Genotoxic effects of paracetamol in V79 Chinese hamster cells

Paracetamol was studied for possible genotoxic effects in V79 Chinese hamster cells. Paracetamol (0.5 mM for 30 min) reduced the rate of DNA synthesis in exponentially growing V79 cells to about 50% of control. A further decrease in the DNA synthesis was seen during the first 30 min after termination of paracetamol exposure. Paracetamol (3 and 10 mM for 2 h) caused a small increase in DNA single-strand breaks, as measured by the alkaline elution technique. After 16 h elution, the amount of DNA retained on the filters was 79 and 70% of controls in cells treated with 3 and 10 mM paracetamol respectively. No indication of DNA damage was seen in measuring the effect of paracetamol (0.25-10 mM for 2 h) on unscheduled DNA synthesis in growth-arrested cultures of V79 cells. At the highest concentrations (3 and 10 mM paracetamol), decreased unscheduled DNA synthesis was observed. Also UV-induced DNA-repair synthesis was inhibited by 3 and 10 mM paracetamol. DNA-repair synthesis was, however, inhibited at a much higher concentration than that inhibiting replicative DNA synthesis. The number of sister-chromatid exchanges (SCE) increased in a dose-dependent manner on 2 h exposure to paracetamol from 1 mM to 10 mM. At the highest dose tested (10 mM), the number of SCE increased to 3 times the control value. Co-culturing the V79 cells with freshly isolated mouse hepatocytes had no further effect on the paracetamol induced sister-chromatid exchanges. The present study indicates that paracetamol may cause DNA damage in V79 cells without any external metabolic activation system added.     

NanoSIMS Analysis of Intravascular Lipolysis and Lipid Movement across Capillaries and into Cardiomyocytes

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Callus induction and plant regeneration from different explant types of Miscanthus x ogiformis Honda ‘Giganteus’

Different explants of Miscanthus x ogiformis Honda Giganteus were tested in order to develop an efficient tissue culture system. Shoot apices, leaf and root sections from in vitro-propagated plants, and leaf and immature inflorescence sections from 6-month-old greenhouse-grown plants were used. The explants were cultured on Murashige and Skoog medium supplemented with 4.5, 13.6, 22.6 or 31.7 M 2,4-dichlorophenoxyacetic acid. Three types of callus were formed but only one was embryogenic and regenerated plants. Callus induction and formation of embryogenic callus depended on the type and developmental stage of the explants. Shoot apices formed the highest percentage of embryogenic callus. There was a difference in the formation of embryogenic callus between leaf explants from in vitro-propagated shoots and greenhouse-grown plants. The best results were obtained from newly formed leaves of in vitro-propagated shoots and older leaves of greenhouse-grown plants. Immature inflorescences smaller than 2.5 cm produced a higher percentage of embryogenic callus than larger more mature inflorescences. Embryogenic callus derived from immature inflorescences had the highest regeneration capacity. Differences in 2,4-dichlorophenoxyacetic acid concentrations had no significant effect on callus induction, embryogenic callus formation and plant regeneration.Abbreviations MS Murashige & Skoog - 2,4-d 2,4-dichlorophenoxyacetic acid - BA benzyladenine - NAA 1-naphthaleneacetic acid - PPFD photosynthetic photon flux density     

Megafauna extinction,tree species range reduction,and carbon storage in Amazonian forests

During the Late Pleistocene and early Holocene 59 species of South American megafauna went extinct. Their extinction potentially triggered population declines of large‐seeded tree species dispersed by the large‐bodied frugivores with which they co‐evolved, a theory first proposed by Janzen and Martin (1982). We tested this hypothesis using species range maps for 257 South American tree species, comparing 63 species thought to be primarily distributed by megafauna with 194 distributed by other animals. We found a highly significant (p < 0.001) decreased mean range size of 26% for the megafauna dispersed fruit (n = 63 species) versus fruit dispersed by other animals (n = 194), results which support the hypothesis. We then developed a mathematical model of seed dispersal to estimate the theoretical impact of megafauna extinction on tree species range and found the estimated dispersal capacity (Φ_seed) of a 2 g seed decreases by > 95% following disperser extinction. A numerical gap dynamic simulations suggests that over a 10 000 yr period following the disperser extinctions, the average convex hull range size of large‐seeded tree species decreased by ～ 31%, while the estimated decrease in population size was ～ 54%, indicating a likely greater decrease in species population size than indicated by the empirical range patterns. Finally, we found a positive correlation between seed size and wood density of animal‐dispersed tree species implying that the Late Pleistocene and early Holocene megafaunal extinctions reduced carbon content in the Amazon by ～ 1.5 ± 0.7%. In conclusion, we 1) provide some empirical evidence that megafauna distributed fruit species have a smaller mean range size than wind, water or other animal‐dispersed species, 2) demonstrate mathematically that such range reductions are expected from megafauna extinctions ca 12 000 yr ago, and 3) illustrate that these extinctions may have reduced the Amazon's carbon storage capacity.     

A network approach for inferring species associations from co‐occurrence data

Positive and negative associations between species are a key outcome of community assembly from regional species pools. These associations are difficult to detect and can be caused by a range of processes such as species interactions, local environmental constraints and dispersal. We integrate new ideas around species distribution modeling, covariance matrix estimation, and network analysis to provide an approach to inferring non‐random species associations from local‐ and regional‐scale occurrence data. Specifically, we provide a novel framework for identifying species associations that overcomes three challenges: 1) correcting for indirect effects from other species, 2) avoiding spurious associations driven by regional‐scale distributions, and 3) describing these associations in a multi‐species context. We highlight a range of research questions and analyses that this framework is able to address. We show that the approach is statistically robust using simulated data. In addition, we present an empirical analysis of > 1000 North American tree communities that gives evidence for weak positive associations among small groups of species. Finally, we discuss several possible extensions for identifying drivers of associations, predicting community assembly, and better linking biogeography and community ecology.     

Toxic effects of cyclophosphamide in differentiating chicken limb bud cell culture using rat liver 9,000 g supernatant or rat liver cells as an activation system: an in vitro short-term test for proteratogens

Cells from 4-day chicken embryo limb buds plated as micromass cultures differentiate and form cartilage nodules after a 5- to 6-day growth period. The innate ability of these cells to biotransform compounds, such as cyclophosphamide (CP), into reactive metabolites is apparently inadequate. Protocols used rat liver S9 from Aroclor 1254-pretreated (PCB) rats or hepatocytes from control rats or polychlorinated biphenyls (PCB)-pretreated rats and were added to micromass cultures with CP causing concentration-related toxicity in the cell cultures. Coculturing chicken limb bud cells with PCB-hepatocytes was the most efficient method, yielding an IC50 of 2 micrograms CP per ml. Toxic CP metabolites accumulated in the medium of PCB-hepatocyte cultures and were quite stable. The toxicity of bioactivated CP was nearly identical for both proliferation and cartilage proteoglycan accumulation.     

The non-genotoxicity to rodents of the potent rodent bladder carcinogens o-anisidine and p-cresidine.

The two potent rodent bladder carcinogens o-anisidine and p-cresidine, and the structurally related non-carcinogen 2,4-dimethoxyaniline, have been extensively evaluated for genotoxicity to rodents and found to be inactive. Most data were generated on o-anisidine, an agent that is also only marginally genotoxic in vitro. The two carcinogens induced methaemoglobinaemia in rodents indicating that the chemicals are absorbed and metabolically oxidized. Despite their total lack of genotoxicity in vivo, the two carcinogens have the hall-marks of being genotoxic carcinogens given that most test animals of both sexes of B6C3F1 mice and F344 rats are reported to have succumbed rapidly to malignant bladder cancer. No reasons for this dramatic conflict of test data are so far apparent. The experiments described involve, in one or other combination, 2 strains of mice (including B6C3F1) and 4 strains of rat (including F344), the use of oral and i.p routes of exposure and observations made after 1, 3 or 6 doses of test chemical. 6 tissues (including the rat bladder) were assayed using 3 genetic endpoints (unscheduled DNA synthesis, DNA single-strand breaks and micronuclei induction). Aroclor-induced rats were employed in one set of experiments with o-anisidine. In the case of one set of mouse bone-marrow micronucleus experiments the same batch of the 3 chemicals as used in the cancer bioassays, and the same strain of mouse, were used. Possible further experiments and the implications of these findings are discussed.