Multicentre Evaluation Of In Vitro Cytotoxicity Research Articles

MEIC Evaluation of Acute Systemic Toxicity

The Multicenter Evaluation of In Vitro Cytotoxicity (MEIC) programme was set up to evaluate the relevance for acute human systemic toxicity of in vitro cytotoxicity tests. At the end of the programme in the summer of 1996, 29 laboratories had tested all 50 reference chemicals in 61 cytotoxicity assays. As a necessary prerequisite to the forthcoming evaluation papers of this series, this paper presents the animal and human toxicity data of the programme. This database contains tabulated handbook data for the 50 chemicals, on: a) oral rat and mouse LD50 values; b) acute oral lethal doses in humans; c) clinically measured acute lethal serum concentrations in humans; d) acute lethal blood concentrations in humans measured postmortem; e) peaks from curves of an approximate 50% lethal blood/serum concentration over time after ingestion (LC50 curves), derived from a compilation of human acute poisoning case reports; f) human kinetics of single doses, including absorption, peak time, distribution/elimination curve, plasma half-life, distribution volume, distribution to organs (notably brain), and blood protein binding; and g) qualitative human acute toxicity data, including lethal symptoms, main causes of death, average time to death, target organs, presence of histopathological injury in target organs, presence of toxic metabolites, and known or hypothetical mechanisms for the lethal toxicity. The rationales for selection of the human toxicity data are also noted. The methods used to compile the in vivo toxicity data are described, including a presentation of a new method of constructing LC50 curves. Finally, the merits and shortcomings of the various human toxicity data for evaluation purposes are discussed.

MEIC Evaluation of Acute Systemic Toxicity

The Multicenter Evaluation of In Vitro Cytotoxicity (MEIC) programme was set up to evaluate the relevance for human acute toxicity of in vitro cytotoxicity tests. At the end of the project in 1996, 29 laboratories had tested all 50 reference chemicals in 61 cytotoxicity assays. Five previous articles have presented the in vitro data and the human database to be used in the evaluation. This article presents three important parts of the final evaluation: a) a comparison of rat and mouse oral LD50 with human acute lethal doses for all 50 chemicals; b) a display of the correlations between IC50 (concentration causing 50% inhibition) values from all 61 assays and three independent sets of human acute lethal blood concentrations, i.e. clinical lethal concentrations, forensic lethal concentrations, and peak concentrations; and c) a series of comparisons between average IC50 values from ten human cell line 24-hour assays and human lethal blood concentrations. In the latter comparisons, results from correlations were linked with known human toxicity data for the chemicals, to provide an understanding of correlative results. This correlative/mechanistic approach had the double purpose of assessing the relevance of the in vitro cytotoxicities, and of testing a series of hypotheses connected with the basal cytotoxicity concept. The results of the studies were as follows. Rat LD50 predictions of human lethal dosage were only relatively good (R2= 0.61), while mouse LD50s gave a somewhat better prediction (R2= 0.65). Comparisons performed between IC50 values from the 61 assays and the human lethal peak concentrations demonstrated that human ceil line tests gave the best average results (R2= 0.64), while mammalian and fish cell tests correlated less well (R2= 0.52–0.58), followed by non-fish ecotoxicological tests (R2= 0.36). Most of the 61 assays underpredicted human toxicity for digoxin, malathion, carbon tetrachloride and atropine sulphate. In the correlative/mechanistic study, the 50 chemicals were first separated into three groups: A = fast-acting chemicals with a restricted passage across the blood–brain barrier; B = slow-acting chemicals with a restricted passage across the blood–brain barrier; and C = chemicals which cross the blood–brain barrier freely, while inducing a non-specific excitation/depression of the central nervous system (CNS). The IC50 values for chemicals in group C were divided by a factor of ten to compensate for a hypothetical extra vulnerability of the CNS to cytotoxicity. Finally, the average human cell line IC50 values (24-hour IC50 for groups A and C, and after 48-hour for group B) were compared with relevant human lethal blood concentrations (peak concentrations for groups A and C, and 48-hour concentrations for group B). As a result, in vitro toxicity and in vivo toxicity correlated very well for all groups (R2= 0.98, 0.82 and 0.85, respectively). No clear overprediction of human toxicity was made by the human cell tests. The human cell line tests underpredicted human toxicity for only four of the 50 chemicals. These outlier chemicals were digoxin, malathion, nicotine and atropine sulphate, all of which have a lethal action in man through interaction with specific target sites not usually found in cell lines. Potassium cyanide has a cellular human lethal action which cannot be measured by standard anaerobic cell lines. The good prediction of the human lethal whole-blood concentration of this chemical was not conclusive, i.e. was probably a “false good correlation”. Another two chemicals in group C resulted in “false good correlations”, i.e. paracetamol and paraquat. The comparisons thus indicated that human cell line cytotoxicities are relevant for the human acute lethal action for 43 of the 50 chemicals. The results strongly support the basal cytotoxicity concept, and further point to the non-specific CNS depression being the obligatory reaction of humans to cytotoxic concentrations of chemicals, provided that the chemicals are able to pass the blood–brain barrier.

MEIC Evaluation of Acute Systemic Toxicity

Results from tests on the Multicentre Evaluation of In Vitro Cytotoxicity (MEIC) reference chemicals 31–50 in 67 different in vitro toxicity assays are presented in this paper as a prerequisite to in vitro/in vivo comparisons for all MEIC in vitro toxicity data in forthcoming papers, i.e. the final MEIC evaluation of the relevance of the tests. With the aim of increasing knowledge about the relative significance of some in vitro methodological factors, the strategies and methods of the preceding parts in the MEIC series (Parts II and III) were again employed to enable comparative cytotoxicity analysis of the new in vitro results presented in this paper. A principal components analysis (PCA) of the results from tests of the 20 chemicals in 67 assays demonstrated a dominating first component describing as much as 74% of the variance in the toxicity data, indicating a similar ranking of the cytotoxicities of the chemicals in most of the tests. The influence on the general variability of the results of a few, key methodological factors was also evaluated by using linear regression comparisons of the results of all pairs of methods available in the study, i.e. methods which were similar in all respects except for the factor being analysed. Results from this “random probe” analysis were: a) the cytotoxicities of 11 of the 20 chemicals increased considerably with exposure time (> 10 times over 4–168 hours); b) in general, human cell line toxicity was well predicted by cytotoxicity in animal cells; c) prediction of human cell line toxicity by most ecotoxicological tests was only fairly good; d) 14 comparisons of similar assays with different cell lines showed similar toxicities (mean R2 = 0.83); e) nine comparisons of similar assays employing different primary cultures and cell lines shared similar toxicities (mean R2 = 0.71); and f) 16 comparisons of similar assays with different growth/viability endpoints showed similar toxicities (mean R2 = 0.71). Results b, d, e and f must contribute to the PCA-documented high general similarity of the in vitro toxicity data. Results a and c, together with factors which were not analysed, such as different protocols and inter-laboratory variability of tests, could explain the 26% dissimilarity. To provide background information to the planned final MEIC evaluation of the relevance of the 61 methods in which all 50 chemicals have been tested, an additional PCA was made of the 50 chemical-61 assay in vitro database (from Parts II and III and the present paper). This supplementary PCA demonstrated an 80% similarity of results. Compared with the previous analysis of the tests of the first 30 MEIC reference chemicals (MEIC Part III), the present analysis of the tests of the last 20 MEIC chemicals indicates a somewhat higher variation in the results. Correspondingly, some deviating endpoint measurements and cell line responses were demonstrated by the pairwise comparisons in the present study. As a result, the analysis revealed a high correlation (R2 = 0.73) between the average human cell line toxicity and the results from a new protein denaturation test. These preliminary results suggest that intracellular protein denaturation may be a frequently occurring mechanism in basal cytotoxicity.

Evaluation of the Cytotoxic Effects of MEIC Chemicals 31–50 on Primary Culture of Rat Hepatocytes and Hepatic and Non-hepatic Cell Lines

The cytotoxicities of 20 chemicals (numbers 31–50) from the Multicenter Evaluation of In Vitro Cytotoxicity (MEIC) programme were assessed with a primary culture of rat hepatocytes and with two hepatic cell lines (Hep G2 and FaO) and one non-hepatic cell line (3T3). The cytotoxicities of the chemicals were evaluated by using the MTT test after the cells had been exposed to the chemicals for 24 hours. For a better evaluation of results, dose–response curves were mathematically linearised and cytotoxicity was expressed as IC50 values and IC10 values (the concentration causing 50% and 10% loss of cell viability, respectively). We found that all the compounds showed similar acute basal cytotoxicity in all four cellular systems (regardless of whether the cells were, or were not, metabolically competent or were or were not of human origin). When these results were used to predicit human toxicity in terms of a mathematical parameter (prediction error [PE]), we found that all four systems gave similar predictions of human toxicity. The best cytotoxicity parameter included in the PE calculation was the IC50/10, because of an underestimation of human toxicity by in vitro systems. However, when PEs were calculated for rodent toxicity, better results were obtained. Data from the literature obtained by using other experimental models for predicting human toxicity were analysed according to the same criteria. We conclude that cellular systems are better predictive tools for human toxicity than are prokaryotic cells or whole-organism models.

Cytotoxicity of MEIC Chemicals to Rainbow Trout R1 Cell Line and Multivariate Comparison with Ecotoxicity Tests

The cytotoxic effects of the first ten chemicals from the Multicenter Evaluation of In Vitro Cytotoxicity (MEIC) programme on the fibroblast-like R1 cell line, derived from rainbow trout (Oncorhynchus mykiss), were measured by using three endpoints: cell attachment (24-hour exposure, crystal violet protein stain); cell viability (24-hour exposure, neutral red uptake cytotoxicity assay); and cell growth (144-hour exposure, crystal violet protein stain). The results were compared with published MEIC toxicity data from fish and mammalian cells, and from ecotoxicity tests with bacteria, invertebrates and plants by using multivariate statistical techniques. For eight of the ten compounds under consideration, a high degree of correlation in toxicity ranking between the various bioassays was observed, irrespective of the test systems or endpoints utilised. This similarity might be explained by the basal cytotoxicity concept. The 20% dissimilarity of the results, however, indicates the influence of test system-specific or end-point-specific sensitivities.

Toxicity of 20 Chemicals from the MEIC Programme Determined by Growth Inhibition of L-929 Fibroblast-like Cells

The Multicentre Evaluation of In vitro Cytotoxicity (MEIC) programme is an international project aimed at evaluating the relevance of in vitro tests in predicting human toxicity. We have screened 20 chemicals (MEIC codes 31-50) from the programme, by using a cytotoxicity test based on growth inhibition of the mouse fibroblast-like L-929 cell line. Inhibition of cell growth was determined by the neutral red uptake method, which is well established and is used for screening the cytotoxicity of chemicals and plastics for pharmaceuticals and medical devices. The concentrations causing 50% inhibition of cell growth after a 72-hour exposure period varied from 3.1μM for hexachlorophene, to 1.4mM for caffeine. This is within the same range as results recently obtained with five other cell models. However, with some chemicals (chloroform, carbon tetrachloride and dichloromethane), no reliable results were obtained. These substances could not be dissolved in a reproducible way in any of the solvents used and, furthermore, they were highly volatile, which led to difficulties in maintaining the concentrations.

ヒト由来細胞培養系を用いた水環境試料中の有機塩素化合物の毒性評価

As part of validation processes of in vitro toxicity assays for the risk assessment of environmental hazards, we applied an in vitro toxicity test using two human cell lines, neuroblastoma NB-1 cells and glioblastoma U-87 MG cells, to the assessment of organochlorine compounds detected in the water environment. The in vitro toxicity assay using NB-1 cells was calibrated by testing reference chemicals proposed by MEIC (Multicenter Evaluation of In Vitro Cytotoxicity), an international program for the validation of in vitro cytotoxicity assays.Beforehand, an assay using cells in frozen stock without subcultivation was examined by comparing IC50 values with the ordinary assay using subcultured cells. IC50 values for MEIC reference chemicals from the former assay showed good correlation with those from the latter assay, suggesting that the assay using cells in frozen stock can he used at least for the assessment of basal cytotoxicity.IC50 values for ten organochlorine compounds frequently detected in the sediment samples from contaminated rivers, p-chloroaniline, 3,4-dichloroaniline, p-dichlorohenzene, o-dichlorobenzene, Tris (2-chloroethyl)-phosphate, 2,5-dichlorophenol, 2,5-dichloroanisol, Triclosan and Triclocarban, were obtained with the in vitro assays and compared with their LD50 values in rats. No significant correlation, however, was seen between the IC50 and LD50 values, indicating that further improvement of in vitro toxicity assays is necessary for the application to the risk assessment of environmental hazards.

Cytotoxic and non-cytotoxic effects of the MEIC reference chemicals on spontaneously contracting primary cultured rat skeletal muscle cells

This study was designed to evaluate the suitability of a multi-endpoint test system using primary cultured spontaneously contracting rat skeletal muscle cells to indicate an acute neuro- and/or cardiotoxic potential of chemicals. The concentration-dependent effects of the 50 MEIC (Multicenter Evaluation of In Vitro Cytotoxicity) reference chemicals on contractility, indicative of the functional integrity of the electrically active muscle cell membrane, were determined. Additionally, effects on two other endpoints, glucose consumption and viability, were monitored to reveal whether alterations in contractility were associated with cytotoxicity. In total, 30 of the tested compounds inhibited contractility at non-cytotoxic concentrations. The contractility-inhibiting and cytotoxic potencies differed by factors of more than 10 in the case of diazepam, phenol, propranolol, phenobarbital, mercuric chloride, thioridazine, verapamil, chloroquine, quinidine, phenytoin and atropine, of more than 100 in the case of amitriptyline, dextropropoxyphene, orphenadrine and amphetamine, and even more than 1000 for nicotine. On the basis of the available knowledge of the acute toxic effects and modes of acute toxic action of the test compounds, this characteristic response pattern is shown to be highly predictive for compounds reported to be cardio- and/or neurotoxic owing to interference with excitable membrane functions and/or neurotransmission.

MEIC Evaluation of Acute Systemic Toxicity

The multicentre evaluation of in vitro cytotoxicity (MEIC) study is a programme designed to evaluate the relevance of in vitro toxicity tests for predicting human toxicity, and is organised by the Scandinavian Society for Cell Toxicology. The project started in 1989 and is scheduled to be finished by June 1996. MEIC is a voluntary effort by international laboratories to test the same 50 reference chemicals in their own in vitro toxicity systems. At present, 31 laboratories have submitted results for the first 30 reference chemicals from a total of 68 in vitro cytotoxicity tests. In the definitive evaluation of the MEIC programme, these in vitro results will be compared with human lethal blood concentrations and other relevant acute systemic toxicity data, and the results will be published as a series of articles. This paper, which is the first article in this series, describes and analyses the methodologies used in the 68 tests. The origins and purities of the test chemicals, the biological systems and the toxicity endpoints are also discussed. Since MEIC is not centrally directed, the selection of tests was entirely dependent on the preferences of the individual laboratories. Thus, the collection of tests is not representative of the full range of existing in vitro toxicity tests. In our study, basal cytotoxicity tests and ecotoxicological tests are prevalent, while tests for toxicity to primary cultures of differentiated cells, measured by organotypic toxicity endpoints, are clearly under-represented.

Dynamic Qualities of Validation and the Evolution of New In Vitro Toxicological Tests

This review summarises some aspects of the dynamics of the evolution of toxicological test methods based on cell biology. Within the multicentre evaluation of in vitro cytotoxicity (MEIC) programme, some general principles for validation have been proposed: a) a human database should be used as the source of reference data in the validation of new methods aimed at predicting human toxicity; b) the relevance of a test should be determined before its reliability is assessed; c) a parallel validation of methods is preferable to a serial validation; and d) toxicokinetic data should be included in the validation process to improve the predictivity of cytotoxicity test results. These toxicokinetic data can be used to extrapolate the cytotoxic in vitro concentrations to provide human toxic exposure levels. As part of test development, the cytotoxic concentration can also be compared directly with the critical toxic human blood or tissue concentration. This approach is being explored in the ERGATT/CFN integrated toxicity testing scheme (ECITTS) prevalidation project. The critical toxic concentrations are determined by using a set of neurospecific cellular tests, chosen and combined on the basis of knowledge of common neurotoxicity mechanisms. Another approach to selecting tests for prevalidation is through the development of tests that are found to be necessary and complementary to existing tests. Such a programme has been initiated on the basis of the results of the MEIC study. The progress made so far in this “missing tests programme” is presented in this paper.

A combination of fluorescent probes for evaluation of cytotoxicity and toxic mechanisms in isolated rainbow trout hepatocytes

The toxicity of 17 chemicals to freshly isolated rainbow trout hepatocytes was determined using four different fluorescent probes measuring different endpoints. Calcein was used to determine viability of the cells, rhodamine 123 and 5,5′,6,6′-tetrachloro-1,1′,3,3'-tetraethylbenzimidazolylcarbocyanine iodide (JC-1) to monitor mitochondrial activity and 5-chloromethylfluorescein diacetate (CMFDA) to monitor intracellular glutathione (GSH) levels. An EC 50 value 10 times lower than that obtained with the calcein assay was taken to indicate a specific action. Two sets of test chemicals were used. The first set contained five chemicals with a known specific toxic action and two chemicals without a known main specific action at a cellular level, and this set was used to examine the specificity of the probes. The second set consisted of 10 chemicals from the MEIC (Multicenter Evaluation of In Vitro Cytotoxicity) chemical list and included only one chemical with a known main specific action at a cellular level. In the first set of chemicals the CMFDA assay detected all chemicals with known GSH-depleting action, and the results obtained with the second set of chemicals indicated that none of the chemicals act mainly by GSH depletion. However, the CMFDA assay showed one false positive (antimycin-A). The results obtained with the rhodamine 123 and the JC-1 assay were less clear. The rhodamine 123 assay recognized the three chemicals in set 1 interfering with mitochondrial function but gave one false positive (ethanol) in this set, whereas the JC-1 assay recognized only two of the chemicals and gave one false positive (menadione). Both assays failed to detect the only chemical in set 2 with a known action on mitochondria (KCN). We conclude that calcein and CMFDA are good candidates as fluorometric probes for detection of cell viability and depletion of GSH, respectively. However, rhodamine 123 and JC-1, on the other hand, do not appear to be good probes for screening of mitochondrial activity in rainbow trout hepatocytes.

有害物質・障害生物の水環境への影響と制御 ほ乳動物培養細胞系を用いた水環境試料の毒性評価

To evaluate the toxicity other than mutagenicity or carcinogenicity present in the water environment, in vitro cytotoxicity tests using cultured mammalian cells were utilized. Cytotoxicity was estimated based on the changes in viable cell numbers of primary rat cerebellar cells, rat pheochromocytoma cell PC12h, and normal rat kidney epithelial cell NRK-52E. Evaluation of these in vitro systems was performed by testing reference chemicals proposed by MEIC (Multicenter Evaluation of In Vitro Cytotoxicity), an international program for the validation of in vitro cytotoxicity tests.When cells in culture were exposed to landfill leachate for 48 hours, viable cell numbers decreased dose dependently. However, fractions prepared by condensation and extraction from the leachates showed much less effects on the viable cell numbers. Their individual cytotoxicity did not account for that of unfractionated leachate, suggesting that component(s) with higher cytotoxicity may not be successfully recovered during the condensation and extraction process.Among the silica-gel column fractions of acetone-extracts of sediment samples, fractions eluted with acetone showed the highest cytotoxicity.These results indicate that the cytotoxicity of water samples like landfill leachates or of their extracts can be detected with the present assay system but toxic components may not be recovered quantitatively during the condensation and extraction process.

Evaluation of the cytotoxicity of 10 chemicals in human and rat hepatocytes and in cell lines: Correlation between in vitro data and human lethal concentration

The cytotoxicity of 10 chemicals from the Multicentre Evaluation of In vitro Cytotoxicity (MEIC) list (nos 21–30) was evaluated in human and rat cultured hepatocytes and in two established cell lines (HepG2 and 3T3) according to the MEIC programme organized by the Scandinavian Society of Cell Toxicology. The MTT test was used as the endpoint of cytotoxicity after 24hr of exposure to the chemicals. Theophylline, phenobarbital and paraquat were the least cytotoxic compounds in the cellular systems (IC 50 = 450-17,000 μm) except for the 3T3 cells. The seven remaining chemicals (dextropropoxyphene, propranolol, arsenic trioxide, cupric sulfate, mercuric chloride, thioridazine and thallium sulfate) showed a similar relative cytotoxic ranking in the four in vitro systems in the lower range of concentrations (IC 50 = 2–350 μm). The data suggest that these 10 chemicals have a basal cytotoxic effect common to the four in vitro systems, and probably none of these compounds could be considered either hepatotoxic or species specific. The correlation between in vitro data and human lethal blood concentrations showed that the predictability of the in vitro systems was similar to that of in vivo rodent tests (LD 50) only when low cytotoxic concentrations (IC 10) were used for correlation.

Short Communication: A comparison of the toxicity of 30 reference chemicals to Daphnia Magna and Daphnia Pulex

AbstractTo determine whether significant differences exist in the sensitivity of different Daphnia species to toxicants, the acute toxicity of the first 30 MEIC (multicenter evaluation of in vitro cytotoxicity) reference chemicals was determined in two species of Daphnia: D. magna and D. pulex. Correlation and regression analysis of the EC50 data for immobilization showed a very good concordance (r = 0.97, slope = 1.02). A comparison between the EC50 data obtained for D. magna by two laboratories independently for the 50 MEIC chemicals also showed a good concordance (r = 0.93, slope = 0.91). In both comparisons the regression line did not differ significantly from the regression line for a 1:1 regression. We conclude that our study, including a set of reference chemicals, indicates there is no difference in the overall sensitivity of the two Daphnia species and the two clones of D. magna.

A COMPARISON OF THE TOXICITY OF 30 REFERENCE CHEMICALS TO DAPHNIA MAGNA AND DAPHNIA PULEX

To determine whether significant differences exist in the sensitivity of different Daphnia species to toxicants, the acute toxicity of the first 30 MEIC (multicenter evaluation of in vitro cytotoxicity) reference chemicals was determined in two species of Daphnia: D. magna and D. pulex. Correlation and regression analysis of the EC50 data for immobilization showed a very good concordance (r = 0.97, slope = 1.02). A comparison between the EC50 data obtained for D. magna by two laboratories independently for the 50 MEIC chemicals also showed a good concordance (r = 0.93, slope = 0.91). In both comparisons the regression line did not differ significantly from the regression line for a 1:1 regression. The authors conclude that their study, including a set of reference chemicals, indicates that is no difference in the overall sensitivity of the two Daphnia species and the two clones of D. magna.

Modelling of human acute toxicity from physicochemical properties and non-vertebrate acute toxicity of the 38 organic chemicals of the MEIC priority list by PLS regression and neural network

Linear and non-linear modelling of human acute toxicity (as human lethal concentrations; HLCs) of the 38 organic chemicals from the 50 priority compounds of the Multicentre Evaluation of In Vitro Cytotoxicity (MEIC) programme was investigated. The models obtained were derived either from a set of 23 physicochemical properties of the compounds or from their acute toxicities to five aquatic non-vertebrates together with the physicochemical properties. For the linear type, modelling was performed using a partial least square projection to latent structures (PLS) regression method; for the non-linear models, both PLS regression and neural network were utilized. A neural network using a combination of backpropagation and cascade-correlation algorithms was applied in this study. The results generally reveal a slightly better predictive performance of the models obtained from PLS regression than those obtained from neural networks. However, the model composed of physicochemical properties (PC-model) from the trained neural network using a back propagation algorithm with pruning technique proved superior to that trained with a combination of back propagation and cascade-correlation algorithms after leave-one-out cross-validation. The predictive power of the PC-models, whether linear or non-linear, was comparable with that of the corresponding models consisting of both structural descriptors and the ecotoxicological tests (ECOPC-models), except for the battery (ECOPC-model) from the neural network. The composition of the ‘best’ PLS and neural network models points to the importance of the combination of physicochemical properties reflecting lipophilicity, size, volume, intermolecular binding forces and electronic properties of the molecule. All the aquatic non-vertebrate tests are shown to be essential in explaining human acute toxicity. However, the degree of contribution differed, with the crustacean ( Artemia salina) and the bacterial (Microtox) bioassays being more important to the linear and non-linear PLS models, whereas the crustacean ( Artemia salina and Streptocephalus proboscideus) tests, and the rotifer ( Brachionus calyciflorus) assay were important to the neural network models. The organochlorine (lindane) and bipyridinium (paraquat) pesticides were common outliers in all the models. Moreover, the latter two compounds and the organophosphate (malathion) pesticide were also common outliers in all ECOPC-models. Other types of pesticides, however, fit the models. The predicted HLCs of a number of non-pesticides, including some chlorinated compounds, also deviated from the observed HLCs by more than one order of magnitude.

QSAR models for predicting the acute toxicity of selected organic chemicals with diverse structures to aquatic non-vertebrates and humans.

The linear and non-linear relationships of acute toxicity (as determined on five aquatic non-vertebrates and humans) to molecular structure have been investigated on 38 structurally-diverse chemicals. The compounds selected are the organic chemicals from the 50 priority chemicals prescribed by the Multicentre Evaluation of In Vitro Cytotoxicity (MEIC) programme. The models used for the evaluations are the best combination of physico-chemical properties that could be obtained so far for each organism, using the partial least squares projection to latent structures (PLS) regression method and backpropagated neural networks (BPN). Non-linear models, whether derived from PLS regression or backpropagated neural networks, appear to be better than linear models for describing the relationship between acute toxicity and molecular structure. BPN models, in turn, outperform non-linear models obtained from PLS regression. The predictive power of BPN models for the crustacean test species are better than the model for humans (based on human lethal concentration). The physico-chemical properties found to be important to predict both human acute toxicity and the toxicity to aquatic non-vertebrates are the n-octanol water partition coefficient (Pow) and heat of formation (HF). Aside from the two former properties, the contribution of parameters that reflect size and electronic properties of the molecule to the model is also high, but the type of physico-chemical properties differs from one model to another. In all of the best BPN models, some of the principal component analysis (PCA) scores of the 13C-NMR spectrum, with electron withdrawing/accepting capacity (LUMO, HOMO and IP) are molecular size/volume (VDW or MS1) parameters are relevant. The chemical deviating from the QSAR models include non-pesticides as well as some of the pesticides tested. The latter type of chemical fits in a number of the QSAR models. Outliers for one species may be different from those of other test organisms.

The cytotoxicity of 50 chemicals from the MEIC study determined by growth inhibition of Ascites Sarcoma BP8 cells: a comparison with acute toxicity data in man and rodents

In this study, 50 chemicals selected on the basis of existence of particularly reliable human toxicity data were screened in a cytotoxicity test involving inhibition of the growth of Ascites Sarcoma BP8 cells. These test results are part of an international validation program, the Multicenter Evaluation of In Vitro Cytotoxicity (MEIC), the aim of which is to recommend batteries of in vitro tests to be used for prediction of human toxicity. The cytotoxicities (expressed as the concentrations causing 50% inhibition of cell growth) were compared to acute toxicity data in humans (LDL 0) and rodents (LD 50), showing the best correlation to rodent data. The results are discussed in relationship to what is usually referred to as basal cytotoxic mechanisms as a cause of in vivo toxicity. It could be concluded that the predicted results on the basis of mechanistic reasoning were not always obtained.

Human acute toxicity prediction of the first 50 MEIC chemicals by a battery of ecotoxicological tests and physicochemical properties

Five acute bioassays consisting of three cyst-based tests (with Artemia salina, Streptocephalus proboscideus and Brachionus calyciflorus), the Daphnia magna test and the bacterial luminescence inhibition test ( Photobacterium phosphoreum) are used to determine the acute toxicity of the 50 priority chemicals of the Multicentre Evaluation of In Vitro Cytotoxicity (MEIC) programme. These tests and five physicochemical properties ( n-octanol-water partition coefficient, molecular weight, melting point, boiling point and density) are evaluated either singly or in combination to predict human acute toxicity. Acute toxicity in humans is expressed both as oral lethal doses (HLD) and as lethal concentrations (HLC) derived from clinical cases. A comparison has also been made between the individual tests and the conventional rodent tests, as well as between rodent tests and the batteries resulting from partial least squares (PLS), with regard to their predictive power for acute toxicity in humans. Results from univariate regression show that the predictive potential of bioassays (both ecotoxicological and rodent tests) is generally superior to that of individual physicochemical properties for HLD. For HLC prediction, however, no consistent trend could be discerned that indicated whether bioassays are better estimators than physicochemical parameters. Generally, the batteries resulting from PLS regression seem to be more predictive than rodent tests or any of the individual tests. Prediction of HLD appears to be dependent on the phylogeny of the test species: cructaceans, for example, appear to be more important components in the test battery than rotifers and bacteria. For HLC prediction, one anostracan and one cladoceran crustacean are considered to be important. When considering both ecotoxicological tests and physicochemical properties, the battery based on the molecular weight and the cladoceran crustacean predicts HLC substantially better than any other combination.

Comparative acute toxicity of the first 50 Multicentre Evaluation of In Vitro Cytotoxicity chemicals to aquatic non-vertebrates

The acute toxicity data of the first 50 chemicals of the Multicentre Evaluation of In Vitro Cytotoxicity (MEIC) programme is compared for three “cyst-based toxicity tests” (Artoxkit M with Artemia salina, Streptoxkit F with Streptocephalus proboscideus, and Rotoxkit F with Brachionus calyciflorus), and two other tests (the Daphnia magna and the Photobacterium phosphoreum Microtox™ tests) commonly used in ecotoxicology. The difference in sensitivity for the 50 chemicals was as high as 19 orders of magnitude (on a molecular weight basis) between the most and least sensitive species. Generally, a similar toxicity ranking of the 5 test species was found for most of the chemicals and the interspecies correlations were high. Results from Principal Component Analysis (PCA) and cluster analysis indicated that the groupings are not related to a clear and defined chemical structure. However, the loading plot of the first two principal components may aid in selecting the minimum number and type of tests that have to be included in a battery which encompasses a broad spectrum of toxicity levels. Consequently, this study supports the use of a selected battery of tests to evaluate ecotoxicity and suggests its possible importance for screening of biologically-active compounds from natural sources.