Structure-toxicity relationships for selected naphthoquinones to Tetrahymena pyriformis.
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Publications and source records attributed to T W Schultz.
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Toxicity data for the 50% growth inhibitory concentration against Tetrahymena pyriformis (log (IGC50-1)) for 42 alkyl- and halogen-substituted nitro- and dinitrobenzenes were obtained experimentally. Log (IGC50-1) along with the hydrophobicity, the logarithm of the 1-octanol/water partition coefficient (log Kow), and the molecular orbital properties, the lowest unoccupied molecular orbital energy (Elumo) and maximum acceptor superdelocalizability (Amax), were used to develop quantitative structure-activity relationships (QSARs). All the nitroaromatic compounds tested had toxicity in excess of baseline, nonpolar narcosis. The nitrobenzenes were thought to elicit their toxic response through multiple (and mixed) mechanisms. No high-quality relationship was observed between toxicity and hydrophobicity, or Elumo, individually. However, a strong relationship ¿log (IGC50-1) = 16.4(Amax) - 4.64; n = 42, r2 = 0.847, s = 0.279, F = 229¿ was obtained. In an effort to improve predictability, two-parameter QSAR, or response surface, analyses were performed. These analyses resulted in the following QSARs: ¿log (IGC50-1) = 0.206(log Kow) - 16.0(Amax) - 5.04; n = 42, r2 = 0.897, s = 0.229, F = 180¿ and ¿log (IGC50-1) = 0.467(log Kow) - 1.60(Elumo) - 2.55; n = 42, r2 = 0.881, s = 0.246, F = 154¿.
The toxicity data of 256 chemicals tested in both the 96-h Pimephales promelas mortality assay and the 2-d Tetrahymena pyriformis growth inhibition assay were evaluated using quantitative structure-activity relationships (QSARs). Each chemical was a priori assigned a mode of action of either narcoses or soft electrophilicity. Narcoses were separated into nonpolar narcosis, polar narcosis, monoester narcosis, diester narcosis, amine narcosis, and weak acid respiratory uncoupling based on the presence or absence of specific toxicophores. Toxicity of each narcotic mechanism was initially regressed against the 1-octanol-water partition coefficient (log K(ow)). The slopes of these log K(ow) based QSARs were observed to ascertain whether a relationship exists between the value of the slope and the reactivity of the mechanism of action. With both the fish and ciliate data nonpolar narcosis was the least reactive mechanism. It was followed by the other reversible narcoses. The soft electrophile mode was separated into the specific molecular mechanisms of: SN2 reactors, Schiff-base formers, Michael-type addition, or proelectrophilicity (precursors to Michael-type addition chemicals). These mechanisms were represented structurally by the nitrobenzenes, aldehydes, polarized alpha-beta unsaturates (e.g., acrylates and methacrylates), and acetylenic alcohols, respectively. Electrophilic toxicity was not correlated with hydrophobicity. QSARs based on molecular orbital (MO) quantum chemical descriptors were used to improve the predictability of the electrophilic mechanisms. Relevant descriptors include average superdelocalizability (Svna) for the nucleophilic addition of the nitrobenzene; atom x and y acceptor superdelocalizability (Ax); and bond order (Bx y) for the Michael-type addition of the acrylates; and log K(ow) and atom x net charge (Qx) for the Schiff-base forming aldehydes. The pertinent descriptors for proelectrophiles were log K(ow) and Svna. Principal differences between the QSARs for the two biological endpoints were observed for the ester narcoses, proelectrophiles, and Schiff-base forming aldehydes.
The relative toxicity (log IGC50(-1)) of 49 selected aliphatic amines and aminoalkanols was evaluated in the static Tetrahymena pyriformis population growth impairment assay. Excess toxicity, indicated by potency greater than predicted for non-polar narcotic alkanols, was associated with both classes of test chemicals. Moreover, the aminoalkanols were found to be more toxic than the corresponding alkanamines. A high quality 1-octanol/water partition coefficient (log K(ow)) dependent quantitative structure-activity relationship (QSAR), logIGC50(-1) = 0.78 (log K(ow)) - 1.42; r2 = 0.934, was developed for alkanamines. This QSAR represented the amine narcosis mechanism of toxic action. No quality QSAR was developed for the aminoalkanols. However, several structure-toxicity features were observed for this class of chemicals. Two-amino-1-hydroxy derivatives being more toxic than the corresponding derivatives, where the amino and hydroxy moieties were separated by methylene groups. Hydrocarbon branching next to the amino moiety resulted in decreased toxicity. Aminoalkanol alters lipid metabolism in T. pyriformis.
Quantitative structure-activity relationships (QSARs) have been utilized to validate toxicity data to Vibrio fisheri (the acute Microtox test) at each of the 5-, 15- and 30-min endpoints. Statistically robust QSARs were found for chemicals acting by a non-polar narcosis mechanism of action (MOA). The baseline, non-polar narcosis QSARs were similar to those found in other aquatic organisms, thus indicating that for this MOA, the acute V. fisheri assay makes a suitable surrogate for higher test species. For the toxicity of phenols, previously modeled in other species with parameters describing membrane transport (i.e. hydrophobicity) and soft electrophilicity or ionization, no significant relationships were obtained. The use of acute V. fisheri toxicity data is not recommended for extrapolation to higher species for these compounds. Despite this recommendation, it was noted, however, that a 'minimal' phenolic toxicity was apparent that was analogous to polar narcosis in other species. This confirmed that a polar narcosis MOA does operate in the acute V. fisheri system analogous to other species. For all the compounds considered, there were highly significant correlations between the toxicities at each endpoint, indicating that data from different time endpoints were effectively interchangeable.
The growth kinetics of preexposed and naive Tetrahymena pyriformis grown in the presence of one hydrophilic and one hydrophobic nonpolar narcotic (acetone and 2-decanone, respectively) have been evaluated. The response of naive Tetrahymena exposed to nonpolar narcotics varied from a change in generation time upon exposure to hydrophilic chemical to a change in lag phase with similar generation time compared to control upon exposure to hydrophobic compounds. Tetrahymena grown in the presence of low concentrations of 2-decanone and then transferred to higher concentrations acclimated to the presence of the toxicant. Acclimation was demonstrated by reduced lag phases compared to naive cells. Results of population growth studies of Tetrahymena grown in the presence of low concentrations of acetone and then transferred to higher concentrations of acetone exhibit the same pattern, an increased generation time with increasing concentration with no lag time, as naive populations. Additionally, the observed generation times in acetone were cumulative relative to the transfer concentration as well as the acclimation concentration. The most feasible explanation for this phenomenon is the interaction of the toxicants with the plasma membrane.
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This study describes effects of selected nonpolar narcotics of varying hydrophobicity (quantified by the 1-octanol-water partition coefficient, log Kow) and molecular structure on the population growth kinetics of the freshwater ciliate Tetrahymena pyriformis. The response of Tetrahymena exposed to different nonpolar narcotics varied from a change in generation time to a change in lag phase with similar generation time compared to control. Two narcotics with high (>3.00), intermediate (>0.00 and <3.00), and low log Kow (<0. 00) values were tested. Growth of Tetrahymena inhibited up to 85% by the high log Kow toxicants (2-decanone and butylbenzene) grew with similar rates as the control, but exhibited increased lag time, suggesting that the protozoan became acclimated to toxicant stress. Results from growth of Tetrahymena in the low log Kow toxicants (ethanol and acetone) indicate an increased generation time with increasing concentration. Cells inhibited by the intermediate log Kow chemicals, 1-pentanol and anisole, exhibited a response that was a combination of the previously mentioned two contrary responses. Cells inhibited <35% with 1-pentanol and <50% with anisole grew with similar generation times as control flasks, whereas in cells inhibited >35% or >50%, respectively, the doubling times were longer than control growth.
Structure-activity models for toxicity and biodegradability of groups of m-anilines and p-phenols were developed and compared. Hydrophobicity was the most important property in determining toxicity. Whereas, electronic and steric properties were the more important in modeling biodegradation.
The aim of this project was to develop a standardized multigeneration growth inhibition test protocol to assess the sublethal effects of industrial chemicals and pesticides on protozoans. The inclusion of a test with protozoa would be an ecologically relevant supplement to the existing basic set in aquatic toxicity testing. The different aspects evaluated in the pilot ring study include: two media, two volumes, two end points and two different methods to measure the cell density. Taking into account the aim to develop a simple, sensitive, reproducible and cost effective test, recommendations are made for a standardized protocol.
The developmental toxicity for each of 45 carboxylic acids was determined for Xenopus embryos. Acids tested included 12 unbranched, saturated aliphatics, 12 branched, saturated aliphatics, 12 unsaturated aliphatics, and 9 aromatics. Embryos were collected following hormone-induced breeding and exposed to at least eight concentrations of the acid, along with a control. For each concentration, 25 properly developing embryos were exposed to the acid solution for 96 h. Each acid was tested on at least three separate occasions and the data were pooled to calculate 96-h LC50 (lethality), 96-h EC50 (malformation), and DHI (developmental hazard index = 96-h LC50/96-h EC50) values. The endpoint data were subjected to quantitative structure-activity relationship (QSAR) analyse: and computer-automated structure evaluation (CASE). Variation in acid-induced lethality was effectively explained by partitioning and ionizability of the acids, while partitioning alone was somewhat effective in explaining variation for acid-induced malformation. The results indicated that developmental hazard of the acids to Xenopus embryos is primarily dependent on carbon-chain length, with acids containing five carbon atoms in the chain tending to be the most potent. Unsaturation reduced the hazard in comparison with the corresponding unbranched saturated acid. Developmental hazard was highest for 2-position branched compounds with a 5- or 6-C chain, but was reduced for 2-position branched acids with a 3- or 4-C chain. Hazard of the non-2 position branched acids was variable. Valproic (2-propylpentanoic) acid showed the highest developmental hazard with Xenopus, twice that of any other acid tested.
The previously described pseudo-equilibrium model for kinetics of distribution of extraneous chemicals in biological systems has been used for the development of the QSAR equation expressing toxicity of phenols against Tetrahymena pyriformis as a non-linear function of their hydrophobicity and acidity. The model assumes binding of all the tested compounds to a single class of the receptors (i.e., it does not discriminate between possible narcotic and respiratory uncoupling modes of action of phenols) with the association constant related to the electronic structure of the molecules rather than to their hydrophobicity. Non-linear regression analysis revealed satisfying agreement between the model and published biological data measured after a single dose.
The ciliotoxic potential of the organophosphorous insecticides Dursban and Lorsban, their active ingredient, chlorpyrifos, and their carrier ingredients (Blanks) were assessed. Since chlorpyrifos inhibits acetylcholinesterase, the acetylcholine-innervated ciliated epithelial cultures of frog palate were used as the model. All compounds caused a decrease in frequency of ciliary beat overtime. EC50 values followed the same order as the time to inhibition. The orders were Lorsban > Dursban > chlorpyrifos, and Lorsban > Dursban approximately Lorsban Blank > Dursban Blank. Stimulation of ciliary beating occurred immediately after exposure to all compounds, followed by inhibition. Dursban, Lorsban, and both Blanks elicited stimulatory effects in the presence of atropine. Atropine only blocked the initial stimulatory response with chlorpyrifos. In addition to chlorpyrifos, some component(s) of the inert ingredients were initially stimulatory but ultimately inhibitory to ciliary beating in the frog palate model. All compounds caused mitochondrial damage, including swelling, disruption of cristae, and loss of matrix.
The dynamics of a microbial community consisting of a eucaryotic ciliate Tetrahymena pyriformis and procaryotic Escherichia coli in a batch culture is explored by employing an individual-based approach. In this portion of the article, Part I, population models are presented. Because both models are individual-based, models of individual organisms are developed prior to construction of the population models. The individual models use an energy budget method in which growth depends on energy gain from feeding and energy sinks such as maintenance and reproduction. These models are not limited by simplifying assumptions about constant yield, constant energy sinks and Monod growth kinetics as are traditional models of microbal organisms. Population models are generated from individual models by creating distinct individual types and assigning to each type the number of real individuals they represent. A population is a compilation of individual types that vary in a phase of cell cycle and physiological parameters such as filtering rate for ciliates and maximum anabolic rate for bacteria. An advantage of the developed models is that they realistically describe the growth of the individual cells feeding on resource which varies in density and composition. Part II, the core of the project, integrates models into a dynamic microbial community and provides model analysis based upon available data.
Premised on relatively simple assumptions, mathematical models like those of Monod, Pirt or Droop inadequately explain the complex transient behavior of microbial populations. In particular, these models fail to explain many aspects of the dynamics of a Tetrahymena pyriformis-Escherichia coli community. In this study an alternative approach, an individual-based model, is employed to investigate the growth and interactions of Tetrahymena pyriformis and E. coli in a batch culture. Due to improved representation of physiological processes, the model provides a better agreement with experimental data of bacterial density and ciliate biomass than previous modeling studies. It predicts a much larger coexistence domain than rudimentary models, dependence of biomass dynamics on initial conditions (bacteria to ciliate biomasses ratio) and appropriate timing of minimal bacteria density. Moreover, it is found that accumulation of E. coli sized particles and E. coli toxic metabolites has a stabilizing effect on the system.
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