Assessment of genotoxic effects induced by selected pesticides on RTG‐2 fish cells by means of a modified fast micromethod assay

The cytotoxic and genotoxic effects induced by alachlor and dichlorvos, two pesticides broadly used, were studied on RTG‐2 fish cell line. As measure of cytotoxicity, neutral red assay was used to determine the cellular viability. Toxicity ranking based on IC₅₀ values found that alachlor was more cytotoxic than dichlorvos. DNA damage has been evaluated on RTG‐2 cultures by means of an in vitro assay based on the ability of PicoGreen® fluorochrome to interact preferentially with double‐stranded DNA (dsDNA), and the results indicated that alachlor induced DNA strand breaks at concentrations above 1.52 μg/mL, equivalent to 1/50‐EC₅₀₍₄₈₎, whereas exposures to dichlorvos induced DNA damage only at the maximal concentrations tested 25 μg/mL (1/10‐EC₅₀₍₄₈₎). These results confirm the suitability of this method for the screening of genotoxic effects of this type of aquatic pollutants, and we suggest their use in hazard assessment for environmental risk procedures. © 2010 Wiley Periodicals, Inc. Environ Toxicol, 2012.     

Genotoxic effects of polychlorinated biphenyls (PCB 153, 138, 101, 118) in a fish cell line (RTG-2)

Polychlorinated biphenyls (PCBs) are persistent pollutants in aquatic environments, often causing the decline or disappearance of wild populations. The primary aim of this study was to investigate the genotoxic effects of some PCBs (PCB153 (2,2′,4,4′,5,5′-hexachlorobiphenyl) and 138 (2,2′,3,4,4′,5′-hexachloro-biphenyl), both non-dioxin-like compounds, and the pentachlorobiphenyls PCB118 (2,3′,4,4′,5-) and 101 (2,2′,4′,5,5′-), the former an ortho-substituted, low-affinity dioxin-like compound and the latter a non-coplanar congener classified as non-dioxin-like) in fish cells (RTG-2). These congeners are mostly present in surface waters and in edible aquatic organisms and the loss of DNA integrity in vitro serves as a sensitive biomarker of cytogenetic alterations and is considered as an initial step for the identification of genotoxic effects.The alkaline comet assay and the micronucleus test show clear genotoxic damage after short and longer exposure (2 and 24 h) to maximum soluble, non-cytotoxic doses, evident sooner with PCBs 101 and 118. Oxidative stress situations involving ROS release, reduction in total GSH, lipid peroxidation and alteration to superoxide dismutase, seen after exposure with all the congeners, though with different kinetics, seem the most likely explanation for the genotoxic damage. This appears to be confirmed by the modified comet assay (pH 10) for detection of oxidized bases using endonuclease III. The increased generation of intracellular ROS might explain the apoptosis seen after treatment with the single PCBs and evaluated on the basis of the rise in 3-7 caspase activity. Therefore both the non-coplanar, non-dioxin-like PCBs (153, 138, 101) and the low-affinity dioxin-like compound PCB118 cause evident genotoxic damage, probably as a consequence of oxidative stress.     

Cytotoxic and genotoxic effect in RTG-2 cell line exposed to selected biocides used in the disinfection of cooling towers

The cytotoxic and genotoxic effects induced by trichloroisocyanuric acid, Oxone, and sodium bromide, active principles included in formulations for cleaning and disinfection of cooling towers, were studied on RTG-2 cell line. Neutral red assay was used to determine the cellular viability. Toxicity ranking based on IC(50) values found that trichloroisocyanuric acid was the most cytotoxic biocide tested followed by Oxone, whereas sodium bromide resulted in a very low cytotoxicity. DNA damage has been evaluated on RTG-2 cultures by means of an in vitro assay based on the ability of PicoGreen fluorochrome to interact preferentially with dsDNA, and the results indicated that trichloroisocyanuric acid induced DNA strand breaks at concentrations above 1.2 mg/l, equivalent to 1/50-EC(50(48)), whereas exposures to Oxone and sodium bromide did not induce DNA damage at the maximal concentrations tested (1/10-EC(50(48))). These results confirm the suitability of this method for the screening of genotoxic effects of this type of aquatic pollutants, and we suggest their use in environmental risk assessment procedures.     

Acute and subacute toxic effects produced by microcystin-YR on the fish cell lines RTG-2 and PLHC-1

Approximately 80 microcystins (MCs) variants have been isolated in surface water worldwide. The toxicity of the most frequently MCs are encountered, MC-LR and MC-RR, has been extensively studied in humans and animals. However, studies dealing with MC-YR toxicity are still scarce. In this work, the toxic effects of MC-YR were investigated in the fish cell line PLHC-1, derived from a hepatocellular carcinoma of the topminnow Poeciliopsis lucida, and RTG-2 fibroblast-like cells derived from the gonads of rainbow trout Oncorhynchus mykiss. After 48 h, morphological and biochemical changes (total protein content, neutral red uptake and methylthiazol tetrazolium salt metabolization) were determined. The most sensitive endpoint for both cell lines was the reduction of total protein content, with EC₅₀ values of 35 μM for PLHC-1 cells and 67 μM for the RTG-2 cell line. Lysosomal function and methylthiazol tetrazolium salt metabolization were stimulated at low concentrations, while they decreased at high doses. Increase of piknotic cells, rounding effects, reduction in cell number and cell size, hydropic degeneration, and death mainly by necrosis but also by apoptosis were observed in the morphological study. Furthermore, PLHC-1 cells are more sensitive than RTG-2 cells to MC-YR exposure. These results were similar to those obtained when both cell lines were exposed for 24 h to a Microcystis aeruginosa isolated strain extract containing MC-LR.     

Genotoxic effects of ketamine on CHO cells

Ketamine, a non-barbiturate anaesthetic agent, was studied for its genotoxic potential using the SCE assay. It was genotoxic in the in vitro system at concentrations comparable to the plasma levels achieved during steady state anaesthesia. It had no effects on cellular kinetics in CHO cells.     

Genotoxic effects of profenofos on the marine fish, Therapon jarbua

Profenofos (EC(50)) is a persistent and toxic organophosphorus insecticide. Animals get exposed to profenofos via food and water. The present study was designed to explore the genotoxic effect of profenofos in the marine fish. The ubiquitously occurring marine fish, Therapon jarbua, was exposed to profenofos and its effect on DNA was measured using comet (single-cell gel electrophoresis) assay. DNA damage were scored using mean percentage of tail length and compared with the comet classes' viz., 0, 1, 2, 3, and 4. In the first three doses, the (21.5, 43.0 and 86.0 μg L(-1)) comets were observed, of which the mean tail length differed significantly (p?相似文献   

In vitro toxicity of antimicrobials on RTG-2 and RTL-W1 fish cell lines

This study proposed a battery of endpoints based on in vitro fish cell lines. Two fish cell lines and four toxicity endpoints are considered. The tetracycline (TC), oxytetracycline (OTC), sulfachlorpyridazine (SCP), and septrin(?) (ST) were selected as model antimicrobials and chlorpyrifos as positive control. EROD was induced by septrin(?) (formulation containing sulfamethoxazole and trimethoprim) at concentrations higher than 20mg/L, but inhibited by tetracycline, oxytetracycline and chlorpyrifos. Dose dependent inhibition responses were observed for β-galactosidase (β-Gal) activity in cells exposed to septrin(?), tetracycline or oxytetracycline. The EROD EC50s ranged between 2.29×10(-2)mg/L (chlorpyrifos) and 167.63mg/L (tetracycline). The β-Gal EC50s ranged between 22.1 (septrin(?)) and 84.59mg/L (tetracycline). Data suggest that in vitro testing using a battery of endpoints can be a cost-effective solution for screening the toxicity of antimicrobials on fish. The absence of in vitro effects at concentrations well above those expected/measured in the environment may replace the need for conducting acute lethality tests on fish.     

Genotoxic and hematological effects of chlorpyrifos exposure on freshwater fish Labeo rohita

Chlorpyrifos is a commonly used organophosphate insecticide that causes toxicological effects in aquatic organisms especially in fish. This study determined the effects of chlorpyrifos on the genotoxic and hematological parameters of freshwater fish, Labeo rohita. The genotoxic effects of different sublethal concentrations of chlorpyrifos were investigated in the erythrocytes of Labeo rohita (commonly known as Rohu) using the Micronucleus test. Effects of chlorpyrifos on the hematological parameters of the fish were also observed. Fish specimens were exposed to three sublethal concentrations of chlorpyrifos viz., sublethal I (SL-I, 1/6th of LC₅₀?=?～73.8?μg/L), sublethal II (SL-II, 1/4th of LC₅₀?=?～110.7?μg/L) and sublethal III (SL-III, 1/2nd of LC₅₀?=?～221.4?μg/L) for 96?h. Blood samples were collected at every 24?h and were subjected to the Micronucleus assay. The observed micronucleus frequencies were concentration and time-dependent. The MN induction was significantly highest (p?相似文献   

Genotoxic and mutagenic effects of erythrosine B,a xanthene food dye,on HepG2 cells

Erythrosine (ErB) is a xanthene and an US Food and Drug Administration approved dye used in foods, drugs and cosmetics. Although its utilization is permitted, ErB is described as inhibitor of enzymes and protein–protein interactions and is toxic to pituitary and spermatogenesis processes. However, the genotoxicity and mutagenicity of ErB is inconclusive in the literature. This study aimed to analyze the genotoxicity of this dye using the alkaline comet assay and is the first investigation to evaluate ErB mutagenicity using the cytokinesis block micronucleus cytome (CBMN-Cyt) assay in HepG2 cells. These cells were chosen because they produce phase I and phase II enzymes that can mimic in vivo metabolism. The cells were treated with seven concentrations (0.1–70.0 μg mL⁻¹) of ErB, and the results showed genotoxicity at the two highest concentrations and mutagenicity at six concentrations. Furthermore, as micronuclei result from clastogenic and aneugenic processes, while comet assay is often considered more sensitive and detects DNA single strain breaks, we suggest that an aneugenic is responsible for the observed damage. Although ErB is approved for use in the food, cosmetic and pharmaceutical industries, it must be used carefully because it damages the DNA structure.     

Genotoxic and cytotoxic potential of titanium dioxide (TiO2) nanoparticles on fish cells in vitro

Intrinsic genotoxic and cytotoxic potential of titanium dioxide (TiO2) engineered nanoparticles (ENPs) were evaluated in a metabolically competent, established fish cell line derived from rainbow trout (Oncorhyncus mykiss) gonadal tissue (i.e. RTG-2 cells). Prior to evaluation of the toxic potential, mean size of the ENPs was determined using transmission electron microscopy (TEM). As a prerequisite, an extensive characterisation of the ENPs was carried out following sonication which enabled the synthesis of an efficient dosing strategy for the cells in which exposure in phosphate buffered saline (PBS) gave an optimal agglomeration effects compared to distilled water (H2O) and minimal essential media (MEM). Interaction of the ENPs with cells under scanning electron microscope (SEM) was also studied. The genotoxic and cytotoxic potential of the ENPs were determined either alone or in combination with ultraviolet radiation (i.e. UVA). Whilst genotoxic potential was determined by evaluating DNA strand breaks using single cell gel electrophoresis (SCGE) or the comet assay and induction of cytogenetic damage using cytokinesis-blocked micronucleus (MN) assay, cytotoxicity was determined by measuring the retention of supra vital stain, neutral red, by the lysosomes using the neutral red retention (NRR) assay. In addition, while performing the comet assay, lesion specific bacterial endonuclease, formamidopyrimidine DNA glycosylase (Fpg), which recognises oxidised purine bases, was used to determine oxidative DNA damage. The results suggested that the highest concentration of the ENPs (i.e. 50 microg ml(-1)) did not produce elevations in DNA damage over 4 h (comet assay), 24 h (modified comet assay) or 48 h (MN assay) exposures in the absence of UVA irradiation, although there was a significant reduction in lysosomal integrity over 24 h exposure (NRR assay). The induction of MN did not show any enhanced levels as a function of ENP concentration. A significantly increased level of strand breaks was observed in combination with UVA (3 kJ m(-2)). In general, the NRR assay suggested elevated levels of cytotoxicity when the UVA exposure was carried out with MEM compared to PBS, although both showed an increase when in combination with the highest concentration of ENPs (i.e. 50 microg ml(-1)). Overall, the study emphasises the need for adoption of an holistic approach while evaluating the potential toxic effects of ENPs in which appropriate measures should be taken to avoid agglomeration or aggregation to facilitate efficient cellular uptake to evaluate potential biological responses.     

Genotoxic effects induced by beta-myrcene following metabolism by liver HepG2/C3A human cells

Beta-myrcene [or myrcene (1,6-Octadiene, 7-methyl-3-methylene-)] and the essential oils containing this monoterpene have been widely used in cosmetics, detergents, and soaps, and as flavoring additives for food and beverages. Due to the potentially high level of human exposure to beta-myrcene, and absence of studies involving its genotoxicity in human cells, the aim of this study was to investigate the cytotoxic and genotoxic potential of this terpenoid in non-metabolizing cells (leukocytes) and liver metabolizing cells (HepG2/C3A cells). Prior to the genotoxic assessment by the comet and micronucleus (MN) assays, a range of beta-myrcene concentrations was tested in a preliminary MTT assay. Regarding the MTT assay, the results showed cytotoxic effects for leukocytes at 250 µg/ml and higher concentrations, while for HepG2/C3A cells, absence of cytotoxicity was noted relative to all tested concentrations (after 24 hr exposure). Thus, the concentrations of 2.5, 10, 25, 50, and 100 µg/ml for leukocytes, and 2.5, 100, and 1000 µg/ml for HepG2/C3A cells were selected for subsequent assays. Genotoxicity evaluation demonstrated significant DNA damage in the comet assay and significant chromosomal abnormalities including nucleoplasmic bridges and nuclear buds in HepG2/C3A cells at beta-myrcene concentrations of 100 and 1000 µg/ml. Under our experimental conditions, caution is recommended in the use of beta-myrcene, since this compound produced genotoxic effects especially after metabolic activation using human HepG2/C3A cells, which may be associated with carcinogenic and teratogenic effects previously reported in the literature.     

The use of the fish cell lines RTG-2 and PLHC-1 to compare the toxic effects produced by microcystins LR and RR.

Cyanobacterial toxins, especially microcystins (MC), are found in eutrophied waters through the world. Acute poisonings of animals and humans has been reported following MC exposure. In the present study, two fish cell lines, PLHC-1 and RTG-2, were evaluated after exposure to the cyanobacterial toxins MC-LR and MC-RR. The effects of different concentrations of the toxins were investigated in both cell lines at morphological and biochemical levels (total protein content, lactate dehydrogenase leakage, lysosomal activity and succinate dehydrogenase activity). The results obtained showed a decrease in protein content and no relevant increase in cell disruption, except for MC-LR in PLHC-1 cells. Morphological changes produced by microcystins were cellular swelling, blebbling, rounding, reduction in the cell number and increase in the number and size of lysosomal bodies. In addition, steatosis was produced in hepatoma PLHC-1 cells, particularly with MC-RR. Furthermore, the fish PLHC-1 cell line was more sensitive than RTG-2 cells to the cyanobacterial toxins compared, being the stimulation of the lysosomal function and the induction of steatosis the most specific changes detected.     

Genotoxic effects of ochratoxin A in human-derived hepatoma (HepG2) cells.

Ochratoxin A (OTA) is a widespread mycotoxin that occurs in many commodities from grains to coffee beans all over the world. Evidence is accumulating that OTA may cause cancer in humans. The compound was tested in micronucleus (MN) and single-cell gel electrophoresis (SCGE) assays in human-derived hepatoma (HepG2) cells and caused pronounced dose-dependent effects at exposure concentrations of 5 microg/ml and greater. On the contrary, no induction of His(+) revertants was found in Salmonella microsome assays with strains TA98 and TA100 with HepG2-derived enzyme (S9) mix in liquid incubation assays under identical exposure concentrations. Taken together, our results indicate that OTA is clastogenic in the human-derived cells. These findings support the assumption that this mycotoxin may cause genotoxic effects in hepatic tissue of humans.     

Genotoxic effects in fish induced by pharmacological agents present in the sewage of some Italian water‐treatment plants

The presence of pharmaceutical substances in the municipal effluents is currently considered the principal source of bio‐active molecule emissions into aquatic environments. This study analyzes the genotoxic damage caused by gemfibrozil and atorvastatin, two regulators of the hematic level of lipids, and sildenafil citrate, a vasodilator, on the teleost Danio rerio. The genotoxicity of these three compounds was evaluated using the comet assay, diffusion assay, and RAPD‐PCR. The alkaline version (pH 12.1) of the comet assay was used for the erythrocytes of the zebrafish to evaluate the presence of single strand DNA breaks. Furthermore, the diffusion assay was used to estimate the number of apoptotic cells. The fish were treated with the three pharmacological agents at the average concentrations previously found at some Italian treatment plants and were then sacrificed from 5 to 35 days after exposure. The data of the comet assay showed a statistically significant loss of DNA integrity after 5 days of exposure to atorvastatin and after one week of exposure to gemfibrozil. This damage was, however, repaired after 14 days. Sildenafil citrate produced, instead, a statistically significant loss of DNA integrity at the concentrations found only after 35 days of exposure. The genotoxicity at the molecular level was tested by RAPD‐PCR. The results from this investigation are in agreement with those from two other tests, confirming the efficacy of the use of the three experimental approaches for the complete evaluation of genotoxic damage. © 2010 Wiley Periodicals, Inc. Environ Toxicol, 2012.     

Genotoxic and oxidative stress-inducing effects of deltamethrin in the erythrocytes of a freshwater biomarker fish species, Channa punctata Bloch

Deltamethrin, an alpha-cyano class of pyrethroid insecticide is used in insect pest control and antimalaria programs in several countries including India. Although various toxic manifestations of deltamethrin are reported in mammals, its ecotoxicologic dimensions are not adequately researched in ecologically and commercially important fishes. In this study, we report genotoxic effect of deltamethrin in a biomarker fish Channa punctata (Bloch). Adult fish were exposed to three concentrations of technical grade deltamethrin (0.4, 0.8, and 1.2 microg/L) for 48 and 72 h. Ethyl methane sulfonate was used as a positive control. Fish were analyzed for induction of micronucleus (MN), nuclear abnormalities (NAs), and oxidative stress biomarkers in erythrocytes. Deltamethrin significantly induced MN and NAs accompanied by increased lipid peroxidation. Activity of antioxidant enzyme superoxide dismutase was significantly decreased but an increase was observed in reduced glutathione level after 72 h of exposure. The NAs in exposed fish included blebbed, lobed and notched nuclei, and binucleated erythrocytes. Our findings suggest that oxidative stress may, in part, be contributing to deltamethrin-induced genotoxic damage to erythrocytes. Although MN induction is a nonspecific biomarker, it may provide an indication of pollution load of deltamethrin in the affected fish population when used as part of suite of other biomarkers.     

Genotoxic effects of old landfill leachate on HepG2 cells after nitration/ultrafiltration/reverse osmosis membrane treatment process

Toxicity assessment of nitration/ultrafiltration/reverse osmosis (nitration/UF/RO) project, which has recently been widely used as an efficient process with applications in practical leachate treatment, was very limited. In the present study, DNA damage of leachates was investigated before and after the nitration/UF/RO process by a battery of assays with human hepatoma cells. Methyletrazolium assay showed a high cytotoxicity of 97.1% after being exposed to the highest concentration of raw leachate for 24 h, and a cytotoxicity of 26% in effluent at a concentration of 30% (v /v). Both comet assay (24 h) and γH2AX flow cytometer assay (3 h) showed increased levels of DNA damage in cells exposed to raw leachate and after nitration/UF‐treated leachate followed by a significant increase of 7‐ethoxyresorufin‐O‐deethylase activity. However, the effluent after nitration/UF/RO treatment showed no significant difference compared to negative control for γH2AX flow cytometer assay but slight DNA damage at concentrations of 20% and 30% (v /v) as well as increase of 7‐ethoxyresorufin‐O‐deethylase. Analysis showed that nitration/UF/RO process exhibited high removal of physicochemical indexes and significant reduction of toxic and genotoxic effects of leachate, but still demands an improvement to reduce all possible negative risks to the environment and humans. Copyright © 2017 John Wiley & Sons, Ltd.     

Genotoxic effects of silver nanoparticles with/without coating in human liver HepG2 cells and in mice

With the rapid expansion of human exposure to silver nanoparticles (AgNPs), the genotoxicity screening is critical to the biosafety evaluation of nanosilver. This study assessed DNA damage and chromosomal aberration in the human hepatoma cell line (HepG2) as well as the effects on the micronucleus of bone marrow in mice induced by 20 nm polyvinylpyrrolidone‐coated nanosilver (PVP‐AgNPs) and 20 nm bare nanosilver (AgNPs). Our results showed that the two types of AgNPs, in doses of 20‐160 μg/mL, could cause genetic toxicological changes on HepG2 cells. The DNA damage degree of HepG2 cells in 20 nm AgNPs was higher than that in 20 nm PVP‐AgNPs, while the 20 nm PVP‐AgNPs caused more serious chromosomal aberration than 20 nm AgNPs. Both kinds of AgNPs caused genetic toxicity in a dose‐dependent manner in HepG2 cells. In the micronucleus test on mouse bone marrow cells, in doses of 10, 50 and 250 mg/kg body weight administered orally for 28 days once a day, the two kinds of AgNPs have no obvious inhibitory effect on the mouse bone marrow cells, and the effect of chromosome aberration could be documented at the high dose of 250 mg/kg. These results suggest that AgNPs have genotoxic effects in HepG2 cells and limited effects on bone marrow in mice; both in vitro and in vivo tests could be of great importance on the evaluation of genotoxicity of nanosilver. These findings can provide useful toxicological information that can help to assess genetic toxicity of nanosilver in vitro and in vivo.     

Genotoxic and cytotoxic effects and gene expression changes induced by fixed orthodontic appliances in oral mucosa cells of patients: a systematic review

Abstract

Context: The accumulation of chronic or severe acute DNA and cellular damage in oral mucosa cells is one of the main factors that help initiate a wide range of malignant lesions in the oral cavity. There has been considerable controversy in the literature about the effect of such sustained genotoxic and cytotoxic damage to oral mucosa cells.

Objective: The aim of this systematic review, reported in accordance with Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) guidelines, is to investigate the effects of such interventions.

Methods: Electronic and manual searches were performed (15 May 2015) for Randomized Clinical Trials/quasi-Randomized Clinical Trials that analyzed the genotoxic/cytotoxic effects of these types of oral appliances in humans. A primary outcome (cell/DNA damage) and a number of secondary outcomes were examined. Two reviewers carried out the study selection and performed a “risk of bias” assessment [Cochrane Collaboration's tool]. Wherever possible the meta-analysis was conducted on homogenous groups.

Results: From the electronic search (2797), 6 studies met the eligibility criteria. Most studies (5/6) observed significant differences in most comparisons at the short-term (1-3 months) and long-term (24–48 months) evaluations, with respect to critically acute genotoxic/cytotoxic effects. Some of the studies (2/3) concluded that the post-removable effects at DNA/cellular levels were not significant (p?>?0.05) with respect to the controls.

Conclusions: Acute DNA/cellular damage in oral mucosa cells is induced by orthodontic appliances. Nevertheless, even though these effects were no longer detected after removing the appliances, more rigorous RCTs are needed to explore the extent to which acquired damage can be observed in the oral mucosa.     

Genotoxic effects of aluminum, iron and manganese in human cells and experimental systems: a review of the literature

There is considerable evidence indicating an increase in neurodegenerative disorders in industrialized countries. The clinical symptoms and the possible mutagenic effects produced by acute poisoning and by chronic exposure to metals are of major interest. This study is a review of the data found concerning the genotoxic potential of three metals: aluminum (Al), iron (Fe) and manganese (Mn), with emphasis on their action on human cells.