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Microcount method for petrolatum-based topical ointments containing waxes.

A practical solvent system for the detection of microorganisms in topical ointments has been developed. The method involves dissolving 0.5 g of topical ointment in 50 ml of a solvent mixture (92 parts isopropyl myristate, 6 parts carbon disulfide, and 2 parts xylene) and filtering it through a 0.45-mum membrane filter. Residual solvent is then washed from the filter pad with 200 ml of sterile 0.5% Brain Heart Infusion broth containing 0.1% Tween 80. The filter pad is then removed and placed on a petri plate containing Trypticase Soy Agar medium. The petri plates thus prepared are then incubated at 37 C for 7 days, and the colonies produced are then counted. The toxicity of the solvent mixture was determined against Staphylococcus aureus, Escherichia coli, Pseudomonas aeruginosa, Salmonella newington, and spores of Bacillus subtilis and was found to be less toxic than the heat-sterilized isopropyl myristate and comparable to the filter-sterilized isopropyl myristate.

Bacillus subtilis↗

Carcinogenic mixtures.

Human populations are generally exposed simultaneously to a number of toxicants present in the environment, including complex mixtures of unknown and variable origin. While scientific methods for evaluating the potential carcinogenic risks of pure compounds are relatively well established, methods for assessing the risks of complex mixtures are somewhat less developed. This article provides a report of a recent workshop on carcinogenic mixtures sponsored by the Committee on Toxicology of the U.S. National Research Council, in which toxicological, epidemiological, and statistical approaches to carcinogenic risk assessment for mixtures were discussed. Complex mixtures, such as diesel emissions and tobacco smoke, have been shown to have carcinogenic potential. Bioassay-directed fractionation based on short-term screening test for genotoxicity has also been used in identifying carcinogenic components of mixtures. Both toxicological and epidemiological studies have identified clear interactions between chemical carcinogens, including synergistic effects at moderate to high doses. To date, laboratory studies have demonstrated over 900 interactions involving nearly 200 chemical carcinogens. At lower doses, theoretical arguments suggest that risks may be near additive. Thus, additivity at low doses has been invoked as as a working hypothesis by regulatory authorities in the absence of evidence to the contrary. Future studies of the joint effects of carcinogenic agents may serve to elucidate the mechanisms by which interactions occur at higher doses.

Animals↗

Lethality and EROD-inducing potency of chlorinated chrysene in chick embryos.

Chrysene was non-specifically chlorinated and the toxic potency of the mixture formed was studied. The chlorinated mixture was considerably more potent than the parent compound in terms of embryolethality and EROD and AHH induction in a 2-week test in chick embryos. The chlorinated chrysene caused anomalies, including edema and beak defects, similar to those previously found after treatment of chick embryos with coplanar PCBs. Chlorinated chrysene was also much more potent than chrysene as an inducer of EROD in a 72-hour test in chick embryos in ovo and in chick embryo liver in vitro. It seems that the mechanism of toxicity of chlorinated chrysene in chick embryos is similar to that of the coplanar PCBs and other Ah receptor ligands. The effects of the chlorinated mixture were mainly accounted for by 6- chlorochrysene and 6,12-dichlorochrysene.

Animals↗

Growth stimulation and inhibition effects of 4-hydroxybenzoic acid and some related compounds on the freshwater green alga Pseudokirchneriella subcapitata.

4-hydroxybenzoic acid (4-HBA) exhibited low algal toxicity with the 72-h median inhibition concentration (IC50) of 9.9 mmol/L in the standard growth inhibition test using the freshwater green alga Pseudokirchneriella subcapitata. In contrast, it stimulated the algal growth at lower concentrations ranging from 0.1 to 1.0 mmol/L. Comparative studies with benzoic acid and 2- and 3-hydroxybenzoic acids (2-HBA and 3-HBA) indicated that 2-HBA was the most toxic, giving a 72-h IC50 of 0.172 mmol/L, and 4-HBA was the least toxic and that only 4-HBA had the pronounced growth stimulation activity. In a semicontinuous exposure to 4-HBA (0.15 and 0.3 mmol/L), algae maintained increased cell growth compared with controls during up to 10 times consecutive batch cultures, without any indication of adaptive responses to the growth enhancing effect of 4-HBA. Return to the clean standard medium of the exposed cells resulted in the quick recovery from the stimulant effect. Furthermore, 4-HBA (0.3 mmol/L) was found to diminish the toxicity of 2-HBA (<1.0 mmol/L). The presence of such compounds in the complex mixture might interact with other toxicants to alter the whole toxicity when assessed by the algal growth inhibition test. The effects of 4-HBA on P. subcapitata growth observed in the present study are not expected for planktonic algae in the aquatic environments, because known environmental concentrations are far below the effective concentration range.

Chlorophyta↗

The relative toxicity of compounds in mainstream cigarette smoke condensate.

Many different in vivo and in vitro tests are currently used to assess the toxicity of chemicals and complex mixtures such as cigarette smoke condensate. In vivo tests include assays in rodents to determine carcinogenicity, tumorigenicity and reproductive effects In vitro tests of mutagenicity are conducted with both bacterial and mammalian cell systems. A first step towards lowering the toxicity of cigarette smoke condensate is the identification of the relevant compound However, changing the concentration of a given smoke component may not linearly alter the biological activity of the complex mixture due to interactive effects. The "effective toxicity" of a chemical constituent is a function of the concentration, the metabolic fate, the potency in in vivo and in vitro assays, and the ability to reach the target tissues. The logarithm of the octanol-water partition coefficient (log P) is an important parameter since it affects metabolism, biological transport properties and intrinsic toxicity. Using concentration data from the International Agency for Cancer Research (IARC), biological activity data from the Registry of Toxic Effects of Chemical Substances (RTECS) database and measured and calculated log P values, we have rank ordered some of the important compounds in cigarette smoke condensate by their measured or potential toxicity. Condensates from different cigarette brands, tar categories and styles vary in their concentrations of these compounds. Chemicals of greater commercial or scientific interest may be toxicity tested more extensively, thereby increasing the probability of positive test results and highlighting the need for consideration of structure-activity relationships.

Acetaldehyde↗

Factors affecting R6 fungicide toxicity on sea urchin fertilization and early development: roles of exposure routes and mixture components.

A technical fungicide mixture, R6 and its components, cymoxanil (CYM) and cupric oxychloride (Cu-OCl), were tested by sea urchin bioassays (Paracentrotus lividus and Sphaerechinus granularis). A set of toxicity endpoints was evaluated including both lethal and sublethal effects with the following endpoints: (a) acute embryotoxicity, (b) developmental defects, (c) changes in sperm fertilization success, (d) transmissible damage from sperm to the offspring, and (e) cytogenetic abnormalities. Acute effects on developing embryos were observed as early (prehatch) mortality at R6 levels > or =25 microg/ml. The pesticide mixture R6 was tested at realistic concentrations, ranging from 25 ng/ ml to 2.5 microg/ml, and the two components, CYM and Cu-OCl, were tested, either alone or in mixture, at concentrations equal to their levels in the corresponding R6 solutions. R6 was either dissolved in filtered seawater (water only, W-O), or spiked in "pristine" silt-clay sediment or soil samples before bioassays. Developmental toxicity of R6, following W-O dissolution, displayed a significant dose-related increase of larval malformations and differentiation arrest at concentrations of 750 ng/ml to 2.5 microg/ml both in P. lividus and in S. granularis larvae. Developmental toxicity was removed in spiked sediment up to R6 nominal levels (25 microg/ml), 10-fold above the embryotoxic R6 levels in W-O exposure. No significant developmental toxicity was exerted by CYM or Cu-OCl (W-O exposure) up to their concentrations equivalent to 2.5 microg/ml R6. The laboratory-prepared mixture of CYM and Cu-OCl, in the same concentration range, only resulted in minor effects, as larval retardation, suggesting the presence of toxic impurities (or additional components) in the R6 formulation. When sperm from either P. lividus or S. granularis were exposed to R6 before fertilization, a W-O exposure resulted in a dose-related decrease in fertilization of P. lividus sperm (up to 250 microg/ml R6), whereas S. granularis sperm underwent a significant increase of fertilization rate at the highest R6 nominal levels (up to 25 microg/ml). Equivalent CYM or Cu-OCl levels were ineffective on sperm fertilization success in both species. The offspring of S. granularis sperm exposed to 25 microg/ml R6 showed a significant increase in larval malformations, which were not detected in the offspring of R6-exposed P. lividus sperm. Again, CYM or Cu-OCl was unable to exert any transmissible damage from sperm to the offspring in either species. The present study raises the case of possible discrepancies between toxicity of a technical mixture and of its analytical-grade components, also providing evidence for a loss of pesticide toxicity following dispersion in an environmental matrix such as sediment or soil.

Acetamides↗

Comparative lethality of methanol, ethanol and mixtures in female rats.

The lethalities of pure methanol and pure ethanol were compared to two mixtures of ethanol/methanol with the following percentages (95/5% and 65/35% v/v). This study was conducted to simulate situations of human exposure to denaturated alcohol (by 5% methanol) or adulterated alcohol (by 35% methanol). Four groups of female adult virgin albino rats were treated with the four mixtures. A fifth group was used as a vehicle control. Graded oral doses were given to eight animals per dose. Lethality over 24 h was used as an end-point. The LD50 was calculated for each of the four treatments on a molar basis. A dose-response function for each mixture was plotted of percentage lethality vs. mmol kg-1 equivalent to the given ml kg-1 dose. Results showed a significantly different LD50 estimates (P less than 0.03) for the four mixtures. The order of lethal toxicity was as follows: 95/5% methanol/ethanol, pure methanol, pure ethanol then 65/35% methanol/ethanol. Slope comparisons indicated two pairs: 65/35% ethanol/methanol and pure ethanol yielding a steep slope, and 95/5% ethanol/methanol and pure methanol yielding a shallow slope. These data indicated that the acute lethality of ethanol/methanol mixtures is a complex unpredictable function. This toxicity presumably depends in a complicated way on the differences in the effective molecular weights of the two alcohols in each of the mixtures.

Animals↗

Effects of organic solvents and solvent-atrazine interactions on two algae, Chlorella vulgaris and Selenastrum capricornutum.

When assessing pesticides toxicity on test organisms, the use of organic solvents is frequently required to formulate solutions of pesticides having low or moderate water solubility. These solvents may influence the results of toxicity tests. This study examined the effects of ethanol and dimethyl sulfoxide (DMSO) on two species of algae, Chlorella vulgaris and Selenastrum capricornutum. The interactives effects of these organic solvents with various concentrations of atrazine were tested to analyse how these solvents can affect the toxicity of atrazine. Toxicity was measured as the change in chlorophyll (a) content (estimated via fluorescence) in cultures of the test organism that were incubated over a 96-h period at standard conditions of temperature and light. In the absence of atrazine, ethanol was toxic to both algae, yielding significant inhibition of chlorophyll (a) content at concentrations as low as 0.05%. Morever, S. capricornutum was less sensitive to ethanol than was C. vulgaris. DMSO did not show any toxic effects on either chlorophycea. At concentrations up to 0.5%, DMSO interacted additively with atrazine for both chlorophycea. An additive response was also observed with ethanol towards S. capricornutum. For C. vulgaris, ethanol interacted antagonistically at most of atrazine concentrations and gave few additive and synergistic interactions. An additive response of an atrazine-solvent mixture indicate the inherent toxicity of the atrazine. Since DMSO generally gave additive responses for both algae, it can be considered as an adequate organic solvent to use in bioassays.

Atrazine↗

Reproductive system impairment of mice fed diets containing beluga whale blubber from the St Lawrence estuary and arctic populations.

The toxic potential of naturally relevant mixtures of PCBs and other organohalogens on the reproductive system of C57Bl/6 female mice was assessed. Mice were fed diets in which lipids were replaced by blubber of beluga whales from a highly contaminated population of the Saint Lawrence River, and a less contaminated population from the Arctic Ocean. Ratios of blubber from both sources were mixed in order to perform a dose-response study. Control mice were fed diets for 90 d in which fat was replaced by corn oil or beef tallow. There were no significant effects of diets on body, liver, spleen or thymus weights. Similarly ovulation occurred in all control and experimental groups. However, Graafian follicles from ovaries of mice fed contaminated diets showed abnormal development of oocytes. Cumulus granulosa cells bind normally to the oocyte prior to ovulation and are essential for sperm penetration and fertilization. These cells were absent in both Graafian follicles and ovulated oocytes in the oviduct of all groups fed contaminated diets. Oviducts of these mice revealed evidence of epithelial degeneration. These results suggest the female mouse reproductive system is sensitive to organohalogens and illustrate the toxic potential of contaminant mixtures as found in the less contaminated Arctic population.

Adipose Tissue↗

The effect of attapulgite and charcoal on enterotoxicity of Vibrio cholerae and Escherichia coli enterotoxins in rabbits.

Vibrio cholerae and certain strains of Escherichia coli produce heat-labile enterotoxins which play a significant role in the pathogenesis of the intestinal disease. Activated attapulgite, a heated magnesium aluminum silicate, was previously shown to prevent the toxic effects of endotoxin. The present study has revealed that this drug inhibits the toxic effects of cholera and E. coli enterotoxins in the intestinal loop of rabbits, when toxin and attapulgite are pre-incubated prior to injection. Up to 50 to 100 minimal effective doses are inhibited. Attapulgite is effective also when injected separately, albeit simultaneously, into the intestinal loops, but not when administered after the toxin. Since supernates of toxinattapulgite mixtures are non-toxic, it is postulated that attapulgite acts by adsorption and that the attached enterotoxin is no longer toxic to the rabbit intestine. The previously reported effect of charcoal on V. cholerae enterotoxin paralleling that of attapulgite, was confirmed. In contrast to the effects of these absorbents on isolated toxin, both failed to prevent enterotoxicity in the rabbit model of an enterotoxin-producing strain of E. coli.

Aluminum Silicates↗

An in situ toxicity identification evaluation method Part II: Field validation.

When sediments are found to be toxic usually there is a mixture of chemicals present. Often it is important to establish which chemicals contribute to the toxicity. Establishing causality can be difficult and often requires fractionation with subsequent toxicity testing. The sample collection and manipulation process can alter chemical bioavailability and toxicity. An in situ toxicity identification evaluation (iTIE) chamber is described that was placed in sediments and fractionated pore-water chemicals into nonpolar chemicals, metals, and ammonia-type groups. This method was field tested and compared to the laboratory-based, U.S. Environmental Protection Agency (U.S. EPA) toxicity identification evaluation (TIE) method. Field studies were performed at three sites contaminated primarily with polycyclic aromatic hydrocarbons (PAHs) (Little Scioto River, OH, USA), polychlorinated biphenyls (PCBs) (Dicks Creek, OH, USA), and chlorobenzenes (Sebasticook River, ME, USA). Both the iTIE and the U.S. EPA TIE methods used Daphnia magna in 24-h exposures. Although the iTIE and TIE were conducted on sediments from the same location, there was significantly more toxicity observed in the iTIE testing. The dominant chemical classes were separated by the iTIE method and revealed which fractions contributed to toxicity. The loss of toxicity in the TIE approach did not allow for subsequent fractionation and stressor identification. Advantages of the iTIE over the TIE method were greater sensitivity and ability to detect causative toxic chemical fractions; lack of sediment collection and subsequent manipulation; and, thus, reduction in potential artifacts, more realistic exposure with slow, continual pore-water renewal in situ, ability to evaluate pore waters in sandy or rocky substrates where pore waters are difficult to collect, and a quicker phase I evaluation. Limitations of the iTIE method as compared to the TIE methods were extensive pretest assembly process, fewer phase I fractionation possibilities, and restriction to shallow waters. The results of these studies suggest that the iTIE method provides a more accurate and sensitive evaluation of pore water toxicity than the laboratory TIE method.

Animals↗

NTP-CERHR Monograph on the Potential Human Reproductive and Developmental Effects of Di-isononyl Phthalate (DINP).

The National Toxicology Program (NTP) Center for the Evaluation of Risks to Human Reproduction (CERHR) conducted an evaluation of the potential for di-isononyl phthalate (DINP) to cause adverse effects on reproduction and development in humans. DINP is one of 7 phthalate chemicals evaluated by the NTP CERHR Phthalates Expert Panel. These phthalates were selected for evaluation because of high production volume, extent of human exposures, use in children's products, and/or published evidence of reproductive or developmental toxicity. DINP is a mixture of branched, C-9 phthalate isomers used to add flexibility to a wide variety of plastic products such as toys, garden hoses, flooring tiles, tarps, and pool liners. The results of this evaluation on DINP are published in a NTP-CERHR monograph which includes: 1) the NTP Brief, 2) the Expert Panel Report on the Reproductive and Developmental Toxicity of Di-isononyl Phthalate, and 3) public comments received on the Expert Panel Report. As stated in the NTP Brief, the NTP reached the following conclusions regarding the possible effects of exposure to DINP on human development and reproduction. First, although DINP could possibly affect human development if exposures are sufficiently high, there is minimal concern for DINP causing adverse effects to human reproduction or fetal development. There is no direct evidence that exposure of people to DINP adversely affects reproduction or development, but studies show that oral exposure of pregnant rats to high doses (500 and 1000 mg/kg bodyweight/day) of DINP can adversely affect fetal development. Effects on pup growth were noted in a 2-generation reproductive toxicity study in rats at doses of 143-285 mg/kg body weight/day. Human exposure information for DINP was not available but it was assumed that the general US population would be exposed to 3-30 mug/kg body weight/day, based upon the range of estimated exposures for DEHP, a more widely used phthalate. Second, based on estimates of exposure of children to DINP from mouthing toys and other objects, the NTP has minimal concern for developmental effects in children. After the expert panel meeting, a US Consumer Products Safety Commission panel estimated that the majority of children exposed to DINP had a "minimum to non-existent risk of injury" from mouthing toys. Children's exposure was estimated at 70-280 mug/kg body weight/day, a level 1000-fold lower than exposures resulting in developmental effects in rats. NTP-CERHR monographs are transmitted to federal and state agencies, interested parties, and the public and are available electronically in PDF format on the CERHR web site (http://cerhr.niehs.nih.gov) and in printed text or CD-ROM from the CERHR (National Institute of Environmental Health Sciences, P.O. Box 12233, MD EC-32, Research Triangle Park, NC; fax: 919-316-4511).

Journal Article↗

NTP-CERHR Monograph on the Potential Human Reproductive and Developmental Effects of Di-Isodecyl Phthalate (DIDP).

The National Toxicology Program (NTP) Center for the Evaluation of Risks to Human Reproduction (CERHR) conducted an evaluation of the potential for di-isodecyl phthalate (DIDP) to cause adverse effects on reproduction and development in humans. DIDP is one of 7 phthalate chemicals evaluated by the NTP CERHR Phthalates Expert Panel. These phthalates were selected for evaluation because of high production volume, extent of human exposures, use in children's products, and/or published evidence of reproductive or developmental toxicity. DIDP is a mixture of branched, C-10 phthalate isomers used to add flexibility to a wide variety of polyvinylchloride (PVC) plastic products such as artificial leather, toys, carpet backing, and pool liners. The results of this evaluation on DIDP are published in a NTP-CERHR monograph which includes: 1) the NTP Brief, 2) the Expert Panel Report on the Reproductive and Developmental Toxicity of Di-Isodecyl Phthalate, and 3) public comments received on the Expert Panel Report. As stated in the NTP Brief, the NTP reached the following conclusions regarding the possible effects of exposure to DIDP on human development and reproduction. First, although DIDP could possibly affect human development if exposures are sufficiently high, there is minimal concern for developmental effects in fetuses and children at current proposed/estimated exposure levels. There is no direct evidence that exposure of people to DIDP adversely affects reproduction or development, but show that oral exposure of pregnant rats to high doses (200 and 1000 mg/kg bodyweight/day) of DIDP can adversely affect fetal development. Human exposure information for DIDP was not available, but it was assumed that the general US population would be exposed to 3-30 mug/kg body weight/day, based upon the range of estimated exposures for DEHP, a more widely used phthalate. Second, there is negligible concern for reproductive toxicity in exposed adults. Studies evaluated showed that, at high exposure levels, there is no evidence of adverse reproductive effects in rats. NTP-CERHR monographs are transmitted to federal and state agencies, interested parties, and the public and are available electronically in PDF format on the CERHR web site (http://cerhr.niehs.nih.gov) and in printed text or CD-ROM from the CERHR (National Institute of Environmental Health Sciences, P.O. Box 12233, MD EC-32, Research Triangle Park, NC; fax: 919-316-4511).

Journal Article↗

Indoor air quality and health in offices and other non-industrial working environments.

BACKGROUND: Over the last 30 years, transformation of indoor environments--in particular in office blocks--has been associated with complaints from workers of discomfort, malaise and even diseases termed Building Related Illnesses (BRI) which are classified as specific (e.g. Legionnaire disease, asthma, hypersensitivity pneumonia) or non-specific (e.g. the Sick Building Syndrome). METHODS: A review was made of data from international public health organisations, epidemiological, clinical and experimental studies and congress proceedings from 1990 to 2006 on the topic of indoor air quality and health in modern, non-industrial workplaces. RESULTS: Studies focused on ventilation, temperature and air humidity and specific pollutants such as Volatile Organic Compounds, particules asbestos fibres, environmental tobacco smoke, radon and biological agents. We can now measure microclimate parameters and many indoor air pollutant levels as well as their effects on health; we can also formulate indications of threshold and guideline values for some of these and make a preventive assessment for toxic emissions from construction and furnishing materials. A stepwise, multi-disciplinary approach--with the specialist in occupational medicine playing a major role--is most suitable for dealing with BRI and the effects of poor indoor air quality on health. CONCLUSIONS: Better criteria are needed to study emission of substances into the indoor environment, adequacy of ventilation, additive or synergistic effects of mixtures of chemicals and toxicity of micro-organism decomposition products. Objective clinical tests to assess the effects of indoor pollutants on health and indices for Indoor Environmental Quality in assessing buildings need to be improved.

Air Pollutants, Occupational↗

Comparative toxicity of four chlorinated dibenzo-p-dioxins (CDDs) and their mixture. IV. Determination of liver concentrations.

Groups of male Sprague-Dawley rats were administered orally the following chlorinated dibenzo-p-dioxins (CDDs) in corn oil/acetone (95/5; v/v): 30-60 micrograms/kg 2,3,7,8-tetrachlorodibenzo-dioxin (tetra-CDD), 160-270 micrograms/kg1,2,3,7,8-pentachlorodibenzo-p-dioxins (penta-CDD), 630-1249 micrograms/kg 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin (hexa-CDD) and 5000-8000 micrograms/kg 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (hepta-CDD) or a mixture of the four homologues such that each was present in the mixture at one quarter of its dose as a single compound. Animals were killed at 2 and 8 days after dosing. Livers were immediately removed, and aliquots frozen in liquid nitrogen. Storage occurred at -80 degrees C until further use. About 0.2 g of each lyophilized rat liver was extracted, the extract purified by column chromatography and analyzed by GC/MS for CDD content. Results obtained suggest that the absorption of CDDs after oral administration decreases in the order of tetra-CDD > or = penta-CDD > hexa-CDD > hepta-CDD, indicating that the dose was an incomplete surrogate of exposure in parts I-III of this publication series (Stahl et al. 1992; Weber et al. 1992a,b). Moreover, data also support the notion that the pharmacokinetics of CDD mixtures at high doses are somewhat different from those expected based on single compound exposures. Our findings suggest that the intrinsic relative potency in terms of toxic equivalents (TEQ) of the higher chlorinated homologues is slightly greater (about a factor of 2) than suggested by Stahl et al.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

Evidence that nicotine acetylcholine receptors are not the main targets of cotinine toxicity.

The toxicity of nicotine, cotinine and their mixtures was studied in Mus musculus mice as well their effects on growth after repetitive administration to young mice. The affinity constants of the two alkaloids for the nicotinic acetylcholine receptors (nAChRs) of Torpedo and rat brain membranes were determined. The administration of these alkaloids produced distinct symptoms of intoxication. Nicotine was 100-fold more toxic than cotinine and 10-fold more rapid than cotinine at producing respiratory arrest. The affinity of nicotine for both subtypes of nAChRs was > 100-fold higher than that of cotinine. Repetitive administrations of nicotine caused weight loss, whereas that of cotinine caused weight gain (P < 0.01). The administration of the two alkaloids as mixtures to mice caused significantly (P < 0.01) higher mortality than theoretically expected. Furthermore, hexamethonium pretreatment reduced by 2-fold (P < 0.01) the toxicity of nicotine but enhanced by 1.6-fold (P < 0.01) that of cotinine and was without effects on toxicity of mixtures. We suggest that nAChRs are not the main targets of cotinine toxicity.

Animals↗

Including transformation products into the risk assessment for chemicals: the case of nonylphenol ethoxylate usage in Switzerland.

A method for applying the risk assessment approach using ratios of predicted environmental concentrations (PECs) and predicted no-effect concentrations (PNECs) to mixtures of parent compounds and their environmental transformation products is presented. Nonylphenol ethoxylates (NPnEOs) and a selection of their most relevant transformation products are investigated as a case study illustrating the method. The PEC values of NPnEO and its transformation products are calculated with a regional multimedia fate model including the transformation kinetics of the NPnEO degradation cascade. PNEC values are derived from a selection of toxicity data on NPnEO and its transformation products. The toxicity of the emerging mixture of NPnEO and its transformation products is then estimated under the assumption of concentration addition (similar mode of action). On this basis, PEC-to-PNEC ratios for the aquatic environment and the sediment are calculated for the individual components of the mixture and the mixture itself. For this purpose, average release rates of NPnEO and its transformation products from Swiss sewage treatment plants were used. While the PEC values of the individual components do not exceed the corresponding PNEC values, the risk quotient of the mixture in water is greater than 1. In sediment, the mixture does not exceed a risk quotient of 1. A combination of sensitivity and scenario analyses is employed to identify the upper and lower bounds of the results.

Animals↗

Photo-induced toxicity of PAHs to Hyalella azteca and Chironomus tentans: effects of mixtures and behavior.

In the aquatic environment, polycyclic aromatic hydrocarbon (PAH) contamination can result from several anthropogenic sources such as petroleum runoff, industrial processes, and petroleum spills. When ultraviolet light (UV) is present at sufficient intensity, the acute toxicity of some PAHs to aquatic biota is greatly enhanced. This photo-induced toxicity of PAHs is directly influenced by the amount of PAH and by the level of UV intensity present in the aquatic environment. Thus, behavioral responses and habits that affect an aquatic organism's exposure to UV as well as exposure to PAHs can influence the extent to which damage due to photo-induced toxicity occurs. Experiments demonstrated the effects of photo-induced toxicity of anthracene and fluoranthene on the survival of two benthic macroinvertebrates, the midge Chironomus tentans and the freshwater amphipod Hyalella azteca. This study further investigated the survival and behavior of the test organisms in different substrates (no substrate, a sand monolayer, leaf discs, and sediment) with and without UV. The free-swimming, epibenthic H. azteca avoided the effects of photo-induced toxicity of PAHs to some extent by hiding in leaves when this substrate was available. Results emphasize the importance of organisms' behavior in affecting the photo-induced toxicity of PAHs in the aquatic environment.

Journal Article↗