Selective antibiofilm properties and biocompatibility of nano-ZnO and nano-ZnO/Ag coated surfaces.

Spread of pathogenic microbes and antibiotic-resistant bacteria in health-care settings and public spaces is a serious public health challenge. Materials that prevent solid surface colonization or impede touch-transfer of viable microbes could provide means to decrease pathogen transfer from high-touch surfaces in critical applications. ZnO and Ag nanoparticles have shown great potential in antimicrobial applications. Less is known about nano-enabled surfaces. Here we demonstrate that surfaces coated with nano-ZnO or nano-ZnO/Ag composites are not cytotoxic to human keratinocytes and possess species-selective medium-dependent antibiofilm activity against Escherichia coli, Staphylococcus aureus and Candida albicans. Colonization of nano-ZnO and nano-ZnO/Ag surfaces by E. coli and S. aureus was decreased in static oligotrophic conditions (no planktonic growth). Moderate to no effect was observed for bacterial biofilms in growth medium (supporting exponential growth). Inversely, nano-ZnO surfaces enhanced biofilm formation by C. albicans in oligotrophic conditions. However, enhanced C. albicans biofilm formation on nano-ZnO surfaces was effectively counteracted by the addition of Ag. Possible selective enhancement of biofilm formation by the yeast C. albicans on Zn-enabled surfaces should be taken into account in antimicrobial surface development. Our results also indicated the importance of the use of application-appropriate test conditions and exposure medium in antimicrobial surface testing.

Selection of resistance by antimicrobial coatings in the healthcare setting.

Antimicrobial touch surfaces have been introduced in healthcare settings with the aim of supporting existing hygiene procedures, and to help combat the increasing threat of antimicrobial resistance. However, concerns have been raised over the potential selection pressure exerted by such surfaces, which may drive the evolution and spread of antimicrobial resistance. This review highlights studies that indicate risks associated with resistance on antimicrobial surfaces by different processes, including evolution by de-novo mutation and horizontal gene transfer, and species sorting of inherently resistant bacteria dispersed on to antimicrobial surfaces. The review focuses on antimicrobial surfaces made of copper, silver and antimicrobial peptides because of the practical application of copper and silver, and the promising characteristics of antimicrobial peptides. The available data point to a potential for resistance selection and a subsequent increase in resistant strains via cross-resistance and co-resistance conferred by metal and antibiotic resistance traits. However, translational studies describing the development of resistance to antimicrobial touch surfaces in healthcare-related environments are rare, and will be needed to assess whether and how antimicrobial surfaces lead to resistance selection in these settings. Such studies will need to consider numerous variables, including the antimicrobial concentrations present in coatings, the occurrence of biofilms on surfaces, and the humidity relevant to dry-surface environments. On-site tests on the efficacy of antimicrobial coatings should routinely evaluate the risk of selection associated with their use.

Evaluation of the potential hazard of lanthanides to freshwater microcrustaceans.

The use of lanthanides in different sectors of industry has significantly increased during the last decades. Although the "anthropogenic" anomalies of lanthanides in the soils, surface and ground waters have already been registered, the ecotoxicological effects of these elements and their fate in the environment are still insufficiently investigated. In this study acute and long-term toxicity of selected lanthanides (La, Ce, Pr, Nd and Gd) nitrates to freshwater crustaceans Daphnia magna, Thamnocephalus platyurus and Heterocypris incongruens were studied and critically evaluated. The data obtained show that (i) due to the methodical nuances the acute toxicity data of lanthanides are not reliable and have doubtful scientific value even for preliminary toxicity screening and thus should not be used for risk assessment; (ii) toxicity of lanthanides in the 21-day D. magna reproduction test was high whereas the mortality of parent daphnids was more sensitive endpoint than reproduction; (iii) the long-term LC50 values for lanthanides varied from 0.3 to 0.5 mg Ln/L and the differences between individual Ln were not statistically significant. All in all, the results of this study allow us to conclude that the environmental risk assessment of lanthanides should be performed only using long-term toxicity tests. In the environmental risk assessment, lanthanides may be considered as a uniform group of elements with additive mode of action until future investigations will not reveal differences in the ecotoxicity mechanisms of these elements.

Effects of carbon and silicon nanotubes and carbon nanofibers on marine microalgae Heterosigma akashiwo.

The effect of carbon and silicon nanotubes (CNTs and SiNTs) and carbon nanofibers (CNFs) to microscopic marine algae Heterosigma akashiwo was studied, using algal growth inhibition for 3 days (acute effect) and 7 days (chronic effect) as toxicity endpoints. The criterion of the toxic effect was the statistically significant reduction of the number of algal cells in the exposed samples compared to the control. Samples did not demonstrate toxic effects at doses 1 mg/l and 10 mg/l. CNTs and SiNTs samples at 100 mg/l exhibited both acute and chronic toxic effects. We assume that the main cause of cell death in these samples was related to the mechanical damage of cell integrity. CNFs at concentrations of 100 mg/l did not inhibit algal growth, but cells with irregular shapes were observed, which were not observed after exposure to CNTs and SiNTs. Nickel impurities present in CNFs samples are presumably the main cause of observed cell deformations.

Toxicity of antimony, copper, cobalt, manganese, titanium and zinc oxide nanoparticles for the alveolar and intestinal epithelial barrier cells in vitro.

Heavy metals are found naturally on Earth and exposure to them in the living environment is increasing as a consequence of human activity. The toxicity of six different metal oxide nanoparticles (NP) at different points in time was compared using resazurin assay. After incubating Caco2 and A549 cells with 100 µg/mL of Sb2O3, Mn3O4 and TiO2 nanoparticles (NPs) for 24 h no toxic effects were observed while Co3O4 and ZnO NPs had moderate effects and CuO NPs were toxic below 100 µg/mL (24 h EC25 = 11 for A549 and 71 µg/mL for Caco2). The long-term monitoring (up to 9 days) of cells to NPs revealed that the toxic effects of Mn3O4 and Sb2O3 NPs remarkably increased over time. The 9 day EC50 values for Sb2O3 NPs were 22 and 48 µg/mL for A549 and Caco2 cells; and for Mn3O4 NPs were 47 and 29 µg/mL for A549 and Caco2 cells, respectively. In general, the sensitivity of the cell lines in the resazurin assay was comparable. Trans epithelial electrical resistance (TEER) measurements were performed for both cell types exposed to Co3O4, Sb2O3 and CuO NPs. In TEER assay, the Caco2 cells were more susceptible to the toxic effects of these NPs than A549 cells, where the most toxic NPs were the Sb2O3 NPs: the permeability of the Caco2 cell layer exposed to 10 µg/mL Sb2O3 NPs already increased after 24 h of exposure.

Profiling of the reactive oxygen species-related ecotoxicity of CuO, ZnO, TiO2, silver and fullerene nanoparticles using a set of recombinant luminescent Escherichia coli strains: differentiating the impact of particles and solubilised metals.

We propose a novel combination of high-throughput luminescent bacterial tests for the evaluation of the reactive oxygen species (ROS)-generating potential of engineered nanoparticles (eNPs) and the role of solubilised metal ions in this process. The set of tests consists of differently engineered recombinant Escherichia coli strains: (1) a new sensor strain, which bioluminescence is induced by superoxide anions; (2) six recombinant E. coli strains (superoxide dismutase (sod) single, double and triple mutants and a respective wild-type strain), transformed with luxCDABE genes responding to toxic compounds by decreasing their luminescence; and (3) three strains in which bioluminescence is specifically induced by bioavailable metals (Cu, Zn and Ag). The applicability of this battery of tests in profiling oxidative potential of eNPs was evaluated on nTiO(2), nCuO, nZnO and nAg (25, 30, 70 and <100 nm, respectively) NPs and fullerenes. As controls for the size or solubility, the bulk formulations (bTiO(2), bCuO and bZnO) and soluble salts (ZnSO(4), CuSO(4) and AgNO(3)) were also analysed. Bacterial toxicity tests showed that nCuO was four-fold more toxic, and nAg was 15-fold more toxic to triple sod mutant than to wild type (2-h EC(50) values were 8.1 and 2.0 mg Cu l(-1), respectively, and 46 and 3.1 mg Ag l(-1), respectively). Formation of ROS by nCuO and nAg was proved by superoxide anion-inducible strain. The metal sensor bacteria showed that the ROS formation by CuO NPs was caused by solubilised Cu ions, but in case of nAg, particles also had an effect. nZnO was remarkably more toxic to sod triple mutant than to wild type strain (2-h EC(50) were 4.5 and 54 mg Zn l(-1), respectively). Fullerenes inhibited the bioluminescence of sod triple mutant at 3,882 mg l(-1) but had no effect on the wild-type strain even at 20,800 mg l(-1). Nano and bTiO(2) showed some effect on viability of bacteria only at high concentrations (>4,000 mg l(-1)) although nTiO(2) (but not bTiO(2)) induced the bioluminescence of the superoxide anion sensing bacteria starting from 100 mg l(-1). Thus, our innovative combined approach is expected to provide more consistent and informative data concerning the general toxicity, ROS-production potential and also solubilisation of metals in the case of metallic NPs.

Ecotoxicity of nanoparticles of CuO and ZnO in natural water.

The acute toxicity of CuO and ZnO nanoparticles in artificial freshwater (AFW) and in natural waters to crustaceans Daphnia magna and Thamnocephalus platyurus and protozoan Tetrahymena thermophila was compared. The L(E)C(50) values of nanoCuO for both crustaceans in natural water ranged from 90 to 224 mg Cu/l and were about 10-fold lower than L(E)C(50) values of bulk CuO. In all test media, the L(E)C(50) values for both bulk and nanoZnO (1.1-16 mg Zn/l) were considerably lower than those of nanoCuO. The natural waters remarkably (up to 140-fold) decreased the toxicity of nanoCuO (but not that of nanoZnO) to crustaceans depending mainly on the concentration of dissolved organic carbon (DOC). The toxicity of both nanoCuO and nanoZnO was mostly due to the solubilised ions as determined by specific metal-sensing bacteria.

High throughput kinetic Vibrio fischeri bioluminescence inhibition assay for study of toxic effects of nanoparticles.

Despite of the growing production and use of nanoparticles (NPs) in various applications, current regulations, including EC new chemical policy REACH, fail to address the environmental, health, and safety risks posed by NPs. This paper shows that kinetic Vibrio fischeri luminescence inhibition test--Flash Assay--that up to now was mainly used for toxicity analysis of solid and colored environmental samples (e.g. sediments, soil suspensions), is a powerful tool for screening the toxic properties of NPs. To demonstrate that Flash Assay (initially designed for a tube luminometer) can also be adapted to a microplate format for high throughput toxicity screening of NPs, altogether 11 chemicals were comparatively analyzed. The studied chemicals included bulk and nanosized CuO and ZnO, polyethylenimine (PEI) and polyamidoamine dendrimer generations 2 and 5 (PAMAM G2 and G5). The results showed that EC50 values of 30-min Flash Assay in tube and microplate formats were practically similar and correlated very well (log-logR2=0.98), classifying all analyzed chemicals, except nano CuO (that was more toxic in cuvette format), analogously when compared to the risk phrases of the EC Directive 93/67/EEC for ranking toxicity of chemicals for aquatic organisms. The 30-min EC50 values of nanoscale organic cationic polymers (PEI and dendrimers) ranged from 215 to 775 mg/l. Thirty-minute EC50 values of metal oxides varied largely, ranging from approximately 4 mg/l (bulk and nano ZnO) to approximately 100 mg/l (nano CuO) and approximately 4000 mg/l (bulk CuO). Thus, considering an excellent correlation between both formats, 96-well microplate Flash Assay can be successfully used for high throughput evaluation of harmful properties of chemicals (including organic and inorganic NPs) to bacteria.

Ecotoxicological study of Lithuanian and Estonian wastewaters: selection of the biotests, and correspondence between toxicity and chemical-based indices.

The toxicity of industrial and urban wastewater (WW) samples collected in Lithuania and Estonia was evaluated by using a suite of biological tests comprising the Algaltoxkit F with Selenastrum capricornutum, the Charatox with Nitellopsis obtusa, Daphtoxkit F with Daphnia magna, Thamnotoxkit F with Thamnocephalus platyurus, Protoxkit F with Tetrahymena thermophila and the Microtox with Vibrio fischeri. The Charatox and Thamnotoxkit F tests showed highest relative sensitivity, responding to 80-90% of samples, respectively, and both expressed good discrimination capacity between samples. Principal Component and pairwise correlation analysis allowed to select test-battery consisting of Charatox, Thamnotoxkit and Microtox. The WW toxicity was evaluated by means of cumulative indices such as average toxicity (AvTx) and two indices derived from the PEEP-index (Environ. Toxicol. Water Qual. 8 (1993) 115). In addition to these integrated evaluations of test-battery response, WW toxicity was evaluated according to the most sensitive test (MST) in the battery. The linear regression analysis between cumulative toxicity indices and chemical-based indices (derived from comparison of WW chemical concentrations and their respective maximum allowable concentration) revealed positive linear relationships (r(2)=0.7-0.8), while toxicity evaluation based on the MST was less positively related with chemical analysis data (r(2)=0.5-0.6). Although better coincidence between the toxicity and chemical-based assessments was achieved when information from all tests in the battery was assembled, the prediction of toxicity from chemical data was still limited. In search of suitable test-battery for the screening of certain type of WWs, a preliminary study comprising excessive suite of tests might be useful.

Study of the environmental hazard caused by the oil shale industry solid waste.

The environmental hazard was studied of eight soil and solid waste samples originating from a region of Estonia heavily polluted by the oil shale industry. The samples were contaminated mainly with oil products (up to 7231mg/kg) and polycyclic aromatic hydrocarbons (PAHs; up to 434mg/kg). Concentrations of heavy metals and water-extractable phenols were low. The toxicities of the aqueous extracts of solid-phase samples were evaluated by using a battery of Toxkit tests (involving crustaceans, protozoa, rotifers and algae). Waste rock and fresh semi-coke were classified as of "high acute toxic hazard", whereas aged semi-coke and most of the polluted soils were classified as of "acute toxic hazard". Analysis of the soil slurries by using the photobacterial solid-phase flash assay showed the presence of particle-bound toxicity in most samples. In the case of four samples out of the eight, chemical and toxicological evaluations both showed that the levels of PAHs, oil products or both exceeded their respective permitted limit values for the living zone (20mg PAHs/kg and 500mg oil products/kg); the toxicity tests showed a toxic hazard. However, in the case of three samples, the chemical and toxicological hazard predictions differed markedly: polluted soil from the Erra River bank contained 2334mg oil/kg, but did not show any water-extractable toxicity. In contrast, spent rock and aged semi-coke that contained none of the pollutants in hazardous concentrations, showed adverse effects in toxicity tests. The environmental hazard of solid waste deposits from the oil shale industry needs further assessment.

Toxicological Investigation of Soils with the Solid-phase Flash Assay: Comparison with Other Ecotoxicological Tests.

A new direct-contact toxicity test, the solid-phase flash assay, which utilises photobacteria in direct contact with soil particles during the exposure, was evaluated on four soil samples. Samples HTNT1 and HTNT2 originated from former military sites in Germany, and were highly contaminated with nitroaromatics (approximately 20g/kg), lead and polycyclic aromatic hydrocarbons. Samples LMKW1 and LMKW2, from bioremediation stacks in Germany, were mainly contaminated with mineral oils. The solid-phase flash assay was applied to soil-water slurries, and the results were compared with the toxicity data for soil-water extracts obtained by using various conventional ecotoxicological tests, in which photobacteria, crustaceans, protozoa and algae were used as test organisms. The LMKW1 and LMKW2 samples were not toxic (EC20 > 12.5%) according to all the tests applied, except for the Photobacterium phosphoreum conventional luminescence-inhibition test for LMKW1 (15-minute EC20 = 5.4%(. The HTNT1 and HTNT2 samples were toxic according to all the tests applied, with the majority of EC20 values being lower than 1%. The solid-phase flash assay (1 minute of extraction and 30 seconds of exposure time) gave comparable results to the conventional tests. Therefore, this flash assay could be applied as a fast screening test in parallel with conventional toxicity tests that use soil 24-hour extracts. The flash assay results will be ready by the start of the conventional assays, and could serve as range-finders for these slower and more expensive tests.

Predicting the Toxicity of Oil-shale Industry Wastewater by its Phenolic Composition.

The chemical composition and toxicity of five phenolic wastewater samples collected from the Kohtla-Järve (Estonia) oil-shale industry region were analysed. The total phenolic contents (HPLC data) of these samples ranged from 0.7mg/l to 195mg/l. A total of 11 phenolic compounds were found in the wastewater samples, the most abundant being phenol (up to 84mg/l) and p-cresol (up to 74mg/l). Artificial phenolic mixtures were also composed, to mimic the content of phenolic compounds in the wastewater samples. The theoretical toxicities of these artificial mixtures were calculated by using the toxicities of the individual phenolic constituents to photobacteria (the BioTox™ test) and were assumed to have an additive mode of action. From the BioTox data, the additive toxic effects of phenolic compounds in the artificial mixtures were confirmed to be highly probable. The toxicities of the wastewater samples and their artificial phenolic analogues (mixtures) were studied by using a battery of Toxkit microbiotests (Daphtoxkit F™ magna, Thamnotoxkit F™, Protoxkit F™ and Rotoxkit F™) and three photobacterial tests (Microtox™, BioTox™ and Vibrio fischeri 1500). The wastewaters were classified as toxic (two samples), very toxic (two samples) and extremely toxic (one sample). Comparison of the test battery responses showed that the industrial wastewaters were 2-28-fold more toxic than the respective artificial phenolic mixtures. The photobacterial tests proved to be the most appropriate for screening purposes. This was the first attempt to use a test battery approach in the toxicity testing of Estonian wastewaters. The study showed that the toxicity of oil-shale industry wastewaters could not be predicted solely on the basis of their phenolic composition, since only 7-50% of their toxicity was shown to be due to phenolic compounds. It is true, to a certain extent, that the majority of environmental samples are usually very complex and contain various types of pollutants. As even a full chemical analysis (which is very expensive) can easily miss the constituent(s) with the greatest toxic effect(s), the use of toxicity tests in parallel to chemical analysis should be encouraged.

The efficiency of different phenol-degrading bacteria and activated sludges in detoxification of phenolic leachates.

Phenolic composition, toxicity and biodegradability of three different phenolic leachates/samples was studied. Samples A and C were the leachates from the oil-shale industry spent shale dumps at Kohtla-Järve, Estonia. Sample B was a laboratory-prepared synthetic mixture of 7 phenolic compounds mimmicking the phenolic composition of the leachate A. Toxicity of these 3 samples was analyzed using two photobacterial test (BioTox and Microtox), Daphnia test (DAPHTOXKIT F pulex) and rotifiers' test (ROTOXKIT F). All the LC50 values were in the range of 1-10%, leachate A being the most toxic. The growth and detoxifying potential (toxicity of the growth medium was measured using photobacterial tests) of 3 different phenol-utilizing bacteria and acclimated activated sludges was studied in shake-flask cultures. 30% leachate A (altogether 0.6 mM total phenolic compounds) was too toxic to rhodococci and they did not grow. Cell number of Kurthia sp. and Pseudomonas sp. in 30% leachate A increased by 2 orders of magnitude but despite of the growth of bacteria the toxicity of the leachate did not decrease even by 7 weeks of cultivation. However, if the activated sludge was used instead of pure bacterial cultures the toxicity of the 30% leachate A was eliminated already after 3 days of incubation. 30% samples B and C were detoxified by activated sludge even more rapidly, within 2 days. As the biodegradable part of samples A and B should be identical, the detoxification of leachate A compared to that of sample B was most probably inhibited by inorganic (e.g. sulphuric) compounds present in the leachate A. Also, the presence of toxic recalcitrant organic compounds in the leachate A (missed by chemical analysis) that were not readily biodegradable even by activated sludge consortium should not be excluded.

The growth rate control in Escherichia coli at near to maximum growth rates: the A-stat approach.

The growth characteristics of Escherichia coli K-12 in the continuous culture with a smooth increase in the dilution rate (A-stat) of various carbon sources (glucose, acetate, succinate, glycerol, lactate, acetate + succinate, casamino, acids + glucose) were studied. For all substrates studied the maximum value of specific respiration rate, QO2, remained between 14-18 mmol O2 h-1 g dwt-1 and the maximum growth rate varied from 0.22 h-1 on acetate to 0.77 h-1 on glucose + casamino acids. After the respiratory capacity of the cells was exhausted at growth rates mu > mu crit, the growth yield YXO2, increased slightly when the dilution rate increased. The maximum growth rate of Escherichia coli K12 was dependent on growth yield, respiratory capacity and glycolytic capacity of the strain. Analysis of the cultivation data using a stoichiometric flux model indicated that ATP synthesis in E. coli exceeds by two-fold that (theoretically) required to build up biomass. The experimental value of mATP < 4 mmol ATP h-1 g dwt-1 determined from A-stat cultivation data was low compared with the calculated 'unproductive hydrolysis' of ATP (64-103 mmole ATP g dwt-1).

Study of the photochemical and phototoxic properties of lonidamine [1-(2,4-dichlorobenzyl)-1H-indazol-3-carboxylic acid].

Lonidamine (LND) is an antispermatogenic and antitumour agent acting via inhibition of the energy metabolism. According to our results LND in vitro acted as a photosensitizer enhancing synergistically the lethal action of UV radiation (lambda max = 330 nm, the range between 260-390 nm) towards Ehrlich carcinoma cells (EAC). The primary targets of phototoxic action of LND probably were cell membranes and mitochondria. UV irradiation of EAC in the presence of LND increased the permeability of the plasma membranes, stimulated the photoperoxidation of lipids, enhanced the inhibition of dehydrogenase activity and oxygen consumption of the cells. Deficiency of oxygen substantially decreased phototoxicity of LND. LND may induce photosensitized destruction of biomolecules by acting through type 1 and 2 reactions. It could be supposed that negative side effects of LND (e.g., photophobia and photosensitivity that have been reported for some cancer patients treated with LND) could be associated with its photosensitizing properties.

Role of adenine nucleotides in the regulation of bacterial energy metabolism: theoretical problems and experimental pitfalls.

The effect of growth rate on ATP pool and adenylate energy charge (EC) value of Escherichia coli has been studied in batch culture on different media (mu max varying from 0.1 h-1 to 1.2 h-2) and in continuous culture at dilution rates (D = mu) from 0.045 h-1 to 0.310 h-1. Within the limits of error both ATP pool and EC values did not change with alterations in the relative growth rate of E. coli. The effect of in vivo EC values on experimental errors in ATP, ADP and AMP measurements with the luciferin-luciferase method, and, subsequently, on measurements of different ratios between adenylates, as in the case of adenylate kinase in vivo equilibrium, is discussed.

On characterization of the growth of Escherichia coli in batch culture.

Several growth monitoring parameters, including adenine nucleotide contents, were measured during Escherichia coli K12 batch cultivation in mineral medium with glucose. The adenylate energy charge with its mean value of 0.83 remained roughly stable during growth. The total adenylate and ATP pools (nmol/mg dry weight), and also the individual cell volume changed with a pattern of two maxima at approximately 4 and 10 h of cultivation. After the exhaustion of the glucose from the growth medium the adenylate energy charge, the pools of ATP and total adenylate started to decrease marking the onset of the stationary growth phase. Our data indicate that actually there was only a limited period within the logarithmic growth phase during which the growth might have been balanced: during this period of 1.5 h different growth monitoring parameters (optical absorbance, cell number, total cell volume, and ATP content per ml) increased with almost equal rates. Moreover, as ATP pool and median cell volume during this short period were approximately constant, the culture might have been even in the steady state.