964 resultados para Toxic effect
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Purpose: To investigate the adverse effect of intravitreal injection of normal saline (NS) and phosphate buffered saline (PBS) in mouse eyes.
Methods: NS or PBS was injected intravitreally into C57BL/6J mouse eyes. Retinal lesions were monitored by fundus imaging, spectral-domain optical coherence tomography (SD-OCT), and histological investigations. Retinal immune gene expression was determined by real-time polymerase chain reaction (PCR). The toxic effect of NS and PBS or retinal protein from NS- or PBS-injected eyes on retinal pigment epithelium (RPE) was tested in B6-RPE-07 mouse RPE cell cultures.
Results: Intravitreal injection of NS dose-dependently induced localized retinal lesion in mice. Histological investigations revealed multiple vacuoles in photoreceptor outer segments and RPE cells. The lesions recovered over time and by 3 weeks post injection the majority of lesions vanished in eyes receiving 1 μl NS. Inflammatory genes, including TNF-α, IL-1β, IL-6, iNOS, and VEGF were upregulated in NS injected eyes. Intravitreal injection of PBS did not cause any pathology. The treatment of B6-RPE07 cells with 30% PBS or 30% NS did not affect RPE viability. However, incubation of 1-μg/ml retinal protein from NS-injected eyes, but not PBS-injected eyes induced RPE cell death.
Conclusion: NS is toxic to the C57BL/6J mouse retina and should not be used as a vehicle for intraocular injection. PBS is not toxic to the retina and is a preferred vehicle.
Translational Relevance: NS is not a physiological solution for intraocular injection in the C57BL/6J mice and questions its suitability for intraocular injection in other species, including human.
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Aflatoxin B1 (AFB1), ochratoxin A (OTA) and fumonisin B1 (FB1) are contaminants which have been shown to regularly co-occur in a range of foods. However, only a small number of studies have evaluated the interactive effect of binary and tertiary mycotoxins. The present study evaluated the effects of low levels of each mycotoxin in combination at their EU regulatory limits. Toxic effect with respect to cell viability was measured by MTT and neutral red assays, assessing mitochondria and lysosome integrities respectively. Individual toxicity showed that OTA (10 μg/ml) was the most cytotoxic mycotoxin in all three cell lines studied (caco-2, MDBK and raw 264.7). Binary combinations were cytotoxic to the MDBK cell line in the order [OTA/FB1] > [AFB1/FB1] > [AFB1/OTA], whilst all effects observed were classified as being additive. Tertiary combinations of AFB1, FB1 and OTA at the EU regulatory limits were tested and not found to exhibit measurable cytotoxicity in MDBK, caco-2 or raw 264.7 cells. However by increasing these concentrations above the legal limits to OTA (3 μg/ml), FB1 (8 μg/ml) and AFB1 (1.28 μg/ml), cytotoxicity was observed with up to 26% reduction in cell viability and synergistic effects were evident with regard to mitochondrial integrity. © 2014 Elsevier Ltd. All rights reserved.
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Kenyan tannery and associated environmental samples were selected for ecotoxicological assessment. A tool-kit of techniques was developed, including whole-cell biosensor and chemical assays. A luminescence based bacterial biosensor (Escherichia coli HB101 pUCD607) (via a multi-copy plasmid) was used for toxicity assessment. Samples were manipulated prior to biosensor interrogation to identify the nature of the toxic contaminants. Untreated samples (before any manipulations) showed a strong toxic effect at the discharge point in comparison to other sampling points. Sparging was used to identify toxicity associated with volatile organics. The toxicity of contaminants, removed by treatment with activated charcoal was identified for all the sampling points except for those upstream of effluent discharges. Filtration identified toxicity associated with suspended solids. Changes in availability of toxic contaminants due to pH adjustment of most samples from the tannery effluent treatment pits were also associated with the extreme pH values (4.0 and 8.0). The approach used has highlighted the complexicity of toxic pollutants in effluent from the tanning industry and the dissection of toxicity points to possible remediation strategies for effluents from the tanning industry.
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Interaction of organic xenobiotics with soil water-soluble humic material (WSHM) may influence their environmental fate and bioavailability. We utilized bacterial assays (lux-based toxicity and mineralization by Burkholderia sp. RASC) to assess temporal changes in the bioavailability of [14C]-2,4-dichlorophenol (2,4-DCP) in soil water extracts (29.5 μg mL-1 2,4-DCP; 840.2 μg mL-1 organic carbon). HPLC determined and bioavailable concentrations were compared. Gel permeation chromatography (GPC) was used to confirm the association of a fraction (>50%) of [14C]-2,4-DCP with WSHM. Subtle differences in parameters describing 2,4-DCP mineralization curves were recorded for different soil-2,4-DCP contact times. Problems regarding the interpretation of mineralization data when assessing the bioavailability of toxic compounds are discussed. The lux-bioassay revealed a time-dependent reduction in 2,4-DCP bioavailability: after 7 d, less than 20% was bioavailable. However, GPC showed no quantitative difference in the amount of WSHM-associated 2,4-DCP over this time. These data suggest qualitative changes in the nature of the 2,4-DCP-WSHM association and that associated 2,4-DCP may exert a toxic effect. Although GPC distinguished between free- and WSHM-associated 2,4-DCP, it did not resolve the temporal shift in bioavailability revealed by the lux biosensor. These results stress that assessment of risk posed by chemicals must be considered using appropriate biological assays.
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Dissertação de mestrado, Ciências Biomédicas, Departamento de Ciências Biomédicas e Medicina, Universidade do Algarve, 2015
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This work explores the use of fluorescent probes to evaluate the responses of the green alga Pseudokirchneriella subcapitata to the action of three nominal concentrations of Cd(II), Cr(VI), Cu(II) and Zn(II) for a short time (6 h). The toxic effect of the metals on algal cells was monitored using the fluorochromes SYTOX Green (SG, membrane integrity), fluorescein diacetate (FDA, esterase activity) and rhodamine 123 (Rh123, mitochondrial membrane potential). The impact of metals on chlorophyll a (Chl a) autofluorescence was also evaluated. Esterase activity was the most sensitive parameter. At the concentrations studied, all metals induced the loss of esterase activity. SG could be used to effectively detect the loss of membrane integrity in algal cells exposed to 0.32 or 1.3 μmol L−1 Cu(II). Rh123 revealed a decrease in the mitochondrial membrane potential of algal cells exposed to 0.32 and 1.3 μmol L−1 Cu(II), indicating that mitochondrial activity was compromised. Chl a autofluorescence was also affected by the presence of Cr(VI) and Cu(II), suggesting perturbation of photosynthesis. In conclusion, the fluorescence-based approach was useful for detecting the disturbance of specific cellular characteristics. Fluorescent probes are a useful diagnostic tool for the assessment of the impact of toxicants on specific targets of P. subcapitata algal cells.
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Metal contamination of the environment is frequently associated to the presence of two or more metals. This work aimed to study the impact of a mixture of metals (Cd, Pb and Zn) on the physiology of the non-conventional yeast Pichia kudriavzevii. The incubation of yeast cells with 5 mg/l Cd, 10 mg/l Pb and 5 mg/l Zn, for 6 h, induced a loss of metabolic activity (assessed by FUN-1 staining) and proliferation capacity (evaluated by a clonogenic assay), with a small loss of membrane integrity (measured by trypan blue exclusion assay). The staining of yeast cells with calcofluor white revealed that no modification of chitin deposition pattern occurred during the exposure to metal mixture. Extending for 24 h, the exposure of yeast cells to metal mixture provoked a loss of membrane integrity, which was accompanied by the leakage of intracellular components. A marked loss of the metabolic activity and the loss of proliferation capacity were also observed. The analysis of the impact of a single metal has shown that, under the conditions studied, Pb was the metal responsible for the toxic effect observed in the metal mixture. Intracellular accumulation of Pb seems to be correlated with the metals' toxic effects observed.
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O chumbo é um importante poluente ambiental. A levedura Saccharomyces cerevisiae constitui um modelo útil para o estudo dos efeitos tóxicos do chumbo. O conhecimento dos mecanismos de defesa e resistência à presença de metais pesados poderá ser útil em tecnologias de proteção ambiental, nomeadamente no desenvolvimento de novas metodologias para a biorremediação de metais pesados. O presente trabalho teve como objetivo avaliar o impacto do Pb na capacidade proliferativa, na integridade membranar e na produção intracelular de espécies reativas de oxigénio (ROS), na estirpe laboratorial da levedura Saccharomyces cerevisiae BY4741 (estirpe selvagem, WT). Foi também estudado o papel das mitocôndrias, como fonte de ROS induzida por Pb, e o envolvimento da H+-ATPase vacuolar (V-ATPase) e de transportadores vacuolares pertencentes à superfamília ABC (de ATP-binding cassette) na defesa contra a toxicidade do Pb. O estudo cinético do impacto de duas concentrações de Pb na viabilidade das leveduras (avaliado através de um ensaio clonogénico), na integridade da membrana celular (determinada com iodeto de propídio) e na produção intracelular de ROS (o anião superóxido foi detetado com dihidroetídio e o peróxido de hidrogénio com 2’,7’- diclorodihidrofluoresceína), revelou uma perda progressiva da capacidade proliferativa (53 e 17% de células viáveis, após a exposição durante 3h a 250 ou 1000 µmol/l de chumbo, respetivamente), coincidente com a acumulação intracelular de anião superóxido e de peróxido de hidrogénio, na ausência de perda da integridade membranar. A importância das mitocôndrias na produção de ROS, induzida por chumbo, foi levada a cabo usando um mutante deficiente respiratório desprovido de ADN mitocondrial (ƿ0). Quando comparado com a respetiva estirpe parental, o mutante ƿ0 apresentou uma maior resistência ao Pb e uma menor produção de ROS induzida por Pb. A exposição das células da estirpe BY4741 a 250 e 1000 µmol/l de chumbo originou a formação de 49 e 58% de células deficientes respiratórias, respetivamente. A função da V-ATPase, na desintoxicação de chumbo, foi avaliada utilizando mutantes com uma estrutura vacuolar normal mas defetivos em subunidades da VATPase (vma1Δ, vma2Δ, vma3Δ e vph1Δ). Comparativamente às células da estirpe WT, todos os mutantes testados, sem V-ATPase funcional, apresentaram uma maior suscetibilidade ao Pb. O papel dos transportadores vacuolares pertencentes à superfamília ABC, na defesa contra a toxicidade induzida por chumbo, foi levada a cabo utilizando mutantes sem os transportadores Ycf1p ou Vmr1p. Os resultados preliminares mostraram que quando comparadas com as células da estirpe WT, as células das estirpes ycf1Δ ou vmr1Δ não apresentavam uma maior perda da viabilidade. A modificação da morfologia vacuolar, em células expostas a chumbo, foi visualizada utilizando a estirpe Vma2p-GFP. O tratamento das células com Pb originou a fusão dos vacúolos de tamanho médio num único vacúolo de grande dimensão. Em conclusão, os estudos desenvolvidos no presente trabalho, utilizando a estirpe laboratorial BY4741, mostraram que a perda da capacidade proliferativa das leveduras, induzida pelo chumbo, pode ser atribuída à acumulação intracelular do anião superóxido e de peróxido de hidrogénio. As mitocôndrias parecem ser uma das principais fontes de ROS induzido por Pb e, simultaneamente, um dos principais alvos da sua toxicidade. Em S. cerevisiae, o vacúolo desempenha um papel importante na desintoxicação do Pb. A modificação da morfologia vacuolar após exposição ao chumbo poderá ser a consequência da acumulação de Pb no vacúolo. Enquanto os transportadores da superfamília ABC parecem não estar envolvidos na sequestração vacuolar de Pb, é necessária a presença, num estado funcional, da V-ATPase para que ocorra a compartimentação do Pb. Muito provavelmente, a compartimentação do Pb no vacúolo previne a sua acumulação no citosol e o desencadear dos respetivos efeitos tóxicos.
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50 years ago, the introduction of penicillin, followed by many other antibacterial agents, represented an often underestimated medical revolution. Indeed, until that time, bacterial infections were the prime cause of mortality, especially in children and elderly patients. The discovery of numerous new substances and their development on an industrial scale gave us the illusion that bacterial infections were all but vanquished. However, the widespread and sometimes uncontrolled use of these agents has led to the selection of bacteria resistant to practically all available antibiotics. Bacteria utilize three main resistance strategies: (1) modification of their permeability, (2) modification of target, and (3) modification of the antibiotic. Bacteria modify their permeability either by becoming impermeable to antibiotics, or by actively excreting the drug accumulated in the cell. As an alternative, they can modify the structure of the antibiotic's molecular target--usually an essential metabolic enzyme of the bacterium--and thus escape the drug's toxic effect. Lastly, they can produce enzymes capable of modifying and directly inactivating antibiotics. In addition, bacteria have evolved extremely efficient genetic transfer systems capable of exchanging and accumulating resistance genes. Some pathogens, such as methicillin-resistant Staphylococcus aureus and multiresistant Mycobacterium tuberculosis, have become resistant to almost all available antibiotics and there are only one or two substances still active against such organisms. Antibiotics are very precious drugs which must be administered to patients who need them. On the other hand, the development of resistance must be kept under control by a better comprehension of its mechanisms and modes of transmission and by abiding by the fundamental rules of anti-infectious chemotherapy, i.e.: (1) choose the most efficient antibiotic according to clinical and local epidemiological data, (2) target the bacteria according to the microbiological data at hand, and (3) administer the antibiotic in an adequate dose which will leave the pathogen no chance to develop resistance.
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Effet de l’atorvastatine sur la dysfonction endothéliale des artères coronaires épicardiques associée à l’hypertrophie ventriculaire gauche dans un modèle porcin Forcillo J, Aubin MC, Horn A, Shi YF, Carrier M, Tardif JC, Perrault LP Introduction: L’atorvastatine par ses effets pléiotropiques pourrait limiter la dysfonction endothéliale associée au développement de l’HVG. Méthodologie : Un cerclage de l’aorte ascendante pendant 2 mois entraîne le développement d’HVG et les groupes ont été traités avec atorvastatine 40 ou 80 mg de 60 à 90 jours. L’HVG est confirmée par échographie. La réactivité vasculaire est évaluée en chambres d’organe, la fonction endothéliale par la quantification de la GMPc et des nitrites/nitrates plasmatiques. Le stress oxydant est mesuré par les niveaux d’ANG II et de la carbonylation des protéines. Résultats : Après 60 et 90 j de cerclage, l’HVG est observée chez tous ces groupes. Les courbes concentrations-réponse des anneaux des artères coronaires épicardiques des groupes traités avec l’atorvastatine 40 et 80 mg pour 30 et 60 jours n’ont démontré aucune amélioration des relaxations dépendantes de l’endothélium. Une exacerbation significative de la dysfonction endothéliale a été observée. Les niveaux vasculaires de GMPc sont significativement diminués dans le groupe sans cerclage traité 60 d et ceux d’ANG II sont fortement augmentés chez ce dernier groupe ainsi que le groupe traité avec 80 mg pour 30 jours par rapport aux contrôles. L’expression de la carbonylation des protéines est augmentée dans le groupe témoin traité avec atorvastatine 80 mg, reflétant une augmentation du stress oxydant. Conclusion : L’administration d’atorvastatine ne prévient pas le développement de l’HVG ni la dysfonction endothéliale dans notre modèle. Au contraire l’atorvastatine à haute dose a un effet toxique sur les artères coronaires épicardiques en augmentant la dysfonction endothéliale.
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La régulation de l’homéostasie du fer est cruciale chez les bactéries. Chez Salmonella, l’expression des gènes d’acquisition et du métabolisme du fer au moment approprié est importante pour sa survie et sa virulence. Cette régulation est effectuée par la protéine Fur et les petits ARN non codants RfrA et RfrB. Le rôle de ces régulateurs est d’assurer que le niveau de fer soit assez élevé pour la survie et le métabolisme de Salmonella, et assez faible pour éviter l’effet toxique du fer en présence d’oxygène. Les connaissances concernant le rôle de ces régulateurs ont été principalement obtenues par des études chez S. Typhimurium, un sérovar généraliste causant une gastro-entérite chez les humains. Très peu d’informations sont connues sur le rôle de ces régulateurs chez S. Typhi, un sérovar humain-spécifique responsable de la fièvre typhoïde. Le but de cette étude était de déterminer les rôles de Fur, RfrA et RfrB dans l’homéostasie du fer et la virulence de Salmonella, et de démontrer qu’ils ont une implication distincte chez les sérovars Typhi et Typhimurium. Premièrement, Fur, RfrA et RfrB régulent l’homéostasie du fer de Salmonella. Les résultats de cette étude ont démontré que Fur est requis pour la résistance au stress oxydatif et pour une croissance optimale dans différentes conditions in vitro. La sensibilité du mutant fur est due à l’expression des petits ARN RfrA et RfrB, et cette sensibilité est beaucoup plus importante chez S. Typhi que chez S. Typhimurium. Également, Fur inhibe la transcription des gènes codant pour les sidérophores en conditions riches en fer, tandis que les petits ARN RfrA et RfrB semblent être importants pour la production d’entérobactine et de salmochélines chez S. Typhi lors de conditions pauvres en fer. Ensuite, ces régulateurs affectent la virulence de Salmonella. Fur est important pour la motilité de Salmonella, particulièrement chez S. Typhi. Fur est nécessaire pour l’invasion des deux sérovars dans les cellules épithéliales, et pour l’entrée et la survie de S. Typhi dans les macrophages. Chez S. Typhimurium, Fur ne semble pas impliqué dans l’interaction avec les macrophages. De plus, les petits ARN RfrA et RfrB sont importants pour la multiplication intracellulaire de Salmonella dans les macrophages pour les deux sérovars. Finalement, la protéine Fur et les petits ARN RfrA et RfrB régulent l’expression de l’opéron fimbriaire tcf, absent du génome de S. Typhimurium. Un site de liaison putatif de la protéine Fur a été identifié dans la région promotrice de tcfA chez S. Typhi, mais une régulation directe n’a pas été confirmée. L’expression de tcf est induite par le fer et par Fur, et est inhibée par les petits ARN RfrA et RfrB. Ainsi, ces régulateurs affectent des gènes de virulence qui sont retrouvés spécifiquement chez S. Typhi. En somme, ce projet a permis de démontrer que les régulateurs de l’homéostasie du fer de Salmonella peuvent affecter la résistance de cette bactérie pathogène à différents stress, notamment le stress oxydatif, la croissance en conditions de carence en fer ainsi que la virulence. Ces régulateurs jouent un rôle distinct chez les sérovars Typhi et Typhimurium.
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Dans une perspective d’analyse des risques pour la santé publique, l’estimation de l’exposition revêt une importance capitale. Parmi les approches existantes d’estimation de l’exposition, l’utilisation d’outils, tels que des questionnaires alimentaires, la modélisation toxicocinétique ou les reconstructions de doses, en complément de la surveillance biologique, permet de raffiner les estimations, et ainsi, de mieux caractériser les risques pour la santé. Ces différents outils et approches ont été développés et appliqués à deux substances d’intérêt, le méthylmercure et le sélénium en raison des effets toxiques bien connus du méthylmercure, de l’interaction entre le méthylmercure et le sélénium réduisant potentiellement ces effets toxiques, et de l’existence de sources communes via la consommation de poisson. Ainsi, l’objectif général de cette thèse consistait à produire des données cinétiques et comparatives manquantes pour la validation et l’interprétation d’approches et d’outils d’évaluation de l’exposition au méthylmercure et au sélénium. Pour ce faire, l’influence du choix de la méthode d’évaluation de l’exposition au méthylmercure a été déterminée en comparant les apports quotidiens et les risques pour la santé estimés par différentes approches (évaluation directe de l’exposition par la surveillance biologique combinée à la modélisation toxicocinétique ou évaluation indirecte par questionnaire alimentaire). D’importantes différences entre ces deux approches ont été observées : les apports quotidiens de méthylmercure estimés par questionnaires sont en moyenne six fois plus élevés que ceux estimés à l’aide de surveillance biologique et modélisation. Ces deux méthodes conduisent à une appréciation des risques pour la santé divergente puisqu’avec l’approche indirecte, les doses quotidiennes estimées de méthylmercure dépassent les normes de Santé Canada pour 21 des 23 volontaires, alors qu’avec l’approche directe, seulement 2 des 23 volontaires sont susceptibles de dépasser les normes. Ces différences pourraient être dues, entre autres, à des biais de mémoire et de désirabilité lors de la complétion des questionnaires. En outre, l’étude de la distribution du sélénium dans différentes matrices biologiques suite à une exposition non alimentaire (shampoing à forte teneur en sélénium) visait, d’une part, à étudier la cinétique du sélénium provenant de cette source d’exposition et, d’autre part, à évaluer la contribution de cette source à la charge corporelle totale. Un suivi des concentrations biologiques (sang, urine, cheveux et ongles) pendant une période de 18 mois chez des volontaires exposés à une source non alimentaire de sélénium a contribué à mieux expliciter les mécanismes de transfert du sélénium du site d’absorption vers le sang (concomitance des voies régulées et non régulées). Ceci a permis de montrer que, contrairement au méthylmercure, l’utilisation des cheveux comme biomarqueur peut mener à une surestimation importante de la charge corporelle réelle en sélénium en cas de non contrôle de facteurs confondants tels que l’utilisation de shampoing contenant du sélénium. Finalement, une analyse exhaustive des données de surveillance biologique du sélénium issues de 75 études publiées dans la littérature a permis de mieux comprendre la cinétique globale du sélénium dans l’organisme humain. En particulier, elle a permis le développement d’un outil reliant les apports quotidiens et les concentrations biologiques de sélénium dans les différentes matrices à l’aide d’algorithmes mathématiques. Conséquemment, à l’aide de ces données cinétiques exprimées par un système d’équations logarithmiques et de leur représentation graphique, il est possible d’estimer les apports quotidiens chez un individu à partir de divers prélèvements biologiques, et ainsi, de faciliter la comparaison d’études de surveillance biologique du sélénium utilisant des biomarqueurs différents. L’ensemble de ces résultats de recherche montre que la méthode choisie pour évaluer l’exposition a un impact important sur les estimations des risques associés. De plus, les recherches menées ont permis de mettre en évidence que le sélénium non alimentaire ne contribue pas de façon significative à la charge corporelle totale, mais constitue un facteur de confusion pour l’estimation de la charge corporelle réelle en sélénium. Finalement, la détermination des équations et des coefficients reliant les concentrations de sélénium entre différentes matrices biologiques, à l’aide d’une vaste base de données cinétiques, concourt à mieux interpréter les résultats de surveillance biologique.
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The work presented in this thesis is centered mainly around delineating the toxic effect of hydrogen sulphide on penaeid prawns and understand its influence on the ecology of estuary. The present investigation also involved characterization of the effects of hydrogen sulphide on the growth and behavioural responses of Penaeus indicus. The test animals employed during the present study namely indicus and Metapenaeus dobsoni are both ecologically and economically relevant. The thesis embodying the details of the investigation has been organized into three chapters comprising Acute toxicity, influence of hydrogen sulphide on the ecology of estuary and effect of hydrogen sulphide on growth and substratum selectivity of penaeid prawn. Each chapter has been partioned into various sections as Introduction, Material and Methods, Results and Discussion for a lucid presentation of the subject matter.
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Internationally agreed standard protocols for assessing chemical toxicity of contaminants in soil to worms assume that the test soil does not need to equilibrate with the chemical to be tested prior to the addition of the test organisms and that the chemical will exert any toxic effect upon the test organism within 28 days. Three experiments were carried out to investigate these assumptions. The first experiment was a standard toxicity test where lead nitrate was added to a soil in solution to give a range of concentrations. The mortality of the worms and the concentration of lead in the survivors were determined. The LC(50)s for 14 and 28 days were 5311 and 5395 mug(Pb) g(soil)(-1) respectively. The second experiment was a timed lead accumulation study with worms cultivated in soil containing either 3000 or 5000 mug(Pb) g(soil)(-1). The concentration of lead in the worms was determined at various sampling times. Uptake at so' Sol both concentrations was linear with time. Worms in the 5000 mug g(-1) soil accumulated lead at a faster rate (3.16 mug Pb g(tissue)(-1) day(-1)) tiss than those in the 3000 mug g(-1) soil (2.21 mug Pb-tissue g(-1) day(-1)). The third experiment was a timed experiment with worms cultivated in tiss soil containing 7000 mugPb g(soil)(-1). Soil and lead nitrate solution were mixed and stored at 20 degreesC. Worms were added at various times over a 35-day period. The time to death increased from 23 h, when worms were added directly after the lead was added to the soil, to 67 It when worms were added after the soil had equilibrated with the lead for 35 days. In artificially Pb-amended soils the worms accumulate Pb over the duration of their exposure to the Pb. Thus time limited toxicity tests may be terminated before worm body load has reached a toxic level. This could result in under-estimates of the toxicity of Pb to worms. As the equilibration time of artificially amended Pb-bearing soils increases the bioavailability of Pb decreases. Thus addition of worms shortly after addition of Pb to soils may result in the over-estimate of Pb toxicity to worms. The current OECD acute worm toxicity test fails to take these two phenomena into account thereby reducing the environmental relevance of the contaminant toxicities it is used to calculate. (C) 2002 Elsevier Science Ltd. All rights reserved.
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Carbendazim-amended soil was placed above or below unamended soil. Control tests comprised two layers of unamended soil. Allolobophora chlorotica earthworms were added to either the upper or the unamended soil. After 72 h vertical distributions of earthworms were compared between control and carbendazim-amended experiments. Earthworm distributions in the carbendazim-amended test containers differed significantly from the ‘normal’ distribution observed in the control tests. In the majority of the experiments, earthworms significantly altered their burrowing behaviour to avoid carbendazim. However, when earthworms were added to an upper layer of carbendazim-amended soil they remained in this layer. This non-avoidance is attributed to (1) the earthworms’ inability to sense the lower layer of unamended soil and (2) the toxic effect of carbendazim inhibiting burrowing. Earthworms modified their burrowing behaviour in response to carbendazim in the soil. This may explain anomalous results observed in pesticide field trials when carbendazim is used as a control substance.