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A new synthetic route towards 6-azaindoles (pyrrolo[2,3- c ]pyridines) and pyrrolo[2,3- d ]pyridazines starting from 4-aroyl pyrroles is described. This overall protocol involves: (i) the Vilsmeier-Haack reaction to obtain pyrrolo-2,3-dicarbonyles and (ii) condensation with hydrazines or glycine methyl ester. The reaction mechanism between pyrrolo-2,3-dicarbonyl with phenyl hydrazine and glycine methyl ester has been modelled using DFT calculations to prove the formation of one from two possible isomers of condensation.

The purpose of this research note is to summarize the current state of knowledge on the impact of environmental exposures on the development of obesity and diabetes. In France, the incidence of diabetes almost doubled between 2000 and 2008 (+ 93%), affecting 1.8 million people. The prevalence of obesity has almost doubled in 10 years. Since the 1980s, the focus of the fight against obesity and diabetes has been on hygienic and dietary measures. However, it is now clear that these measures have failed to reverse the trend. Chronic diseases such as obesity and diabetes have resulted in a dramatic increase in public health spending. A growing body of data has highlighted the important role of chemical pollution in the epidemic of metabolic diseases, particularly substances classified as endocrine disrupting chemicals (EDCs). By altering the endocrine function of organs such as adipose tissue, liver, pancreas, and skeletal muscle, EDCs disrupt the metabolism of carbohydrates and lipids, leading in turn to insulin resistance and diabetes and obesity, which both increase the risk of cardiovascular complications. The traditional toxicological principle that "the dose makes the poison" does not reflect the complexity of the deleterious effect of EDCs either alone or in combination. EDC-induced patho-physiological alterations can be programmed during the fetal period, before appearing later in life. A new paradigm evaluating the toxicological properties of EDCs is needed to support new recommendations in terms of prevention policy, at both national and European levels.

The term volatile organic compounds includes a wide variety of chemical substances with the common feature of being carbon compounds that are volatile at ambient temperature. They can be classified into different families defined by their chemical formulae, each of which possesses common properties, although there may be major differences in terms of toxicity. For that reason the effects of VOC on health have to be considered both in an individual way and also from a global viewpoint on account of their common toxic properties and the role they play in the formation of environmental photo-oxidative pollutants, both outdoors and indoors.

Glycol ethers (GE) are a family of solvents, the use of which has increased dramatically since the 60's, in domestic and occupational mainly water-based products, such as paintings, inks, varnishes, cleaning agents. There are two subgroups: E series and P series. EGME, among the E series, is the reference substance. This is a reprotoxic chemical causing infertility and genital apparatus atrophy on both sexes, embryofetal toxicity through maternal exposure (malformation, growth alterations and functional deficits). European Union has classified nine other GE as reprotoxic. P series, with the beta isomers exception, has no specific reprotoxicity. Epidemiological studies published from the 80's onwards, have confirmed animal data (malformation, oligoazoospermia, spontaneous abortion, hypofertility). The effects can be observed even after the end of exposure. Risk assessment studies tend to prove that this massive exposure during several decades could have had an important impact on reproductive human health. Even if this exposure has considerably decreased since the last few years, a ban of reprotoxic GE, as required by two official bodies (CSC, CSHPF), seems necessary, due to the high risk level. Classification should be completed for some GE, not classified now (EGBE). Health assessment of past exposure should be carried out. Physicians should look after a possible glycol ethers responsibility when facing this kind of reprotoxic effects.

The Finnish Institute of Occupational Health (FIOH) has received support from the World Health Organization (WHO) and the International Labor Office (ILO) to publish the African Newsletter on Occupational Health and Safety. The African Newsletter on Occupational Health and Safety should not be a medium for industry propaganda, or the source of misinformation among the workers of Africa. Instead, FIOH should provide the same level of scientific information in Africa that it does in Finland and other developed countries.

Glycol ethers (Ge) are a family of substances with a growing use in industrial and domestic products for the two last decades. Ge (group 1 and 2) are experimentally toxic for reproduction and development, at various levels. That begins to be found in humans. Epidemiological studies confirm toxicokinetic data showing humans are more sensitive than animals, because of a low excretion rate of the toxic metabolites. Occupational and consumer exposures are frequently higher than reference concentrations deducted from animal data. They may be involved in the growing number of genital reproductive system and reproduction anomaly, observed in most developed countries. Genetic toxicity is suspected from experimental data, but further investigations are needed.

Ethylene glycol ethers and their acetate derivatives were analyzed for their toxicity in vitro on several hemopoietic cell lines, either growth-factor-dependent or leukemic, in mouse, rat, and human species. Considering the concentrations that reduced the cell viability in culture by 50%, most of the ethylene glycol ethers and in particular ethylene glycol monoethyl ether (EGEE) or ethylene glycol monobutyl ether (EGBE) should be considered as hemopoietic toxins. EGBE was found to be the most potent toxin on the human promyelocytic cell line, NB4 (median inhibitory concentration (IC50) 5 mM at 6 h; IC50 0.1 mM at 96 h) but also on the factor-dependent cell line DA1 (IC50 80 microM at 48 h). Factor-dependent cell lines were not significantly more sensitive than leukemic cell lines. The toxicity of these compounds falls in the same range of concentration as benzene or phenol, but hydroquinone was significantly more toxic in the same assay (IC50 3-15 microM at 48 h). Toxic effects increased linearly with time. The toxicity of ethylene glycol ethers was confirmed by both assays for colony-forming units in culture medium (CFU-C) (human blood cord cells) and murine bone marrow long-term culture (IC50 5-10 mM). Stromal cells in the adherent layer were more resistant than hemopoietic cells. An all or none toxicity was found within a narrow range of concentration (2-5 mM for EGBE), and chronic exposure over two months did not show cumulative effects on the culture cellularity. The possibility that fibroblastic or macrophage cells worked at the detoxification of the culture is suggested. Results are discussed with regard to epidemiological and in vivo experimental data presently available.

The CS2 and H2S pollution was evaluated in two viscose plants: a sponge factory and a rayon spinning mill. Two kinds of sampling were used: background samples with the help of a laboratory van equipped with a Gas Phase Chromatograph and an Air Sampler allowing sequential workplace monitoring. personal samples. The results show the H2S pollution is not negligible and can even be equal to that with CS2 in some workshops (e.g. the spinning-room). The proposed methodology permits an accurate description of the pollution.