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Using factorial experiments to study the toxicity of metal mixtures.

Two-level factorial experiments were employed in this study for understanding and predicting the toxicity of binary and ternary metal mixtures. Toxicity of metal mixtures with concentrations between the respective EC10 and EC80 values was experimentally measured. Models were fit to the experimental data and the resultant models were of high quality as reflected by R2 (coefficient of determination). Interactions between mixture components were indicated by the existence of statistically significant interaction terms in the models. Toxicity predictions based on the models were compared with observed toxicity for binary and ternary metal mixtures. The models developed did not assume additivity between metals, were simple and interpretable, and gave satisfactory predictions of the toxicity of metal mixtures in aqueous solutions without requiring knowledge on synergism or antagonism.

Bacterial Proteins↗

Modeling photoinduced algal toxicity of polycyclic aromatic hydrocarbons.

The influence of light conditions on the toxicity of polycyclic aromatic hydrocarbons (PAHs) to different organisms has long been recognized. The aim of this study was to investigate whether previously proposed models can be used to qualitatively and quantitatively predict photoinduced toxicity to the green algae Scenedesmus vacuolatus. For this purpose 14 different PAH compounds were tested under three different light conditions for their effects on the algae reproduction. Illumination conditions comprised standard algae growth light, simulated sunlight aiming to mimic environmental light conditions, and UV-filtered light in order to minimize light influence on PAH toxicity. Models proposed for the prediction of photoinduced toxicity were modified in order to account for different exposure conditions and toxic endpoints used in the bioassay. The results of this study show that the gap between the highest occupied molecular orbital (HOMO) and the lowest unoccupied molecular orbital (LUMO) proposed as an indication for photoinduced toxicity to Daphnia magna can be used as a qualitative indication of a potential photoinduced toxicity to the green algae Scenedesmus vacuolatus. The impact of light conditions on PAH toxicity can be quantified by a linear model which allows the estimation of the ED50 of each compound from the amount of absorbed photons and an empirically determined relative phototoxic efficacy value of the compound.

Chlorophyta↗

Application of a sigmapolycyclic aromatic hydrocarbon model and a logistic regression model to sediment toxicity data based on a species-specific, water-only LC50 toxic unit for Hyalella azteca.

Two models, a sigmapolycyclic aromatic hydrocarbon (PAH) model based on equilibrium partitioning theory and a logistic-regression model, were developed and evaluated to predict sediment-associated PAH toxicity to Hyalella azteca. A sigmaPAH model was applied to freshwater sediments. This study is the first attempt to use a sigmaPAH model based on water-only, median lethal concentration (LC50) toxic unit (TU) values for sediment-associated PAH mixtures and its application to freshwater sediments. To predict the toxicity (i.e., mortality) from contaminated sediments to H. azteca, an interstitial water TU, calculated as the ambient interstitial water concentration divided by the water-only LC50 in which the interstitial water concentrations were predicted by equilibrium partitioning theory, was used. Assuming additive toxicity for PAH, the sum of TUs was calculated to predict the total toxicity of PAH mixtures in sediments. The sigmaPAH model was developed from 10- and 14-d H. azteca water-only LC50 values. To obtain estimates of LC50 values for a wide range of PAHs, a quantitative structure-activity relationship (QSAR) model (log LC50 - log Kow) with a constant slope was derived using the time-variable LC50 values for four PAH congeners. The logistic-regression model was derived to assess the concentration-response relationship for field sediments, which showed that 1.3 (0.6-3.9) TU were required for a 50% probability that a sediment was toxic. The logistic-regression model reflects both the effects of co-occurring contaminants (i.e., nonmeasured PAH and unknown pollutants) and the overestimation of exposure to sediment-associated PAH. An apparent site-specific bioavailability limitation of sediment-associated PAH was found for a site contaminated by creosote. At this site, no toxic samples were less than 3.9 TU. Finally, the predictability of the sigmaPAH model can be affected by species-specific responses (Hyalella vs Rhepoxynius); chemical specific (PAH vs DDT in H. azteca) biases, which are not incorporated in the equilibrium partitioning model; and the uncertainty from site-specific effects (creosote vs other sources of PAH contamination) on the bioavailability of sediment-associated PAH mixtures.

Animals↗

[Hepatoprotectors containing phospholipids decrease the immunosuppressive effect of prednisolone in rats with experimental toxic hepatitis].

The experiments on rats with a model toxic hepatitis induced by tetrachloromethane showed that hepatoprotectors containing phospholipids (eplir and essentiale) introduced in combination with prednisolone decrease the immunodepressant effect of this glucocorticoid, as manifested by a decrease in the atrophy of thymus and an increase in the amount of blood lymphocytes, the number of splenic blasts, and the functional activity of mononuclear cells in C3b and Fc(gamma) receptors in peritoneal exudate.

Animals↗

Multiple computer-automated structure evaluation study of aquatic toxicity. III. Vibrio fischeri.

An acute toxicity model was constructed on the basis of 901 chemicals tested for toxicity against the luminescent bacteria Vibrio fischeri (formerly Photobacterium phosphoreum, the Microtox test). The model was created using the Multiple Computer-Automated Structure Evaluation (M-CASE) program. The model can correctly predict acute toxicity for 92% of the compounds with an error averaging 0.55 log units per median effect concentration (EC50). The main toxicophores, corresponding to polar and nonpolar narcosis, and other types of reactive chemicals were identified.

Animal Testing Alternatives↗

Relations between environmental black carbon sorption and geochemical sorbent characteristics.

Pyrogenic carbon particles in sediments (soot and charcoal, collectively termed "black carbon" or BC) appear to be efficient sorbents of many hydrophobic organic compounds, so they may play an important role in the fate and toxicity of these substances. To properly model toxicant sorption behavior, it is important to (i) quantify the magnitude of the role of BC in sorption and (ii) elucidate which geochemical BC characteristics determine the strength of environmental BC sorption. Sorption isotherms of d10-phenanthrene (d10-PHE) were determined over a wide concentration range (0.0003-20 microg/L), for five sediments with widely varying characteristics. From the sorption isotherms, we determined Freundlich coefficients of environmental BC sorption, K(F,BCenv. These varied from 10(4.7) to 10(5.5). From the data, it could be deduced that BC was responsible for 49-85% of the total d10-PHE sorption at a concentration of 1 ng/L. At higher concentrations, the importance of BC for the sorption process diminished to <20% at 1 microg/L and 0-1% at 1 mg/L. There were no significant relationships between BC sorption strength and the tested geochemical BC characteristics [the fraction of small (<38 microm) BC particles, the BC resistance to high-temperature oxidation, the fraction of biomass-derived BC, the native polycyclic aromatic hydrocarbon and total organic carbon contents]. Because of the limited variation in BC sorption strength with widely varying BC characteristics, the presented BC sorption coefficients may putatively be used as generic starting points for environmental modeling purposes.

Adsorption↗

Cytotoxicity assessment of antibiofouling compounds and by-products in marine bivalve cell cultures.

Short-term primary cell cultures were derived from adult marine bivalve tissues: the heart of oyster Crassostrea gigas and the gill of clam Ruditapes decussatus. These cultures were used as experimental in vitro models to assess the acute cytotoxicity of an organic molluscicide, Mexel-432, used in antibiofouling treatments in industrial cooling water systems. A microplate cell viability assay, based on the enzymatic reduction of tetrazolium dye (MTT) in living bivalve cells, was adapted to test the cytotoxicity of this compound: in both in vitro models, toxicity thresholds of Mexel-432 were compared to those determined in vivo with classic acute toxicity tests. The clam gill cell model was also used to assess the cytotoxicity of by-products of chlorination, a major strategy of biofouling control in the marine environment. The applications and limits of these new in vitro models for monitoring aquatic pollutants were discussed, in reference with the standardized Microtox test.

Animals↗

SAR modelling of complex phenomena: probing methodological limitations.

The increased acceptance of the use of structure-activity relationship (SAR) approaches to toxicity modelling has necessitated an evaluation of the limitations of the methodology. In this study, the limit of the capacity of the MULTICASE SAR program to model complex biological and toxicological phenomena was assessed. It was estimated that, provided the data set consists of at least 300 chemicals, divided equally between active and inactive compounds, the program is capable of handling phenomena that are even more "complex" than those modelled up to now (for example, allergic contact dermatitis, Salmonella mutagenicity, biodegradability, inhibition of tubulin polymerisation). However, within the data sets currently used to generate SAR models, there are limits to the complexity that can be handled. This may be the situation with regard to the modelling of systemic toxicity (for example, the LD50).

Animals↗

Toxicity of azaarenes.

Heterocyclic compounds by far outnumber the homocyclic PAHs. In addition, they are often more soluble in water, which may imply a greater biological significance of these heterocycles. Yet, most research focuses on the homocyclics, based on the implicit assumption that the mostly higher concentration of the homocyclics rank these compounds as priority compounds. This review critically examines the available evidence and poses questions on the biological activity and environmental risk of one small group of heterocyclics, the azaarenes, which contain one nitrogen atom in one of the aromatic rings. In different sections, the biotransformation and different types of toxicity are discussed in comparison to those of homocyclic PAHs. The last section focuses on the implications for risk assessment of PAHs. Two- and three-ringed azaarenes can be relatively easily transformed by bacteria, fungi, invertebrates, and vertebrates. The presence of the N-moiety in the smaller azaarenes leads to metabolic routes that partly differ from those of the homoaromatic analogues. Major metabolic products of the azaarenes appear to be ketones and mono- or dihydroxylated azaarenes. Microorganisms can further degrade these into multiple oxygen-containing compounds or they can open up the aza-containing aromatic ring and fully metabolize the products. Fungi and vertebrates were shown to produce the mutagenic dihydrodiol metabolites. The metabolism of the larger azaarenes in vertebrates proceeds analogous to homoaromatic PAH, because in these larger molecules the N-moiety has less influence. Transformation of the larger azaarenes by microorganisms proceeds much slower if occurring at all. Direct toxicity data of azaarenes are mostly restricted to the effects of acridine and quinoline on a relatively small number of species. From this limited set it becomes clear that differences between species are relatively small. As with homocyclic PAHs, toxicity generally increases with increasing number of rings, and baseline toxicity models based on homocyclic PAHs do apply. Toxicity differences between isomers indicate that azaarene toxicity cannot be explained by molecular size-related parameters alone, indicating that electronic forces may be important as well. Considering chronic toxicity it becomes clear that the often-used acute-to-chronic-ratios often underestimate specific chronic toxicity, even within the very limited set of chronic data available. In contrast with homocyclic PAHs, photodegradation of azaarenes shows the same degradation products as biological transformation involving monooxygenases. In general, as for homocyclic PAHs, the degree of phototoxicity is related to the UV absorption characteristics of the azaarenes, which makes it possible to apply the QSAR models developed for homocyclic PAHs to azaarenes as well. Recent research on algae showed that UV-A is the main cause of photoenhanced toxicity. Together with the fact that in the water column UV-B is almost absent, this clearly demonstrates the relevance of phototoxicity in the field. Mutagenicity of azaarenes generally proceeds through similar pathways as in homocyclic PAHs, with bay region diol epoxides as major genotoxic metabolites. The N-moiety can, however, result in differences in genotoxic activities between isomers. Carcinogenicity of azaarenes in mammals is generally restricted to four-ringed and larger structures, and mechanisms leading to cancer are similar to those of homocyclic aromatics. An exception to this general pattern is quinoline, which has been shown to induce liver cancer. The present risk assessment for PAHs is solely based on homocyclic PAHs. Yet, from the present review it becomes clear that this approach fails to protect against a vast number of heterocyclic compounds and biotransformation products that may exhibit stronger or other toxic effects than their homocyclic analogues. Therefore, incorporating the role of heterocyclic compounds and their metabolism appears to be a necessity for a reliable risk assessment for polycyclic aromatic compounds. In addition, reliable long-term protection against PAHs demands data on chronic toxicity, including teratogenicity, both for homocyclic as for heterocyclic compounds.

Animals↗

Cellular and metabolic consequences of chronic ischemia on kidney function.

Approximately 15% of end-stage renal disease is attributable to chronic ischemic nephropathy from renovascular disease, representing significant patient morbidity and sizable medical costs. Although the pathophysiology of both ischemic acute renal failure and renovascular hypertension are under intense study, there have been little data obtained on the pathophysiology of chronic ischemic injury to the kidney. Data from studies of renovascular hypertension demonstrate the primary dependence of the stenotic kidney on angiotensin II in maintenance of glomerular filtration rate, although other vascular regulators, such as endothelium-derived nitric oxide and endothelin, may also play a role. Clues to the pathophysiology of cellular injury in chronic ischemic nephropathy can be found in acute models of ischemic injury to the tubules, toxic models of chronic decreased blood flow such as cyclosporine, and from recent pathological studies showing immunologic alterations. Because there are very little data on the cellular mechanisms of chronic ischemic injury to the kidney, this is an important area for laboratory investigation, particularly because the techniques developed both in studies of acute renal ischemia and chronic renovascular hypertension are readily available. Further understanding of the cellular mechanisms of chronic renal ischemia may eventually lead to medical interventions for patients with ischemic nephropathy too ill to undergo major abdominal surgery.

Adenosine Triphosphate↗

Zebrafish as a model for developmental neurotoxicity testing.

BACKGROUND: To establish zebrafish as a developmental toxicity model, we used 7 well-characterized compounds to examine several parameters of neurotoxicity during development. METHODS: Embryos were exposed by semistatic immersion from 6 hrs postfertilization (hpf). Teratogenicity was assessed using a modified method previously developed by Phylonix. Dying cells in the brain were assessed by acridine orange staining (these cells are likely to be apoptotic). Motor neurons were assessed by antiacetylated tubulin staining and catecholaminergic neurons were visualized by antityrosine hydroxylase staining. RESULTS: Atrazine, dichlorodiphenyltrichloroethane (DDT), and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were primarily teratogenic and not specifically neurotoxic. 2,4-dichlorophenoxyacetic acid (2,4-D), dieldrin, and nonylphenol showed specific neurotoxicity; dieldrin and nonylphenol were specifically toxic to catecholaminergic neurons. Malathion, although not teratogenic, showed some nonspecific toxicity. CONCLUSIONS: Teratogenicity measured in 96-hpf zebrafish is predictive of mammalian teratogenicity and is useful in determining whether a compound causes specific neurotoxicity or general developmental toxicity. Induction of apoptosis or necrosis is an indicator of neurotoxicity. An effect on motor neurons in the caudal third of the embryo correlates with expected defects in motility. Overall, our results showed a strong correlation with mammalian data and suggest that zebrafish is a predictive animal model for neurotoxicity screening.

Animals↗

Application of bacterial growth kinetics to in vitro toxicity assessment of substituted phenols and anilines.

Bacterial growth kinetics were applied to determine toxicity of substituted phenols and anilines serving as model toxicants. The effects observed on Escherichia coli can be quantified reliably. Additional information is obtained about the onset, the duration, and the time course of the toxic action. For most compounds under study a uniform mode of toxicity was observed, but multihalogen-and/or nitrosubstituted phenols differ in toxicity pattern. Possible reasons for the change in mechanism were examined. A comparison with published quantitative data for fish toxicity of halogenated phenols indicates good agreement with toxic effects observed in E. coli cultures. This may lead to the possibility of replacing the more costly, less stable fish test system by this simple and reliable in vitro test system.

Aniline Compounds↗

Impact of metal sorption and internalization on nitrification inhibition.

The goal of this study was to explore the relationship between metal extracellular sorption, intracellular accumulation, and nitrification inhibition. Metal sorption on nitrifying biomass was rapid and could be described by linear partitioning with partition coefficients (Kp) of 20.3 +/- 0.1, 0.4 +/- 0.0, 0.1 +/- 0.0, and 0.2 +/- 0.0 L/g biomass chemical oxygen demand for Cu, Zn, Ni, and Cd, respectively. On the other hand, intracellular Zn, Ni, and Cd concentrations continued to increase with time beyond 12 h after metal addition, whereas intracellular Cu attained equilibrium after 4 h. Metal internalization kinetics could be described by an intraparticle diffusion model, with characteristic diffusion time constants (td) of 9.4, 64.6, 80.5, and 66.1 h for Cu, Zn, Ni, and Cd, respectively. Ultimate internalized percentages of the total cell-associated metal were 1.4 +/- 0.0, 4.3 +/- 0.5,7.6 +/- 1.0, and 2.7 +/- 0.2% for Cu, Zn, Ni, and Cd, respectively. Nitrification inhibition was not a function of the sorbed metal fraction but correlated well with intracellular Zn, Ni, or Cd fractions. An intraparticle diffusion model coupled with a saturation-type biological toxicity model fit the inhibition data for varying initial Cd concentrations and exposure periods. In contrast, no relationship between intracellular or sorbed Cu concentrations and nitrification inhibition was observed. In the presence of 1 mM Cu, less than 13.3 +/- 10.5% cells remained viable as compared to 72.8 +/- 7.5,104.8 +/- 1.7, and 84.7 +/- 7.0% (assumed 100% viable cells in metal-free control) in the presence of 1 mM Zn, Ni, and Cd, respectively. Hence, the observations that inhibition by metals such as Zn, Ni, and Cd is related to their intracellular fraction and the slow kinetics of metal internalization indicate that metal inhibition can easily be underpredicted from short-term batch assays. Furthermore, the inhibitory mechanism of Cu was very different from Zn, Ni, and Cd and may involve rapid loss of membrane integrity.

Adsorption↗

On the generation and outcome of 3-(N-phenylamino)propane-1,2-diol derivatives in deodorized model oils related to toxic oil syndrome.

Toxic Oil Syndrome (TOS) was a massive food-born intoxication that occurred in Spain in 1981 and affected more than 20,000 people. TOS was attributed to the ingestion of rapeseed oil that had been adulterated with aniline, illegally refined, and delivered for human consumption. Two chemical species derived from aniline have been identified in oil batches: fatty acid anilides, qualified as biomarkers of the adulterated oil, and fatty acid esters of 3-(N-phenylamino)propane-1,2-diol (PAP), considered toxic oil biomarkers. These esters were generated by chemical processes during oil refining, specifically in the deodorization step, which involves treatment of the oil at high temperatures under vacuum to remove volatile contaminants. Since PAP derivatives are strongly associated with TOS, their formation and putative interconversion in a toxic oil model has been studied. The main results obtained are (i) only triglycerides and aniline are required to produce PAP esters, thus eliminating the possibility that unknown activators present in the deodorization tank were required for toxification of the oil; (ii) PAP and PAP mono- and diesters are chemically interrelated, as are anilides and PAP esters to an even higher degree. In addition to the reaction of aniline with triglycerides, anilides can be also formed via attack of PAP esters by aniline. However, the most important source of anilides during deodorization seems to be the thermal decomposition of PAP esters. Overall, these results suggest that the generation and outcome of PAP derivatives during deodorization is a complex scenario whereby PAP esters are not only generated from different reactions but decompose to produce anilides, among other compounds. In addition to providing a rapeseed oil model that reproduces the composition of case oils with respect to anilides and PAP derivatives, the results presented herein further support the hypothesis imputing PAP diesters or their metabolites for the intoxication episode.

Anilides↗

Reactive oxygen and nitrogen species: weapons of neuronal destruction in models of Parkinson's disease.

Parkinson's disease (PD) is a common neurodegenerative disease whose etiology and pathogenesis remain mainly unknown. To investigate its cause and, more particularly, its mechanism of neuronal death, numerous in vivo experimental models have been developed. Currently, both genetic and toxic models of PD are available, but the use of neurotoxins such as 6-hydroxydopamine, paraquat, 1-methyl-4-phenyl-1,2,3,6-tetrahydropyridine, and rotenone are still the most popular means for modeling the destruction of the nigrostriatal dopaminergic neurons seen in PD. These four neurotoxins, although distinct in their intimate cytotoxic mechanisms, kill dopaminergic neurons via a cascade of deleterious events that consistently involves oxidative stress. Herein, we review and compare the molecular mechanisms of 6-hydroxydopamine, paraquat, 1-methyl-4-phenyl-1,2,3,6- tetrahydropyridine, and rotenone, placing the emphasis of our discussion on how reactive oxygen and nitrogen species contribute to the neurotoxic properties of these four molecules. As the reader will discover, to achieve the above stated goal, we had to not only appraise recent findings, but also revisit earlier landmark studies to provide a comprehensive view on this topic. This approach also enabled us to describe how our understanding of the mechanism of actions of certain toxins has evolved over time, which is particularly striking in the case of the quatrogenarian neurotoxin, 6-hydroxydopamine.

Animals↗

Studies of skin toxicity in vitro: dose-response studies on JB6 cells.

There are many reasons for developing in vitro tests of toxicity including cost, speed, studies of mechanisms, and studies utilizing human cells and tissues. The present study focuses on the development of in vitro tests to predict in vivo toxicity by comparing them to data from the literature. A broad spectrum of model toxic compounds was evaluated for toxicity on mouse skin JB6 cells in culture. These included mercuric chloride, sodium lauryl sulfate, formaldehyde, dimethyl sulfoxide, benzoyl peroxide, and ionomycin, all of which have been proven to be positive in the Draize test or in cutaneous toxicity studies. Cell viability was evaluated every 15 min for up to 1 hr, and then after 24 hr of treatment using the Trypan Blue exclusion method; morphological changes were evaluated using phase-contrast and transmission electron microscopy. Dose- and time-dependent cell death and morphological changes were observed at concentrations ranging from 10(-14) to 10(-2) M. Arbitrary rankings were assigned based on 1) IC50 value estimated from the present data, and 2) in vivo toxicity reported in the Registry of Toxic Effects of Chemical Substances. Good correlation between in vitro and in vivo toxicity based on arbitrary rankings was observed. Thus, these findings suggest that the JB6 cell culture model can be used for predicting in vivo toxicity. In the future, it may be possible to utilize this system for the study of intracellular ionized calcium ([Ca2+]i), and the expression of oncogenes as early indicators of toxicity.

Animals↗

Evaluation of Xenopus tropicalis as an alternative test organism for frog embryo teratogenesis assay--Xenopus (FETAX).

As a formal recommendation from an Interagency Coordinating Committee for the Validation of Alternative Methods (ICCVAM) workshop review of the Frog Embryo Teratogenesis Assay--Xenopus (FETAX) developmental toxicity model, the use of Xenopus tropicalis as an alternative test species for this model was evaluated. Three test substances with varying developmental toxicity potentials were evaluated using FETAX modified to accommodate the use of X. tropicalis. Two separate definitive concentration-response tests were performed with isoniazid, methotrexate, and 6-aminonicotinamide. Historical FETAX results with X. laevis were compared to the results from FETAX assays with X. tropicalis. Test with X. tropicalis indicated that each of the compounds possessed teratogenic potential with varying degrees of potency: 6-aminonicotinamide > methotrexate > isoniazid. Based on overt teratogenicity, but not embryo-lethality, results from these studies indicated that these two species responded similarly to the test compounds. Malformation syndromes induced in both species were similar in X. tropicalis and X. laevis. These results suggested that X. tropicalis should be further evaluated as an alternative test organism for the FETAX model.

6-Aminonicotinamide↗

Characterization of the human hepatocellular carcinoma (hepg2) cell line as an in vitro model for cadmium toxicity studies.

Biochemical indicators and in vitro models, if they mimic in vivo responses, offer potentially sensitive tools for inclusion in toxicity assessment programs. The purpose of this study was to determine whether the HepG2 cell line would mimic known in vivo or in vitro (or both) responses of mammalian systems when confronted with cadmium (Cd2+). Uptake and compartmentalization of Cd2+, metallothionein (MT) compartmentalization, and glutathione (GSH) depletion were examined. In addition, several cytotoxic and stress effects, e.g., viability (neutral red [NR] uptake, 3-[4,5-dimethylthiozole-2-yl]-2,5,-biphenyl tetrazolium bromide [MTT] dye conversion, and live/dead [L/D]), membrane damage (lactate dehydrogenase leakage), metabolic activity (adenosine triphosphate levels), and detoxification capabilities (GSH content, cytochrome P4501A1/2 [EROD (ethoxyresorufin-o-deethylase)] activity, and MT induction), were measured in both naive (no previous exposure) and Cd2+ preexposed cells. Cadmium uptake increased during a 24-h period. Metallothionein induction occurred in response to both Cd2+ and ZnCl2; however, Cd2+ was the more potent inducer. Both Cd2+ and MT were localized primarily in the cytoplasmic compartment. All biochemical responses, except EROD, showed concentration- response relationships, after 24-h exposure to Cd2+ (ranges 0-3 ppm [26.7 microM]). Cadmium effects were reduced in preexposed cells, indicating adaptive tolerance or increased resistance had occurred. Twenty-four-hour LC50, dose causing death of 50% of the test subjects, values were 0.97, 0.69, and 0.80 ppm (8.7, 6.2, and 7.2 microM) for naive cells and 1.45, 1.21, and 1.39 ppm (12.9, 10.7, and 12.3 microM) for preexposed cells based on the NR, MTT, and L/D assays, respectively. These data indicate that this carcinoma cell line is a useful in vitro model for cadmium toxicity studies.

Biomarkers↗