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A new in vitro toxicity test based on the response to toxic substances in solutions of mitochondria from beef heart.

A simple, rapid and inexpensive in vitro method which may be used as a biological sensor for the valuation of toxicity of chemical compounds in water is proposed. The method utilizes the response of the respiratory chain of beef heart mitochondria to a wide range of toxic substances. By means of simple voltametric measurements, the method not only gives an indication of toxicity in water but, by using different substrates of the respiratory chain and exploiting some features of the toxic substances, it also allows selective detection of some toxic substance or groups of substances. Since the method reproduces the standard "rainbow trout" test, it may also be proposed as a screening test to precede whole bioorganisms bioassays or as a method to assess the presence of certain toxic substances in water.

Adenosine Triphosphate↗

A theoretical model for simulating the outcome of mechanism based in vitro toxicity testing strategies.

In order to investigate the fundamental principles that influence the optimal selection of toxicity test methods for the evaluation of chemical hazards, it is useful to have a design model to explore possible alternative testing strategies. In general, our lack of detailed knowledge of the mechanisms of toxicity (including not only the early events in the interaction of chemicals with biological systems, but the sequence of events that lead to experimentally measurable toxicity) limits the development of realistic dynamic models of the toxicological process for individual chemicals. We report here the development of a theoretical model that includes two independent hypothetical mechanisms of toxicity. The mechanisms are designed to be qualitatively similar to known mechanisms of action. The model is exercised to simulate the experimental data that would be obtained for a collection of "test" and "validation" chemicals using a single or a combination of two toxicity tests. The data generated are used to evaluate the "relevance" of the testing strategy based on the two proposed in vitro toxicity tests.

Aging↗

Mouse breeds and the toxicity test for pertussis vaccine.

Mice from 14 suppliers (breeders) responded significantly different in the mouse-weight-gain test for toxicity of pertussis vaccine. Seven-day weight gain varied by 2.4 fold (2.5 to 6.1 g) and did not correlate with normal gain. Weight gain expressed as percentage-weight gain of the control varied by two-fold (52 to 104%). The percentage-weight gain requirement of greater than 60% (The Netherlands) was more discriminatory between mouse breeds than was the requirement of greate than or equal to 3.0 g gain (U.S.A.). Percentage-weight gains greater than 60%, however, showed significant distinctions. Specifications for the mice for this test are needed. Suggestions for the selection of the mouse are given.

Animals↗

Toxicity testing, risk assessment, and options for dredged material management.

Programs for evaluating proposed discharges of dredged material into waters of the United States specify a tiered testing and evaluation protocol that includes performance of acute and chronic bioassays to assess toxicity of the dredged sediments. Although these evaluations reflect the toxicological risks associated with disposal activities to some degree, analysis activities are limited to the sediments of each dredging project separately. Cumulative risks to water column and benthic organisms at and near the designated disposal site are therefore difficult to assess. An alternate approach is to focus attention on the disposal site, with the goal of understanding more directly the risks of multiple disposal events to receiving ecosystems. Here we review current US toxicity testing and evaluation protocols, and describe an application of ecological risk assessment that allows consideration of the temporal and spatial components of risk to receiving aquatic ecosystems. When expanded to include other disposal options, this approach can provide the basis for holistic management of dredged material disposal.

Animals↗

Effects of waste incineration combustion emissions measured by some toxicity test systems.

The toxicity of combustion emissions from a municipal incineration plant was tested in a series of rapid test methods. The series included tests concerning cellular energy metabolism, cellular detoxification and mutagenicity. In the most sensitive test systems, brown adipocytes and mitochondria, an effect was observed at an emission extract concentration corresponding to 0.02 m3 of exhaust. The results indicate an influence on the mitochondrial level as well as the premitochondrial level. In Ames' test concentrations corresponding to up to 0.3 m3 exhaust did not increase the number of revertants, although the chemical analysis of the emission indicates that the combustion emission contains mutagenic substances.

Adipose Tissue, Brown↗

Disturbances to metal partitioning during toxicity testing of iron(II)-rich estuarine pore waters and whole sediments.

Metal partitioning is altered when suboxic estuarine sediments containing Fe(II)-rich pore waters are disturbed during collection, preparation, and toxicity testing. Experiments with model Fe(II)-rich pore waters demonstrated the rates at which adsorptive losses of Cd, Cu, Ni, Mn, Pb, and Zn occur upon exposure to air. Experiments with Zn-contaminated estuarine sediments demonstrated large and often unpredictable changes to metal partitioning during sediment storage, removal of organisms, and homogenization before testing. Small modifications to conditions, such as aeration of overlying waters, caused large changes to the metal partitioning. Disturbances caused by sediment collection required many weeks for reestablishment of equilibrium. Bioturbation by benthic organisms led to oxidation of pore-water Fe(II) and lower Zn fluxes because of the formation of Fe hydroxide precipitates that adsorb pore-water Zn. For five weeks after the addition of organisms to sediments, Zn fluxes increased slowly as the organisms established themselves in the sediments, indicating that the establishment of equilibrium was not rapid. The results are discussed in terms of the dynamic nature of suboxic, Fe(II)-rich estuarine sediments, how organisms perturb their environment, and the importance of understanding chemistry in toxicity testing with whole sediments or pore water. Recommendations are provided for the handling of sediments for toxicity testing.

Ferrous Compounds↗

Primary cultures of microglial cells for testing toxicity of anticancer drugs.

Toxicity of anticancer agents on normal neural cells during chemotherapy of primary or secondary brain tumors is a clinical problem of increasing relevance and concern. In this perspective, here we used primary cultures of rat cortical microglia as an in vitro paradigm of normal glia to investigate the neurotoxicity of anticancer agents. The effects of two compounds frequently used for treatment of brain tumors, methotrexate (MTX) and temozolomide (TMZ), were compared to those of a known microglial activator, bacterial lipopolysaccharide (LPS); cell viability and metabolism was assessed by the MTS assay. We found that LPS, in the low-intermediate range of concentrations, strongly activates microglia cells, but a highly significant decrease in viability was observed from 100 ng/ml onward. TMZ has no effect at concentrations of clinical interest, whereas MTX significantly increases cell metabolism at 30 microM, a phenomenon possibly reflecting MTX neurotoxicity observed in patients.

Animals↗

[Modification of the Photobacterium phosphoreum toxicity test method].

In order to reduce the variation of Photobacterium phosphoreum luminous intensity during testing, the Photobacterium phosphoreum toxicity test was modified by a correction factor, PIacetone, in this paper. The effects of magnetic stirring time, culture time, culture generation and culture temperature on the measured results were discussed. The modified method had good laboratory repeatability and the relative standard deviation (RSD) was between 2.1% and 13.1%. Reliable data could be obtained using the modified method. It would be beneficial to the development of the quantitative structure-activity relationships on multicomponent organic compounds.

Luminescent Measurements↗

Beryllium toxicity testing in the suspension culture of mouse fibroblasts.

Suspension culture of mouse fibroblast cell line L-A 115 was used to test beryllium toxicity in the presence of magnesium ions. Beryllium added to the MEM cultivation medium was bound in a complex with sulphosalicylic acid BeSSA complex, because the use of beryllium chloride turned out to yield ineffective beryllium phosphate that formed macroscopically detectable insoluble opacities. The BeSSA complex was used in the concentration range: 10(-3)--10(-9)M, magnesium was used in 3 concentrations: 10(-1)M, 5 x 10(-2)M and 10(-2)M. Growth curve analysis revealed pronounced beryllium toxicity at the concentration of 10(-3)M, magnesium-produced toxic changes were observed only at the concentration of 10(-1)M. No competition between the beryllium and magnesium ions was recorded. It is assumed that the possible beryllium-magnesium competition was significantly modified by the use of BeSSA complex-bound beryllium.

Animals↗

Critical aspects in reproductive and developmental toxicity testing of environmental chemicals.

The process of toxicity testing of environmental chemicals is ruled by a framework of guidelines (OECD, OPPTS, etc.). The present paper will describe the process from the biological tests for environmental chemicals up to potential labelling and will focus on some critical aspects in this cascade of events. It is also the aim of this paper to give an overview of the existing documents and draft documents relevant for this field and available in the internet. Based on the current situation, the following points are discussed as critical issues: life stage considerations and their implications on testing, usefulness of investigations in juvenile animals, requirements for ADME studies, design and endpoints in fertility studies, use and usefulness of developmental milestones, performance of special studies versus one-study-design, considerations on transplacental carcinogenicity and early aging, significance of maternal/parental toxicity, application of triggers to justify studies, inclusion of new endpoints into test guidelines, and test strategies applied. Based on this, the usefulness of risk considerations in the current EU classification system for toxicity to reproduction as well as potency considerations will be discussed and suggestions will be made to improve the basic requirements for chemical testing which have remained relatively unchanged over the past 20 years.

Animals↗

Development of a novel, bioluminescence-based, fungal bioassay for toxicity testing.

Naturally bioluminescent fungi, Armillaria mellea and Mycena citricolor, were used to develop a novel, bioluminescence-based bioassay for toxicity testing. Bioassays were carried out to assess the toxicity of 3,5-dichlorophenol (3,5-DCP), pentachlorophenol (PCP), copper and zinc. The results suggested that 60 min was a suitable exposure time for the bioassay. Light reduction was observed in response to 3,5-DCP, PCP and Cu for both A. mellea and M. citricolor, but to Zn only for A. mellea. Armillaria mellea was significantly less sensitive to 3,5-DCP and PCP than M. citricolor. The EC50 values for A. mellea and M. citricolor were similar to EC50 values for 3,5-DCP, PCP and Cu (but not Zn) of bioluminescence-based bacterial biosensors. They were also similar to EC50 values for Cu and Zn of a bioluminescence-based yeast biosensor. The results highlighted the importance of using both prokaryotic and eukaryotic biosensors. The novel bioassay provides a rapid and sensitive method to assess bioavailability of pollutants as well as a method to determine their toxicity to filamentous fungi. It also expands the range of organisms that can be used for bioluminescence-based toxicity testing by complementing existing biosensors.

Agaricales↗

Acute toxicity tests on 113 environmental chemicals.

Acute toxicity tests on 113 environmental chemicals were conducted by the order of the Japanese government agencies. the LD50s or LC50s for 23 household chemicals, 11 medical drugs, 10 drug additives, 20 food additives, 13 industrial chemicals, 14 environmental pollutants, 12 agricultural chemicals and 5 organic solvents are presented together with the major toxic signs and symptoms and macroscopic changes in tissues. These toxicity data will be useful as an information source for regulatory purposes and also for prediction of the potential for acute toxicity of a wide variety of new chemicals.

Animals↗

Metabolic perspectives on in vitro toxicity tests.

1. The toxic effects of chemicals arise either from the chemical itself or from metabolites. In either event, the concentration of the molecular species responsible for toxicity is under the control of metabolism. This metabolism is highly variable between animals and humans, and in human populations may exhibit substantial inter-individual differences. The range of human variability can be covered by resorting to a number of animal models. 2. For many purposes, it is desirable to have in vitro procedures to allow detailed examination of mechanisms, but for a long time it was commonly the case that results from in vitro systems were misleading. It was realised that this problem arose at least in part from the absence of appropriate metabolism in many in vitro systems, and to overcome this, it has become common to add metabolizing enzymes in the form of the so-called S9 fraction--the 9000 g supernatant containing both microsomal and cytosolic enzymes--of rat liver. These enzyme preparations contain both the cytochrome P-450 mono-oxygenases and the obligatory NADPH-generating system. This system is thereby optimized for the mono-oxygenase reactions which are frequently responsible for the metabolic activation of toxic chemicals. 3. It is extremely important to appreciate that such systems are highly artificial, being far removed from the situation operating in the intact cell and the whole body. The levels of reactive metabolites in the whole cell are determined by the balance between activating and inactivating enzyme systems. When the S9 fraction is used for metabolism, the detoxication enzymes are essentially inactive, so that a misleading emphasis is thrown upon metabolic activation. Although the inactivating enzymes, such as the glutathione S-transferases, the sulphotransferases and the glucuronosyltransferases, are present in the S9 fraction, their cofactors are diluted so far below the relevant Km values as to render them completely inoperative. This absence of metabolic inactivation in in vitro test systems very commonly underlies observed discrepancies between the results of bacterial mutagenicity tests and carcinogenicity studies in whole animals. 4. Present and future demands upon the toxicologist require the use of rapid in vitro tests for the screening of chemicals, the results of which have predictive value for in vivo adverse effects, e.g. general toxicity, carcinogenicity or mutagenicity. The key role of metabolic information in such procedures is illustrated in this report with reference to the series of methylated derivatives of the polycyclic aromatic hydrocarbon benz(a)anthracene.(ABSTRACT TRUNCATED AT 400 WORDS)

9,10-Dimethyl-1,2-benzanthracene↗

[Acute toxicity test of garlic extract].

The acute toxicity toxicity test of garlic extract was studied in Wistar rats and ddY mice. The LD50 values of garlic extract by P.O., I.P. and S.C. administration were estimated over 30 ml/kg respectively in male and female of both rodents. In 30 ml/kg of I.P. group, five of ten in male rats and one of ten in female rats were died within a day after administration, however no specific signs due to garlic extract were observed in survivals for 7 days.

Animals↗

Silica sand as an artificial control sediment in a 20 day Neanthes arenaceodentata toxicity test.

The use of artificial control sediments in toxicity tests offers several advantages over field-collected control sediments, especially for laboratory-cultured organisms such as Neanthes arenaceodentata. Ten side-by-side trials were conducted using a field-collected sediment from West Beach, Whidbey Island, Washington State, USA and an artificial sediment composed of a silica quartz sand commonly used for masonry applications. After a 20-d exposure to sediment and clean overlying seawater, a similar biological response (as measured by the final average individual dry weight of Neanthes) was observed. The average individual dry weight was 14.77 +/- 3.83 and 14.70 +/- 3.57 mg/worm for the artificial and field-collected negative controls, respectively.

Animals↗

Acute and subacute toxicity tests of madder root, natural colorant extracted from madder (Rubia tinctorum), in (C57BL/6 X C3H)F1 mice.

As part of the safety assessment of madder root (MR), a food colorant extracted from madder (Rubia tinctorum), toxicity tests were undertaken using (C57BL/6 x C3H)F1 mice of both sexes. An acute toxicity test was performed by 14-day administration of MR dissolved in distilled water by gavage at doses of 0, 500, 2000, 3500, and 5000 mg/kg body weight to groups of each sex. One male mouse dosed at 5000 mg/kg body weight was dead before the end of the study, indicating that the maximum tolerated dose of MR was between 3500 and 5000 mg/kg body weight. A subacute toxicity test of MR was performed using 62 mice of each sex, mixing their diets with MR at concentrations of 0, 0.3, 0.6, 1.25, 2.5, and 5% for 90 days. All mice tolerated these doses of MR well. The body weight gains of either sex were not affected by the treatment. None of the mice treated with MR showed clinical signs of toxicity. Histopathological examinations showed retention cysts of the kidneys and epidermal vaginal cysts in a few of the treated or control mice. No hyperplastic, preneoplastic, and neoplastic lesions and no pathological findings of toxicity were found. These results suggest that dietary exposure of MR at these doses has no acute or subacute toxic effects on mice.

Animals↗