotes
Disclosure
The authors report no conflicts of interest in this work.
References
- 1.Marambio-Jones C, Hoek EMV. A review of the antibacterial effects of silver nanomaterials and potential implications for human health and the environment. J Nano Res. 2010;12(5):1531–1551. [Google Scholar]
- 2.Wilson Center [webpage on the Internet] An Inventory of Nanotechnology-Based Consumer Products Introduced on the Market. [Accessed July 2015]. Available from: http://www.nanotechproject.org/cpi.
- 3.Kim JS, Kuk E, Yu KN, et al. Antimicrobial effects of silver nanopar-ticles. Nanomed Nanotechnol. 2007;3(1):95–101. doi: 10.1016/j.nano.2006.12.001. [DOI] [PubMed] [Google Scholar]
- 4.Vertelov GK, Yu AK, Efremenkova OV, Olenin AY, Lisichkin GV. A versatile synthesis of highly bactericidal Myramistin® stabilized silver nanoparticles. Nanotechnology. 2008;19(35):355707. doi: 10.1088/0957-4484/19/35/355707. [DOI] [PubMed] [Google Scholar]
- 5.Smetana AB, Klabunde KJ, Sorensen CM. Synthesis of spherical silver nanoparticles by digestive ripening, stabilization with various agents, and their 3-D and 2-D superlattice formation. J Colloid Interface Sci. 2005;284(2):521–526. doi: 10.1016/j.jcis.2004.10.038. [DOI] [PubMed] [Google Scholar]
- 6.Alivisatos AP. Semiconductor clusters, nanocrystals, and quantum dots. Science. 1996;271(5251):933–937. [Google Scholar]
- 7.Levard C, Hotze EM, Lowry GV, Brown GE., Jr Environmental transformations of silver nanoparticles: impact on stability and toxicity. Environ Sci Technol. 2012;46(13):6900–6914. doi: 10.1021/es2037405. [DOI] [PubMed] [Google Scholar]
- 8.Nel A, Xia T, Madler L, Li N. Toxic potential of materials at the nano-level. Science. 2006;311(5761):622–627. doi: 10.1126/science.1114397. [DOI] [PubMed] [Google Scholar]
- 9.Liu J, Hurt RH. Ion release kinetics and particle persistence in aqueous nano-silver colloids. Environ Sci Technol. 2010;44(6):2169–2175. doi: 10.1021/es9035557. [DOI] [PubMed] [Google Scholar]
- 10.Ma R, Levard C, Marinakos SM, et al. Size-controlled dissolution of organic-coated silver nanoparticles. Environ Sci Technol. 2012;46(2):752–759. doi: 10.1021/es201686j. [DOI] [PubMed] [Google Scholar]
- 11.Sotiriou GA, Pratsinis SE. Antibacterial activity of nanosilver ions and particles. Environ Sci Technol. 2010;44(14):5649–5654. doi: 10.1021/es101072s. [DOI] [PubMed] [Google Scholar]
- 12.Liu J, Sonshine DA, Shervani S, Hurt RH. Controlled release of biologically active silver from nanosilver surfaces. ACS Nano. 2010;4(11):6903–6913. doi: 10.1021/nn102272n. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Kittler S, Greulich C, Diendorf J, Köller M, Epple M. Toxicity of silver nanoparticles increases during storage because of slow dissolution under release of silver ions. Chem Mater. 2010;22(16):4548–4554. [Google Scholar]
- 14.Badawy AME, Luxton TP, Silva RG, Scheckel KG, Suidan MT, Tolaymat TM. Impact of environmental conditions (pH, ionic Strength, and electrolyte type) on the surface charge and aggregation of silver nano-particles suspensions. Environ Sci Technol. 2010;44(4):1260–1266. doi: 10.1021/es902240k. [DOI] [PubMed] [Google Scholar]
- 15.Carlson C, Hussain SM, Schrand AM, et al. Unique cellular interaction of silver nanoparticles: size-dependent generation of reactive oxygen species. J Phys Chem B. 2008;112(43):13608–13619. doi: 10.1021/jp712087m. [DOI] [PubMed] [Google Scholar]
- 16.Schmidt M, Masson A, Bréchignac C. Oxygen and silver clusters: transition from chemisorption to oxidation. Phys Rev Lett. 2003;91(24):243401. doi: 10.1103/PhysRevLett.91.243401. [DOI] [PubMed] [Google Scholar]
- 17.Xiong Y, Brunson M, Huh J, et al. The role of surface chemistry on the toxicity of Ag nanoparticles. Small. 2013;9(15):2628–2638. doi: 10.1002/smll.201202476. [DOI] [PubMed] [Google Scholar]
- 18.Asharani PV, Low Kah Mun G, Hande MP, Valiyaveettil S. Cytotoxicity and genotoxicity of silver nanoparticles in human cells. ACS Nano. 2008;3(2):279–290. doi: 10.1021/nn800596w. [DOI] [PubMed] [Google Scholar]
- 19.Holt KB, Bard AJ. Interaction of silver(I) ions with the respiratory chain of Escherichia coli: an electrochemical and scanning electrochemical microscopy study of the antimicrobial mechanism of micromolar Ag+ Biochemistry. 2005;44(39):13214–13223. doi: 10.1021/bi0508542. [DOI] [PubMed] [Google Scholar]
- 20.Bastús NG, Merkoçi F, Piella J, Puntes V. Synthesis of highly monodisperse citrate-stabilized silver nanoparticles of up to 200 nm: kinetic control and catalytic properties. Chem Mater. 2014;26(9):2836–2846. [Google Scholar]
- 21.Wiegand I, Hilpert K, Hancock RE. Agar and broth dilution methods to determine the minimal inhibitory concentration (MIC) of antimicrobial substances. Nat Protoc. 2008;3(2):163–175. doi: 10.1038/nprot.2007.521. [DOI] [PubMed] [Google Scholar]
- 22.Porter NA. A perspective on free radical autoxidation: the physical organic chemistry of polyunsaturated fatty acid and sterol peroxidation. J Org Chem. 2013;78(8):3511–3524. doi: 10.1021/jo4001433. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Janardhanan R, Karuppaiah M, Hebalkar N, Rao TN. Synthesis and surface chemistry of nano silver particles. Polyhedron. 2009;28(12):2522–2530. [Google Scholar]
- 24.Yang H, Lan Y, Zhu W, et al. Polydopamine-coated nanofibrous mats as a versatile platform for producing porous functional membranes. J Mater Chem. 2012;2(33):16994–17001. [Google Scholar]
- 25.Rudkevich DM, Stauthamer WPRV, Verboom W, Engbersen JFJ, Harkema S, Reinhoudt DN. Uranyl UO2-salenes: neutral receptors for anions with a high selectivity for dihydrogen phosphate. J Am Chem Soc. 1992;114(24):9671–9673. [Google Scholar]
- 26.Love JC, Estroff LA, Kriebel JK, Nuzzo RG, Whitesides GM. Self-assembled monolayers of thiolates on metals as a form of nanotechnology. Chem Rev. 2005;105(4):1103–1170. doi: 10.1021/cr0300789. [DOI] [PubMed] [Google Scholar]
- 27.Romanska D, Mazur M. Electrochemical preparation of thiol-coated silver nanostructures on highly oriented pyrolytic graphite. Langmuir. 2003;19(11):4532–4534. [Google Scholar]
- 28.Grubbs RB. Roles of polymer ligands in nanoparticle stabilization. Polym Rev. 2007;47(2):197–215. [Google Scholar]
- 29.Lu W, Senapati D, Wang S, et al. Effect of surface coating on the toxicity of silver nanomaterials on human skin keratinocytes. Chem Phys Lett. 2010;487(1–3):92–96. doi: 10.1016/j.cplett.2010.01.027. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Shoults-Wilson WA, Reinsch BC, Tsyusko OV, Bertsch PM, Lowry GV, Unrine JM. Effect of silver nanoparticle surface coating on bioaccumulation and reproductive toxicity in earthworms (Eisenia fetida) Nanotoxicology. 2011;5(3):432–444. doi: 10.3109/17435390.2010.537382. [DOI] [PubMed] [Google Scholar]
- 31.Li H, Cui Z, Han C. Glutathione-stabilized silver nanoparticles as colorimetric sensor for Ni2+ ion. Sens Actuators B Chem. 2009;143(1):87–92. [Google Scholar]
- 32.Cronholm P, Karlsson HL, Hedberg J, et al. Intracellular uptake and toxicity of Ag and CuO nanoparticles: a comparison between nanoparticles and their corresponding metal ions. Small. 2013;9(7):970–982. doi: 10.1002/smll.201201069. [DOI] [PubMed] [Google Scholar]
- 33.Wang Z, Liu S, Ma J, et al. Silver nanoparticles induced RNA polymerase-silver binding and RNA transcription inhibition in erythroid progenitor cells. ACS Nano. 2013;7(5):4171–4186. doi: 10.1021/nn400594s. [DOI] [PubMed] [Google Scholar]
- 34.Hsiao IL, Hsieh YK, Wang CF, Chen IC, Huang YJ. Trojan-horse mechanism in the cellular uptake of silver nanoparticles verified by direct Intra- and extracellular silver speciation analysis. Environ Sci Technol. 2015;49(6):3813–3821. doi: 10.1021/es504705p. [DOI] [PubMed] [Google Scholar]
- 35.Sousa PMF, Videira MA, Bohn A, et al. The aerobic respiratory chain of Escherichia coli: from genes to supercomplexes. Microbiology. 2012;158(9):2408–2418. doi: 10.1099/mic.0.056531-0. [DOI] [PubMed] [Google Scholar]
- 36.Cui Y, Zhao Y, Tian Y, Zhang W, Lü X, Jiang X. The molecular mechanism of action of bactericidal gold nanoparticles on Escherichia coli. Biomaterials. 2012;33(7):2327–2333. doi: 10.1016/j.biomaterials.2011.11.057. [DOI] [PubMed] [Google Scholar]
- 37.Kohanski MA, Dwyer DJ, Hayete B, Lawrence CA, Collins JJ. A common mechanism of cellular death induced by bactericidal antibiotics. Cell. 2007;130(5):797–810. doi: 10.1016/j.cell.2007.06.049. [DOI] [PubMed] [Google Scholar]
- 38.Bandyopadhyay U, Das D, Banerjee RK. Reactive oxygen species: oxidative damage and pathogenesis. Curr Sci. 1999;77(5):658–666. [Google Scholar]
- 39.Navarro E, Piccapietra F, Wagner B, et al. Nanosilver toxicity: ions, nanoparticles or both? Environ Sci Technol. 2008;42(23):8959–8964. doi: 10.1021/es801785m. [DOI] [PubMed] [Google Scholar]
- 40.Rival T, Cinq-Frais C, Silva-Sifontes S, et al. Alteration of plasma phospholipid fatty acid profile in patients with septic shock. Biochimie. 2013;95(11):2177–2181. doi: 10.1016/j.biochi.2013.08.006. [DOI] [PubMed] [Google Scholar]
- 41.Yin R, Mao SQ, Zhao B, et al. Ascorbic acid enhances Tet-mediated 5-methylcytosine oxidation and promotes DNA demethylation in mammals. J Am Chem Soc. 2013;135(28):10396–10403. doi: 10.1021/ja4028346. [DOI] [PubMed] [Google Scholar]
- 42.Zhao B, Yang Y, Wang X, et al. Redox-active quinones induces genome-wide DNA methylation changes by an iron-mediated and Tet-dependent mechanism. Nucleic Acids Res. 2014;42(3):1593–1605. doi: 10.1093/nar/gkt1090. [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.